Effects of long-term particulate matter exposure on platelet counts in adults of Northeast China

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Abstract Associations between air pollution exposure and platelet counts have been inconsistent in previous studies, and there have been few studies of effects of long-term exposure in Asian populations. We explored the associations between long-term PM2.5 (particulate matter < 2.5 µm) exposure and platelet counts using a prospective cohort study in Northeast China. We used a logistic regression model to analyze the effects of different PM2.5 increments and platelet count elevation. Mixed linear models were used to analyze the association between PM2.5 concentration and platelet counts. Interaction and stratified analyses were also conducted. Results showed that every 1 µg/m3 increment of PM2.5 exposure was associated with 0.29% (95%CI: 0.25–0.32%) increase in platelet counts and 10% (95%CI: 8–12%) higher risk of platelet elevation. Effects of long-term PM2.5 exposure on platelet elevation were stronger in male participants, of Han ethnicity, and without diabetes. Our findings add more evidence to the potential biological mechanisms responsible for the effect of air pollution exposure on cardiovascular disease.
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We explored the associations between long-term PM 2.5 (particulate matter < 2.5 µm) exposure and platelet counts using a prospective cohort study in Northeast China. We used a logistic regression model to analyze the effects of different PM 2.5 increments and platelet count elevation. Mixed linear models were used to analyze the association between PM 2.5 concentration and platelet counts. Interaction and stratified analyses were also conducted. Results showed that every 1 µg/m 3 increment of PM 2.5 exposure was associated with 0.29% (95%CI: 0.25–0.32%) increase in platelet counts and 10% (95%CI: 8–12%) higher risk of platelet elevation. Effects of long-term PM 2.5 exposure on platelet elevation were stronger in male participants, of Han ethnicity, and without diabetes. Our findings add more evidence to the potential biological mechanisms responsible for the effect of air pollution exposure on cardiovascular disease. Health Economics & Outcomes Research Health Policy particulate matter air pollution platelet counts cohort study Figures Figure 1 Figure 2 1. Introduction Previous studies showed that acute and long-term exposure to air pollution (especially particulate matter < 2.5 µm, i.e. PM 2.5 ) were both associated with higher morbidity and mortality of cardiovascular diseases [ 1 , 2 ] . Studies in animals also showed that exposure to PM 2.5 increases blood coagulability, which accelerates atherosclerosis progression and results in vascular diseases [ 3 , 4 ] . Underlying mechanisms relating air pollution exposure to cardiovascular diseases include platelet activation, oxidative stress and interplay between interleukin-6 and tissue factors [ 5 , 6 ] , of which increased platelet count is associated with increased blood coagulability and cardiovascular disease mortality [ 7 , 8 ] . Previous epidemiological studies on associations between air pollution and platelet counts gave inconsistent results and mainly concentrated on short-term exposure assessment [ 9 , 10 ] . Studies of the effects of long-term air pollution exposure on platelet counts in large populations are limited [ 11 ] , especially in Asian populations. In this study, we aim to explore the associations between long-term PM 2.5 exposure and platelet counts in adults in Northeast China based on a large cohort population. Results may provide more evidence of associations between long-term air pollution exposure and cardiovascular diseases. 2. Materials And Methods 2.1. Study participants Participants in this study came from a large prospective natural population cohort in Northeast China, which is supported by the National K&D Project of China. The cohort consisted of four sub-cohorts: adults in city and county, maternal-children, special job exposures and health management. There were 30,000 adults in city and country included in this study. All participants responded to questionnaires and received physical examinations and blood tests. We excluded participants who did not provide detailed living addresses or complete blood platelet count tests, and 25,355 participants were included in the final analysis. The protocol of this study was approved by the Ethics Committee of the Shengjing Hospital of China Medical University (No. 2017PS190K). 2.2. Air pollution exposure assessment We use two-year average PM 2.5 concentration for the living address of each participant as the measure of long-term air pollution exposure. All participants were from Liaoning Province. Annual land use regression model based on 78 national monitoring stations were used to construct land use regression model and predict air pollution exposure, the method of which was described in detail in our previous study [ 12 ] . Addresses of each participant were transformed into latitude and longitude data and imported into ArcGIS 10.3. Then we estimated average PM 2.5 concentration for the year of the blood test and the previous year separately for each participant. The two-year average PM 2.5 concentration value was used as long-term ambient PM 2.5 exposure. 2.3. Platelet counts test All blood routine examinations were conducted in the Laboratory Department in Shengjing Hospital of China Medical University. Platelet count was included in the routine blood examination. The normal reference range of platelet counts is 100 × 10 9 to 350 × 10 9 /ml. Tests of fasting blood-glucose and blood lipids were also included. 2.4. Other factors involved Age, gender, race, income, status of education, smoking and alcohol drinking, indoor decoration in the previous five years, activity time per week, white blood cell (WBC) counts and presence of hypertension, diabetes, hyperlipemia and heart disease were included in the final analysis due to their confounding effects on the association between long-term PM 2.5 exposure and platelet counts [ 13 ] . Race was divided into Han, Manchu and others. Education level was divided into three categories according to education duration: 12 years. Smoking and alcohol drinking status were divided into current, ever and never. Activity degree was divided into three categories according to the physical exercise duration per week: 2 h. Hypertension was defined as average systolic pressure of three separate measures over 140 mmHg or average diastolic pressure of three separate measures over 90 mmHg. Diabetes was defined as fasting blood-glucose over 7 mmol/L. Heart disease was self-reported in the questionnaire. Hyperlipemia was defined as total cholesterol over 6.2 mmol/L, low-density lipid cholesterol over 4.1 mmol/L, triglyceride over 5.2 mmol/L or high-density lipid cholesterol below 1 mmol/L. 2.5. Statistical analysis We defined elevated platelet count as a platelet count over the 90th percentile. Continuous variables are presented as least square means with 95% confidence intervals (CIs), and categorical variables are presented as total counts with percentages. Variance analyses and c 2 tests were conducted between each variable and platelet elevation. We used different logistic models to examine the associations between every 1 µg/m 3 increment of PM 2.5 exposure and elevated platelet count. Model 1 was used to calculate crude odds ratios (ORs). Model 2 was adjusted for age, gender, race, education, income and body mass index (BMI). Model 3 was further adjusted for status of smoking and alcohol drinking, decoration in the previous five years, hypertension, diabetes, heart disease, hyperlipemia, activity per week and WBC counts. We also divided PM 2.5 exposure into four categories according to quartile and used the first quartile as a reference to calculate the effects of PM 2.5 exposure in other quartiles on platelet elevation. Effects of interactions of PM 2.5 exposure with other involved factors on platelet elevation were examined separately. Further stratified analysis was conducted based on significant interactions of confounding factors with PM 2.5 exposure. Several sensitivity analyses were conducted, and mixed linear analyses were used to examine the linear associations between PM 2.5 exposure and log-transformed platelet counts. Elevated platelet count was defined as a platelet count over the 75th percentile for the logistic analysis. All analyses were conducted using SAS version 9.4 and SPSS version 25.0. 3. Results General characteristics of the study participants are shown in Table 1 . Among the 25,355 participants, 9.7% (n = 2467) were categorized as having platelet elevation. There were significant effects on platelet elevation of age, gender, race, education level, status of smoking and alcohol drinking, indoor decoration, activity per week, WBC counts and having hypertension, heart disease or hyperlipemia. Table 1 General characteristics of the study participants. Characteristics Platelet counts P-value ≤P90 a (n = 22,888) >P90 b (n = 2467) Age, years 54.2 (54.1,54.4) c 51 (50.6,51.5) < 0.0001 d Gender, n e (%) Male 8126 (35.5) f 534 (21.7) < 0.0001 g Female 14761(64.5) 1932(78.3) Race, n (%) Han 14571(63.7) 1622(65.7) 0.006 Manchu 8287(36.2) 837(33.9) Other 30(0.1) 8(0.3) Income (10,000 Yuan) 31.7(13.7,49.8) 5.8(5.6,6) 0.355 BMI, kg/m 2 31(25.6,36.4) 28.4(24.6,32.2) 0.763 Education, n (%) 0–6 years 5551(24.3) 497(20.1) 12 years 3735(16.3) 512(20.8) Smoke, n(%) Current 3597(15.7) 337(13.7) < 0.0001 Ever 1016(4.4) 64(2.6) Never 18275(79.8) 2066(83.7) Alcohol, n(%) Current 3996(17.5) 361(14.6) < 0.0001 Ever 362(1.6) 31(1.3) Never 18530(81) 2075(84.1) Decoration, n(%) No 18958(82.8) 1934(78.5) < 0.0001 Yes 3925(17.2) 531(21.5) Hypertension, n(%) No 14425(63) 1640(66.5) 0.001 Yes 8463(37) 827(33.5) Diabetes, n(%) No 19906(87) 2161(87.6) 0.38 Yes 2982(13) 306(12.4) Heart disease, n(%) No 21390(93.5) 2329(94.4) 0.068 Yes 1498(6.5) 138(5.6) Activity, n(%) < 1 h/week 10768(47) 1186(48.1) 2 h/week 9779(42.7) 965(39.1) Hyperlipemia, n(%) No 18534(81) 1805(73.2) < 0.0001 Yes 4354(19) 662(26.8) White blood cell count (10 9 /ml) 6.2(6.2,6.3) 7.2(7.1,7.2) < 0.0001 PM 2.5 exposure (µg/m 3 ) 36.8(36.7,36.8) 37.7(37.5,37.9) 90th percentile; c, least square means with 95% CI intervals – applies to all such values; d, P-values of variance analyses – applies to all such values; e, number of participants; f, total counts with percentages – applies to all such values; g, P-values of c 2 tests – applies to all such values. Average PM 2.5 exposure of all participants was 37.25 µg/m 3 with a significant difference between participants with elevated platelet counts and those without. Figure 1 shows the distributions of participant locations and variation in PM 2.5 exposure across the whole study area. The associations between PM 2.5 exposure and 90th percentile platelet elevations remained stable after adjusting for all possible confounders (Table 2 ). When PM 2.5 was treated as a continuous variable, the OR between every 1 µg/m 3 increment of PM 2.5 exposure and platelet elevation was 1.1 (95%CI: 1.08–1.12). When PM 2.5 was treated as a categorical factor, compared with participants in the first quartile, those in the third (OR = 1.28, 95%CI: 1.08–1.52) and fourth (OR = 2.18, 95%CI: 1.83–2.60) quartiles were more likely to have elevated platelet counts. Table 2 Effects of PM 2.5 exposure on 90th percentile platelet elevation. PM 2.5 OR (95%CI) Model 1 P-value Model 2 P-value Model 3 P-value 1 µg/m 3 increment 1.06 (1.05,1.08) < 0.0001 1.11(1.09,1.12) < 0.0001 1.1(1.08,1.12) < 0.0001 1st quartile Ref Ref Ref 2st quartile 0.88(0.77,1.0) 0.05 1.07(0.92,1.25) 0.37 1.1(0.94,1.29) 0.24 3rd quartile 1.02(0.9,1.16) 0.73 1.31(1.11,1.55) 0.00 1.28(1.08,1.52) 0.01 4st quartile 1.84(1.64,2.05) < 0.0001 2.21(1.88,2.59) < 0.0001 2.18(1.83,2.6) < 0.0001 P-value for trend < 0.0001 < 0.0001 < 0.0001 Model 1, crude model; Model 2, adjusted for age, gender, race, education, income and BMI; Model 3, further adjusted for status of smoking and alcohol drinking, decoration in the previous five years, hypertension, diabetes, heart disease, hyperlipemia, activity per week and white blood cell counts.1st quartile, PM 2.5 ≤ 25th percentile; 2nd quartile, 25th percentile < PM 2.5 ≤50th percentile; 3rd quartile, 50th percentile 75th percentile. Model 3 showed significant interactions of PM 2.5 exposure with gender (P < 0.01), race (P < 0.0001) and diabetes status (P < 0.001). Figure 2 shows the stratified analysis results according to gender (male and female), race (Han and Manchu) and diabetes (yes and no). Males were more likely to have platelet elevation after long-term PM 2.5 exposure compared with females. Those of Han ethnicity were more likely to have platelet elevation compared with Manchu ethnicity. Participants without diabetes were more likely to have platelet elevation after long-term PM 2.5 exposure. Sensitivity analysis results are shown in Supplemental Tables 1 and 2. Analysis results for the mixed linear model between long-term PM 2.5 exposure and platelet counts showed that every 1 µg/m 3 increment of PM 2.5 exposure was associated with 0.29% (95%CI: 0.25–0.32%) increase in platelet counts; and effects of PM 2.5 exposure were more evident in participants who were male, of Han ethnicity and without diabetes (Supplemental Table 1). Using the 75th percentile as the cut-off to define elevated platelet counts gave similar results (Supplemental Table 2) to those for the 90th percentile. 4. Discussion To our knowledge, this is the first cohort study in mainland China focusing on the association between long-term air pollution exposure and platelet counts. We found that long-term PM 2.5 exposure was associated with elevated platelet counts – every 1 µg/m 3 increment of PM 2.5 exposure was associated with 0.29% increase in platelet counts and 10% higher risk of platelet elevation. Gender, race and diabetes status might interact with long-term PM 2.5 exposure in regard to platelet counts. Our findings add more evidence to determining the potential biological mechanisms relating air pollution exposure to cardiovascular disease. Results of this study are similar to those of some previous studies focusing on the associations between short-term PM exposure and platelet activation (platelet count elevation or platelet aggregation) [ 14 , 15 , 16 ] in Europe and China. In a large cohort study of Taiwanese adults, long-term PM 2.5 exposure was associated with elevated platelet counts, but with a weaker effect than in our study, possibly because the Taiwanese study population was generally younger than in our study [ 17 ] . A prospective cohort study of German adults also found similar results, with every 2.4 µg/m 3 increment of PM 2.5 exposure associated with an adjusted increase of 2.3% in platelet counts [ 18 ] . Animal experiments also showed that repeat dose exposure of PM 2.5 triggered disseminated intravascular coagulation in Sprague Dawley rats with elevated platelet counts [ 19 ] . We also found significant differences in the effects of long-term PM 2.5 exposure on platelet elevation related to gender, race and diabetes of participants. Stronger associations between PM 2.5 exposure and platelet elevation were found for male participants, similar to previous studies [ 20 ] – the biological mechanisms responsible might be the effects of different hormone levels in men and women, which may interact with chemicals in PM 2.5 [ 21 ] but more studies are required. Significant differences in platelet parameters as well as related risk factors have been found for European and Asian countries [ 22 ] , but race-related effects on platelet counts following long-term PM 2.5 exposure have seldom been mentioned. There were considerable proportions of Han and Manchu ethnicities among participants in our study. Research has revealed that frequencies of human platelet alloantigen alleles differ among Chinese ethnic groups [ 23 ] and associated risk factors differ among different races [ 24 ] , which might explain some of the effects of race on platelet counts with PM 2.5 exposure. Previous studies reported that the effect of ultra-fine particulates on thrombosis was significantly attenuated in diabetic subjects taking aspirin [ 25 , 26 ] , possibly explaining our results of weaker effects of long-term PM 2.5 exposure on platelet elevation in participants with diabetes. We found no significant effects of other cardiovascular-related risk factors such as age and BMI [ 27 ] , possibly because the average age of participants was over 40 years and the younger sub-group was relatively small. The biological pathway of platelet activation following PM 2.5 exposure remains unclear. A previous study showed that PM 2.5 exposure increased the methylation levels of CpG sites, with the function related to platelet activation, inflammation and oxidative stress [ 14 ] . Furthermore, more oxidative stress after PM 2.5 exposure reflected in an increased level of reactive oxygen species, which can also promote platelet activation, has been hypothesized as a possible mechanism [ 14 ] . Previous studies showed PM exposure was also associated with changes in fibrinogen levels, extracellular vesical release and miRNA content [ 29 ] ; however, the biological pathway related to platelet activation or pro-thrombosis requires further research. This is the first cohort study in Northeast China to study the association between long-term PM 2.5 exposure and platelet counts. The large number of participants gave stable results, as shown by our sensitivity analysis. The abundant information from questionnaire and blood tests gave an assessment of a wide range of potential confounders, which allowed us to better characterize the associations and find new modifiers. Although this was a multi-center cohort study, all tests of platelet counts were from one laboratory, thus there was no heterogeneity in outcome definition, making our results reliable. However, there were some limitations in this study. First, although previous study demonstrated the predictive value of platelet counts for thrombosis and cardiovascular diseases [ 30 ] , using platelet counts alone to represent coagulation might limit the specificity blood coagulation assessment and future study should include more specific biomarkers. However, low test cost and easy availability make platelet counts more suitable for large-scale epidemiological studies compared to other biomarkers. Second, participants in our cohort were comparatively older than in previous studies, which might have resulted in a stronger correlation between PM 2.5 exposure and platelet elevation. Third, PM 2.5 level was comparatively higher than those reported in other countries, which might also explain the stronger correlation between PM 2.5 exposure and platelet elevation in our study, although this allowed us to investigate health effects of PM 2.5 exposure across a wider range. 5. Conclusion We explored the associations between long-term PM 2.5 exposure and platelet counts based on a prospective cohort study in Northeast China. We found long-term PM 2.5 exposure was associated with elevated platelet count. Gender, race and diabetes status interacted with the effect of long-term PM 2.5 exposure on platelet counts. Our findings add evidence concerning the potential biological mechanisms responsible for the relationship between air pollution exposure and cardiovascular disease. We recommend more epidemiological study on the interactions of air pollution exposure with race and disease status, and more basic research on the biological pathway of platelet count elevation after air pollution exposure. Declarations Conflicts of interest The authors declare that they have no competing financial interests. Ethics approval and consent to participate The protocol of this study was approved by the Institutional Review Board of Shengjing Hospital of China Medical University in 2017 (No. 2017PS190K). Funding This work was supported by the National Key R&D Project of China (Grant number 2017YFC0907401, 2017) and the 345 Talent Project of Shengjing Hospital of China Medical University. Authors’ contributions Zhang Hehua analyzed the data and wrote the paper; Zhao Yuhong designed the study process and reviewed the work. Acknowledgments We thank the participants of the cohort for their kind cooperation and all cohort team workers for their hard work. 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Circulating monocyte-platelet aggregates are a robust marker of platelet activity in cardiovascular disease[J]. Atherosclerosis. 2019;282:11–8. Supplementary Files supplementalmaterials.docx Cite Share Download PDF Status: Posted Version 1 posted You are reading this latest preprint version Research Square lets you share your work early, gain feedback from the community, and start making changes to your manuscript prior to peer review in a journal. As a division of Research Square Company, we’re committed to making research communication faster, fairer, and more useful. We do this by developing innovative software and high quality services for the global research community. Our growing team is made up of researchers and industry professionals working together to solve the most critical problems facing scientific publishing. Also discoverable on Platform About Our Team In Review Editorial Policies Advisory Board Help Center Resources Author Services Accessibility API Access RSS feed Manage Cookie Preferences © Research Square 2026 | ISSN 2693-5015 (online) Privacy Policy Terms of Service Do Not Sell My Personal Information {"props":{"pageProps":{"initialData":{"identity":"rs-52543","acceptedTermsAndConditions":true,"allowDirectSubmit":true,"archivedVersions":[],"articleType":"Research","associatedPublications":[],"authors":[{"id":1202625,"identity":"7621f732-dcfc-4114-be2c-fd7a6fdb18fb","order_by":0,"name":"Hehua Zhang","email":"","orcid":"","institution":"Shengjing Hospital of China Medical University","correspondingAuthor":false,"submittingAuthor":false,"prefix":"","firstName":"Hehua","middleName":"","lastName":"Zhang","suffix":""},{"id":1202626,"identity":"3d25b988-e582-48a1-84a3-682e405c11ef","order_by":1,"name":"Yuhong Zhao","email":"data:image/png;base64,iVBORw0KGgoAAAANSUhEUgAAAZAAAAAyAQMAAABI0h/eAAAABlBMVEX///8AAABVwtN+AAAACXBIWXMAAA7EAAAOxAGVKw4bAAABFklEQVRIie2RsWrDMBCGzwjkDk5mGQWnL1CQMWSr8yo1Anvp4NGTkTGoS6Grn6SziiFd+gCGdkiXdOkQyJIhhUqkkKUy7VaovkEnxH2cfgnA4fiLEMCmIL3RMICp3zTr7S8UBjjo27j7gQJHRY/BpJD0bMRgzzeb9b6qfaBtvyvLwxyHr4ICpNGFsCgvqohvn3oEs1VOO8ZiSTORlMCThbIow9WKTKTSWa4XKGDMMwrvQGX3ViWT4YesjZLstLKU4YPog1GFYzqRyCiMaiWTxGvaMSUcckxnJgvJTZaEyyBrvY7Zs0yHYhO+VzUHwvWLHaLLO//xbb+t0simnH+d86Uy/3m68Pfthrk41tQsyN7ncDgc/5lPXuZXSPxYnOMAAAAASUVORK5CYII=","orcid":"https://orcid.org/0000-0003-4265-6692","institution":"Shengjing Hospital of China Medical University","correspondingAuthor":true,"submittingAuthor":false,"prefix":"","firstName":"Yuhong","middleName":"","lastName":"Zhao","suffix":""}],"badges":[],"createdAt":"2020-08-02 11:09:10","currentVersionCode":1,"declarations":"","doi":"10.21203/rs.3.rs-52543/v1","doiUrl":"https://doi.org/10.21203/rs.3.rs-52543/v1","draftVersion":[],"editorialEvents":[],"editorialNote":"","failedWorkflow":false,"files":[{"id":1809010,"identity":"c4920b07-719c-469c-9b29-fdd6d806b0be","added_by":"auto","created_at":"2020-08-05 22:23:44","extension":"png","order_by":1,"title":"Figure 1","display":"","copyAsset":false,"role":"figure","size":292676,"visible":true,"origin":"","legend":"Distributions of participants and PM2.5 exposure. Note: The designations employed and the presentation of the material on this map do not imply the expression of any opinion whatsoever on the part of Research Square concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. This map has been provided by the authors.","description":"","filename":"Fig1.png","url":"https://assets-eu.researchsquare.com/files/rs-52543/v1/Fig1.png"},{"id":1809011,"identity":"80484108-aafc-4194-bec4-cbb60bff0bd9","added_by":"auto","created_at":"2020-08-05 22:23:44","extension":"png","order_by":2,"title":"Figure 2","display":"","copyAsset":false,"role":"figure","size":64436,"visible":true,"origin":"","legend":"Stratified analysis according to gender, race and diabetes.","description":"","filename":"Fig2.png","url":"https://assets-eu.researchsquare.com/files/rs-52543/v1/Fig2.png"},{"id":13570023,"identity":"e6d8c102-2285-4b98-ae8d-c81bfe2b2757","added_by":"auto","created_at":"2021-09-17 03:42:23","extension":"pdf","order_by":0,"title":"","display":"","copyAsset":false,"role":"manuscript-pdf","size":594086,"visible":true,"origin":"","legend":"","description":"","filename":"manuscript.pdf","url":"https://assets-eu.researchsquare.com/files/rs-52543/v1/5a595bf3-f528-4925-9f1c-e255a03c71d5.pdf"},{"id":1809013,"identity":"e2c95958-502e-4adc-85f3-3be037ed4b7f","added_by":"auto","created_at":"2020-08-05 22:23:45","extension":"docx","order_by":1,"title":"","display":"","copyAsset":false,"role":"supplement","size":16874,"visible":true,"origin":"","legend":"","description":"","filename":"supplementalmaterials.docx","url":"https://assets-eu.researchsquare.com/files/rs-52543/v1/supplementalmaterials.docx"}],"financialInterests":"","formattedTitle":"Effects of long-term particulate matter exposure on platelet counts in adults of Northeast China","fulltext":[{"header":"1. Introduction","content":" \u003cp\u003ePrevious studies showed that acute and long-term exposure to air pollution (especially particulate matter\u0026thinsp;\u0026lt;\u0026thinsp;2.5\u0026nbsp;\u0026micro;m, i.e. PM\u003csub\u003e2.5\u003c/sub\u003e) were both associated with higher morbidity and mortality of cardiovascular diseases\u003csup\u003e[\u003cspan citationid=\"CR1\" class=\"CitationRef\"\u003e1\u003c/span\u003e, \u003cspan citationid=\"CR2\" class=\"CitationRef\"\u003e2\u003c/span\u003e]\u003c/sup\u003e. Studies in animals also showed that exposure to PM\u003csub\u003e2.5\u003c/sub\u003e increases blood coagulability, which accelerates atherosclerosis progression and results in vascular diseases\u003csup\u003e[\u003cspan citationid=\"CR3\" class=\"CitationRef\"\u003e3\u003c/span\u003e, \u003cspan citationid=\"CR4\" class=\"CitationRef\"\u003e4\u003c/span\u003e]\u003c/sup\u003e. Underlying mechanisms relating air pollution exposure to cardiovascular diseases include platelet activation, oxidative stress and interplay between interleukin-6 and tissue factors\u003csup\u003e[\u003cspan citationid=\"CR5\" class=\"CitationRef\"\u003e5\u003c/span\u003e, \u003cspan citationid=\"CR6\" class=\"CitationRef\"\u003e6\u003c/span\u003e]\u003c/sup\u003e, of which increased platelet count is associated with increased blood coagulability and cardiovascular disease mortality\u003csup\u003e[\u003cspan citationid=\"CR7\" class=\"CitationRef\"\u003e7\u003c/span\u003e, \u003cspan citationid=\"CR8\" class=\"CitationRef\"\u003e8\u003c/span\u003e]\u003c/sup\u003e. Previous epidemiological studies on associations between air pollution and platelet counts gave inconsistent results and mainly concentrated on short-term exposure assessment\u003csup\u003e[\u003cspan citationid=\"CR9\" class=\"CitationRef\"\u003e9\u003c/span\u003e, \u003cspan citationid=\"CR10\" class=\"CitationRef\"\u003e10\u003c/span\u003e]\u003c/sup\u003e. Studies of the effects of long-term air pollution exposure on platelet counts in large populations are limited\u003csup\u003e[\u003cspan citationid=\"CR11\" class=\"CitationRef\"\u003e11\u003c/span\u003e]\u003c/sup\u003e, especially in Asian populations.\u003c/p\u003e \u003cp\u003eIn this study, we aim to explore the associations between long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure and platelet counts in adults in Northeast China based on a large cohort population. Results may provide more evidence of associations between long-term air pollution exposure and cardiovascular diseases.\u003c/p\u003e "},{"header":"2. Materials And Methods","content":" \u003cdiv id=\"Sec3\" class=\"Section2\"\u003e \u003ch2\u003e2.1. Study participants\u003c/h2\u003e \u003cp\u003eParticipants in this study came from a large prospective natural population cohort in Northeast China, which is supported by the National K\u0026amp;D Project of China. The cohort consisted of four sub-cohorts: adults in city and county, maternal-children, special job exposures and health management. There were 30,000 adults in city and country included in this study. All participants responded to questionnaires and received physical examinations and blood tests. We excluded participants who did not provide detailed living addresses or complete blood platelet count tests, and 25,355 participants were included in the final analysis. The protocol of this study was approved by the Ethics Committee of the Shengjing Hospital of China Medical University (No. 2017PS190K).\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec4\" class=\"Section2\"\u003e \u003ch2\u003e2.2. Air pollution exposure assessment\u003c/h2\u003e \u003cp\u003eWe use two-year average PM\u003csub\u003e2.5\u003c/sub\u003e concentration for the living address of each participant as the measure of long-term air pollution exposure. All participants were from Liaoning Province. Annual land use regression model based on 78 national monitoring stations were used to construct land use regression model and predict air pollution exposure, the method of which was described in detail in our previous study\u003csup\u003e[\u003cspan citationid=\"CR12\" class=\"CitationRef\"\u003e12\u003c/span\u003e]\u003c/sup\u003e. Addresses of each participant were transformed into latitude and longitude data and imported into ArcGIS 10.3. Then we estimated average PM\u003csub\u003e2.5\u003c/sub\u003e concentration for the year of the blood test and the previous year separately for each participant. The two-year average PM\u003csub\u003e2.5\u003c/sub\u003e concentration value was used as long-term ambient PM\u003csub\u003e2.5\u003c/sub\u003e exposure.\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec5\" class=\"Section2\"\u003e \u003ch2\u003e2.3. Platelet counts test\u003c/h2\u003e \u003cp\u003eAll blood routine examinations were conducted in the Laboratory Department in Shengjing Hospital of China Medical University. Platelet count was included in the routine blood examination. The normal reference range of platelet counts is 100\u0026thinsp;\u0026times;\u0026thinsp;10\u003csup\u003e9\u003c/sup\u003e to 350\u0026thinsp;\u0026times;\u0026thinsp;10\u003csup\u003e9\u003c/sup\u003e/ml. Tests of fasting blood-glucose and blood lipids were also included.\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec6\" class=\"Section2\"\u003e \u003ch2\u003e2.4. Other factors involved\u003c/h2\u003e \u003cp\u003eAge, gender, race, income, status of education, smoking and alcohol drinking, indoor decoration in the previous five years, activity time per week, white blood cell (WBC) counts and presence of hypertension, diabetes, hyperlipemia and heart disease were included in the final analysis due to their confounding effects on the association between long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure and platelet counts\u003csup\u003e[\u003cspan citationid=\"CR13\" class=\"CitationRef\"\u003e13\u003c/span\u003e]\u003c/sup\u003e. Race was divided into Han, Manchu and others. Education level was divided into three categories according to education duration: \u0026lt;6, 6\u0026ndash;12 and \u0026gt;\u0026thinsp;12\u0026nbsp;years. Smoking and alcohol drinking status were divided into current, ever and never. Activity degree was divided into three categories according to the physical exercise duration per week: \u0026lt;1, 1\u0026ndash;2 and \u0026gt;\u0026thinsp;2\u0026nbsp;h. Hypertension was defined as average systolic pressure of three separate measures over 140\u0026nbsp;mmHg or average diastolic pressure of three separate measures over 90\u0026nbsp;mmHg. Diabetes was defined as fasting blood-glucose over 7\u0026nbsp;mmol/L. Heart disease was self-reported in the questionnaire. Hyperlipemia was defined as total cholesterol over 6.2\u0026nbsp;mmol/L, low-density lipid cholesterol over 4.1\u0026nbsp;mmol/L, triglyceride over 5.2\u0026nbsp;mmol/L or high-density lipid cholesterol below 1\u0026nbsp;mmol/L.\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec7\" class=\"Section2\"\u003e \u003ch2\u003e2.5. Statistical analysis\u003c/h2\u003e \u003cp\u003eWe defined elevated platelet count as a platelet count over the 90th percentile. Continuous variables are presented as least square means with 95% confidence intervals (CIs), and categorical variables are presented as total counts with percentages. Variance analyses and c\u003csup\u003e2\u003c/sup\u003e tests were conducted between each variable and platelet elevation. We used different logistic models to examine the associations between every 1\u0026nbsp;\u0026micro;g/m\u003csup\u003e3\u003c/sup\u003e increment of PM\u003csub\u003e2.5\u003c/sub\u003e exposure and elevated platelet count. Model 1 was used to calculate crude odds ratios (ORs). Model 2 was adjusted for age, gender, race, education, income and body mass index (BMI). Model 3 was further adjusted for status of smoking and alcohol drinking, decoration in the previous five years, hypertension, diabetes, heart disease, hyperlipemia, activity per week and WBC counts. We also divided PM\u003csub\u003e2.5\u003c/sub\u003e exposure into four categories according to quartile and used the first quartile as a reference to calculate the effects of PM\u003csub\u003e2.5\u003c/sub\u003e exposure in other quartiles on platelet elevation. Effects of interactions of PM\u003csub\u003e2.5\u003c/sub\u003e exposure with other involved factors on platelet elevation were examined separately. Further stratified analysis was conducted based on significant interactions of confounding factors with PM\u003csub\u003e2.5\u003c/sub\u003e exposure. Several sensitivity analyses were conducted, and mixed linear analyses were used to examine the linear associations between PM\u003csub\u003e2.5\u003c/sub\u003e exposure and log-transformed platelet counts. Elevated platelet count was defined as a platelet count over the 75th percentile for the logistic analysis. All analyses were conducted using SAS version 9.4 and SPSS version 25.0.\u003c/p\u003e \u003c/div\u003e "},{"header":"3. Results","content":" \u003cp\u003eGeneral characteristics of the study participants are shown in Table\u0026nbsp;\u003cspan refid=\"Tab1\" class=\"InternalRef\"\u003e1\u003c/span\u003e. Among the 25,355 participants, 9.7% (n\u0026thinsp;=\u0026thinsp;2467) were categorized as having platelet elevation. There were significant effects on platelet elevation of age, gender, race, education level, status of smoking and alcohol drinking, indoor decoration, activity per week, WBC counts and having hypertension, heart disease or hyperlipemia.\u003c/p\u003e \u003cp\u003e \u003cdiv class=\"gridtable\"\u003e\u003ctable float=\"Yes\" id=\"Tab1\" border=\"1\"\u003e \u003ccaption language=\"En\"\u003e \u003cdiv class=\"CaptionNumber\"\u003eTable 1\u003c/div\u003e \u003cdiv class=\"CaptionContent\"\u003e \u003cp\u003eGeneral characteristics of the study participants.\u003c/p\u003e \u003c/div\u003e \u003c/caption\u003e \u003ccolgroup cols=\"5\"\u003e \u003cthead\u003e \u003ctr\u003e \u003cth align=\"left\" colspan=\"2\" morerows=\"1\" nameend=\"c2\" namest=\"c1\" rowspan=\"2\"\u003e \u003cp\u003eCharacteristics\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colspan=\"2\" nameend=\"c4\" namest=\"c3\"\u003e \u003cp\u003ePlatelet counts\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c5\"\u003e \u003cp\u003eP-value\u003c/p\u003e \u003c/th\u003e \u003c/tr\u003e \u003ctr\u003e \u003cth align=\"left\" colname=\"c3\"\u003e \u003cp\u003e\u0026le;P90\u003csup\u003ea\u003c/sup\u003e (n\u0026thinsp;=\u0026thinsp;22,888)\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c4\"\u003e \u003cp\u003e\u0026gt;P90\u003csup\u003eb\u003c/sup\u003e (n\u0026thinsp;=\u0026thinsp;2467)\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c5\"\u003e\u0026nbsp;\u003c/th\u003e \u003c/tr\u003e \u003c/thead\u003e \u003ctbody\u003e \u003ctr\u003e \u003ctd align=\"left\" colspan=\"2\" nameend=\"c2\" namest=\"c1\"\u003e \u003cp\u003eAge, years\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e54.2 (54.1,54.4)\u003csup\u003ec\u003c/sup\u003e\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e51 (50.6,51.5)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003csup\u003ed\u003c/sup\u003e\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003eGender, n\u003csup\u003ee\u003c/sup\u003e (%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eMale\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e8126 (35.5)\u003csup\u003ef\u003c/sup\u003e\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e534 (21.7)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u0026nbsp;\u003csup\u003eg\u003c/sup\u003e\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eFemale\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e14761(64.5)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1932(78.3)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003eRace, n (%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eHan\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e14571(63.7)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1622(65.7)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003e0.006\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eManchu\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e8287(36.2)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e837(33.9)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eOther\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e30(0.1)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e8(0.3)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colspan=\"2\" nameend=\"c2\" namest=\"c1\"\u003e \u003cp\u003eIncome (10,000 Yuan)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e31.7(13.7,49.8)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e5.8(5.6,6)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e0.355\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colspan=\"2\" nameend=\"c2\" namest=\"c1\"\u003e \u003cp\u003eBMI, kg/m\u003csup\u003e2\u003c/sup\u003e\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e31(25.6,36.4)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e28.4(24.6,32.2)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e0.763\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003eEducation, n (%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e0\u0026ndash;6\u0026nbsp;years\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e5551(24.3)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e497(20.1)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e7\u0026ndash;12\u0026nbsp;years\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e13602(59.4)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1458(59.1)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e\u0026gt;\u0026thinsp;12\u0026nbsp;years\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e3735(16.3)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e512(20.8)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003eSmoke, n(%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eCurrent\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e3597(15.7)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e337(13.7)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eEver\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e1016(4.4)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e64(2.6)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eNever\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e18275(79.8)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e2066(83.7)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003eAlcohol, n(%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eCurrent\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e3996(17.5)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e361(14.6)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eEver\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e362(1.6)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e31(1.3)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eNever\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e18530(81)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e2075(84.1)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003eDecoration, n(%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eNo\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e18958(82.8)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1934(78.5)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eYes\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e3925(17.2)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e531(21.5)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003eHypertension, n(%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eNo\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e14425(63)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1640(66.5)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003e0.001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eYes\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e8463(37)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e827(33.5)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003eDiabetes, n(%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eNo\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e19906(87)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e2161(87.6)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003e0.38\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eYes\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e2982(13)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e306(12.4)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003eHeart disease, n(%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eNo\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e21390(93.5)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e2329(94.4)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003e0.068\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eYes\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e1498(6.5)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e138(5.6)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003eActivity, n(%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;1\u0026nbsp;h/week\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e10768(47)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1186(48.1)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"2\" rowspan=\"3\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e1\u0026ndash;2\u0026nbsp;h/week\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e2341(10.2)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e316(12.8)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e\u0026gt;\u0026thinsp;2\u0026nbsp;h/week\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e9779(42.7)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e965(39.1)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003eHyperlipemia, n(%)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eNo\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e18534(81)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1805(73.2)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eYes\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e4354(19)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e662(26.8)\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colspan=\"2\" nameend=\"c2\" namest=\"c1\"\u003e \u003cp\u003eWhite blood cell count (10\u003csup\u003e9\u003c/sup\u003e/ml)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e6.2(6.2,6.3)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e7.2(7.1,7.2)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colspan=\"2\" nameend=\"c2\" namest=\"c1\"\u003e \u003cp\u003ePM\u003csub\u003e2.5\u003c/sub\u003e exposure (\u0026micro;g/m\u003csup\u003e3\u003c/sup\u003e)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e36.8(36.7,36.8)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e37.7(37.5,37.9)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003c/tbody\u003e \u003c/colgroup\u003e \u003c/table\u003e\u003c/div\u003e \u003c/p\u003e \u003cp\u003ea, \u0026le;\u0026thinsp;90th percentile; b, \u0026gt;\u0026thinsp;90th percentile; c, least square means with 95% CI intervals \u0026ndash; applies to all such values; d, P-values of variance analyses \u0026ndash; applies to all such values; e, number of participants; f, total counts with percentages \u0026ndash; applies to all such values; g, P-values of c\u003csup\u003e2\u003c/sup\u003e tests \u0026ndash; applies to all such values.\u003c/p\u003e \u003cp\u003eAverage PM\u003csub\u003e2.5\u003c/sub\u003e exposure of all participants was 37.25\u0026nbsp;\u0026micro;g/m\u003csup\u003e3\u003c/sup\u003e with a significant difference between participants with elevated platelet counts and those without. Figure\u0026nbsp;\u003cspan refid=\"Fig1\" class=\"InternalRef\"\u003e1\u003c/span\u003e shows the distributions of participant locations and variation in PM\u003csub\u003e2.5\u003c/sub\u003e exposure across the whole study area.\u003c/p\u003e \u003cp\u003e \u003c/p\u003e \u003cp\u003eThe associations between PM\u003csub\u003e2.5\u003c/sub\u003e exposure and 90th percentile platelet elevations remained stable after adjusting for all possible confounders (Table\u0026nbsp;\u003cspan refid=\"Tab2\" class=\"InternalRef\"\u003e2\u003c/span\u003e). When PM\u003csub\u003e2.5\u003c/sub\u003e was treated as a continuous variable, the OR between every 1\u0026nbsp;\u0026micro;g/m\u003csup\u003e3\u003c/sup\u003e increment of PM\u003csub\u003e2.5\u003c/sub\u003e exposure and platelet elevation was 1.1 (95%CI: 1.08\u0026ndash;1.12). When PM\u003csub\u003e2.5\u003c/sub\u003e was treated as a categorical factor, compared with participants in the first quartile, those in the third (OR\u0026thinsp;=\u0026thinsp;1.28, 95%CI: 1.08\u0026ndash;1.52) and fourth (OR\u0026thinsp;=\u0026thinsp;2.18, 95%CI: 1.83\u0026ndash;2.60) quartiles were more likely to have elevated platelet counts.\u003c/p\u003e \u003cp\u003e \u003cdiv class=\"gridtable\"\u003e\u003ctable float=\"Yes\" id=\"Tab2\" border=\"1\"\u003e \u003ccaption language=\"En\"\u003e \u003cdiv class=\"CaptionNumber\"\u003eTable 2\u003c/div\u003e \u003cdiv class=\"CaptionContent\"\u003e \u003cp\u003eEffects of PM\u003csub\u003e2.5\u003c/sub\u003e exposure on 90th percentile platelet elevation.\u003c/p\u003e \u003c/div\u003e \u003c/caption\u003e \u003ccolgroup cols=\"7\"\u003e \u003cthead\u003e \u003ctr\u003e \u003cth align=\"left\" colname=\"c1\" morerows=\"1\" rowspan=\"2\"\u003e \u003cp\u003ePM\u003csub\u003e2.5\u003c/sub\u003e\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colspan=\"6\" nameend=\"c7\" namest=\"c2\"\u003e \u003cp\u003eOR (95%CI)\u003c/p\u003e \u003c/th\u003e \u003c/tr\u003e \u003ctr\u003e \u003cth align=\"left\" colname=\"c2\"\u003e \u003cp\u003eModel 1\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c3\"\u003e \u003cp\u003eP-value\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c4\"\u003e \u003cp\u003eModel 2\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c5\"\u003e \u003cp\u003eP-value\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c6\"\u003e \u003cp\u003eModel 3\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c7\"\u003e \u003cp\u003eP-value\u003c/p\u003e \u003c/th\u003e \u003c/tr\u003e \u003c/thead\u003e \u003ctbody\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\"\u003e \u003cp\u003e1\u0026nbsp;\u0026micro;g/m\u003csup\u003e3\u003c/sup\u003e increment\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e1.06 (1.05,1.08)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1.11(1.09,1.12)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c6\"\u003e \u003cp\u003e1.1(1.08,1.12)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c7\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\"\u003e \u003cp\u003e1st quartile\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003eRef\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e\u0026nbsp;\u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003eRef\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e\u0026nbsp;\u003c/td\u003e \u003ctd align=\"left\" colname=\"c6\"\u003e \u003cp\u003eRef\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c7\"\u003e\u0026nbsp;\u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\"\u003e \u003cp\u003e2st quartile\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e0.88(0.77,1.0)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e0.05\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1.07(0.92,1.25)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e0.37\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c6\"\u003e \u003cp\u003e1.1(0.94,1.29)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c7\"\u003e \u003cp\u003e0.24\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\"\u003e \u003cp\u003e3rd quartile\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e1.02(0.9,1.16)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e0.73\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e1.31(1.11,1.55)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e0.00\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c6\"\u003e \u003cp\u003e1.28(1.08,1.52)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c7\"\u003e \u003cp\u003e0.01\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\"\u003e \u003cp\u003e4st quartile\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e1.84(1.64,2.05)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003e2.21(1.88,2.59)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c6\"\u003e \u003cp\u003e2.18(1.83,2.6)\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c7\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\"\u003e \u003cp\u003eP-value for trend\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colspan=\"2\" nameend=\"c3\" namest=\"c2\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colspan=\"2\" nameend=\"c5\" namest=\"c4\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colspan=\"2\" nameend=\"c7\" namest=\"c6\"\u003e \u003cp\u003e\u0026lt;\u0026thinsp;0.0001\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003c/tbody\u003e \u003c/colgroup\u003e \u003c/table\u003e\u003c/div\u003e \u003c/p\u003e \u003cp\u003eModel 1, crude model; Model 2, adjusted for age, gender, race, education, income and BMI; Model 3, further adjusted for status of smoking and alcohol drinking, decoration in the previous five years, hypertension, diabetes, heart disease, hyperlipemia, activity per week and white blood cell counts.1st quartile, PM\u003csub\u003e2.5\u003c/sub\u003e \u0026le; 25th percentile; 2nd quartile, 25th percentile\u0026thinsp;\u0026lt;\u0026thinsp;PM\u003csub\u003e2.5\u003c/sub\u003e \u0026le;50th percentile; 3rd quartile, 50th percentile\u0026thinsp;\u0026lt;\u0026thinsp;PM\u003csub\u003e2.5\u003c/sub\u003e \u0026le;75th percentile; 4th quartile, PM\u003csub\u003e2.5\u003c/sub\u003e \u0026gt; 75th percentile.\u003c/p\u003e \u003cp\u003eModel 3 showed significant interactions of PM\u003csub\u003e2.5\u003c/sub\u003e exposure with gender (P\u0026thinsp;\u0026lt;\u0026thinsp;0.01), race (P\u0026thinsp;\u0026lt;\u0026thinsp;0.0001) and diabetes status (P\u0026thinsp;\u0026lt;\u0026thinsp;0.001). Figure\u0026nbsp;\u003cspan refid=\"Fig2\" class=\"InternalRef\"\u003e2\u003c/span\u003e shows the stratified analysis results according to gender (male and female), race (Han and Manchu) and diabetes (yes and no). Males were more likely to have platelet elevation after long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure compared with females. Those of Han ethnicity were more likely to have platelet elevation compared with Manchu ethnicity. Participants without diabetes were more likely to have platelet elevation after long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure.\u003c/p\u003e \u003cp\u003e \u003c/p\u003e \u003cp\u003eSensitivity analysis results are shown in Supplemental Tables\u0026nbsp;1 and 2. Analysis results for the mixed linear model between long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure and platelet counts showed that every 1\u0026nbsp;\u0026micro;g/m\u003csup\u003e3\u003c/sup\u003e increment of PM\u003csub\u003e2.5\u003c/sub\u003e exposure was associated with 0.29% (95%CI: 0.25\u0026ndash;0.32%) increase in platelet counts; and effects of PM\u003csub\u003e2.5\u003c/sub\u003e exposure were more evident in participants who were male, of Han ethnicity and without diabetes (Supplemental Table\u0026nbsp;1). Using the 75th percentile as the cut-off to define elevated platelet counts gave similar results (Supplemental Table\u0026nbsp;2) to those for the 90th percentile.\u003c/p\u003e "},{"header":"4. Discussion","content":" \u003cp\u003eTo our knowledge, this is the first cohort study in mainland China focusing on the association between long-term air pollution exposure and platelet counts. We found that long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure was associated with elevated platelet counts \u0026ndash; every 1\u0026nbsp;\u0026micro;g/m\u003csup\u003e3\u003c/sup\u003e increment of PM\u003csub\u003e2.5\u003c/sub\u003e exposure was associated with 0.29% increase in platelet counts and 10% higher risk of platelet elevation. Gender, race and diabetes status might interact with long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure in regard to platelet counts. Our findings add more evidence to determining the potential biological mechanisms relating air pollution exposure to cardiovascular disease.\u003c/p\u003e \u003cp\u003eResults of this study are similar to those of some previous studies focusing on the associations between short-term PM exposure and platelet activation (platelet count elevation or platelet aggregation)\u003csup\u003e[\u003cspan citationid=\"CR14\" class=\"CitationRef\"\u003e14\u003c/span\u003e, \u003cspan citationid=\"CR15\" class=\"CitationRef\"\u003e15\u003c/span\u003e, \u003cspan citationid=\"CR16\" class=\"CitationRef\"\u003e16\u003c/span\u003e]\u003c/sup\u003e in Europe and China. In a large cohort study of Taiwanese adults, long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure was associated with elevated platelet counts, but with a weaker effect than in our study, possibly because the Taiwanese study population was generally younger than in our study\u003csup\u003e[\u003cspan citationid=\"CR17\" class=\"CitationRef\"\u003e17\u003c/span\u003e]\u003c/sup\u003e. A prospective cohort study of German adults also found similar results, with every 2.4\u0026nbsp;\u0026micro;g/m\u003csup\u003e3\u003c/sup\u003e increment of PM\u003csub\u003e2.5\u003c/sub\u003e exposure associated with an adjusted increase of 2.3% in platelet counts\u003csup\u003e[\u003cspan citationid=\"CR18\" class=\"CitationRef\"\u003e18\u003c/span\u003e]\u003c/sup\u003e. Animal experiments also showed that repeat dose exposure of PM\u003csub\u003e2.5\u003c/sub\u003e triggered disseminated intravascular coagulation in Sprague Dawley rats with elevated platelet counts\u003csup\u003e[\u003cspan citationid=\"CR19\" class=\"CitationRef\"\u003e19\u003c/span\u003e]\u003c/sup\u003e.\u003c/p\u003e \u003cp\u003eWe also found significant differences in the effects of long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure on platelet elevation related to gender, race and diabetes of participants. Stronger associations between PM\u003csub\u003e2.5\u003c/sub\u003e exposure and platelet elevation were found for male participants, similar to previous studies\u003csup\u003e[\u003cspan citationid=\"CR20\" class=\"CitationRef\"\u003e20\u003c/span\u003e]\u003c/sup\u003e \u0026ndash; the biological mechanisms responsible might be the effects of different hormone levels in men and women, which may interact with chemicals in PM\u003csub\u003e2.5\u003c/sub\u003e \u003csup\u003e[\u003cspan citationid=\"CR21\" class=\"CitationRef\"\u003e21\u003c/span\u003e]\u003c/sup\u003e but more studies are required. Significant differences in platelet parameters as well as related risk factors have been found for European and Asian countries\u003csup\u003e[\u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e22\u003c/span\u003e]\u003c/sup\u003e, but race-related effects on platelet counts following long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure have seldom been mentioned. There were considerable proportions of Han and Manchu ethnicities among participants in our study. Research has revealed that frequencies of human platelet alloantigen alleles differ among Chinese ethnic groups\u003csup\u003e[\u003cspan citationid=\"CR23\" class=\"CitationRef\"\u003e23\u003c/span\u003e]\u003c/sup\u003e and associated risk factors differ among different races\u003csup\u003e[\u003cspan citationid=\"CR24\" class=\"CitationRef\"\u003e24\u003c/span\u003e]\u003c/sup\u003e, which might explain some of the effects of race on platelet counts with PM\u003csub\u003e2.5\u003c/sub\u003e exposure. Previous studies reported that the effect of ultra-fine particulates on thrombosis was significantly attenuated in diabetic subjects taking aspirin\u003csup\u003e[\u003cspan citationid=\"CR25\" class=\"CitationRef\"\u003e25\u003c/span\u003e, \u003cspan citationid=\"CR26\" class=\"CitationRef\"\u003e26\u003c/span\u003e]\u003c/sup\u003e, possibly explaining our results of weaker effects of long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure on platelet elevation in participants with diabetes. We found no significant effects of other cardiovascular-related risk factors such as age and BMI\u003csup\u003e[\u003cspan citationid=\"CR27\" class=\"CitationRef\"\u003e27\u003c/span\u003e]\u003c/sup\u003e, possibly because the average age of participants was over 40\u0026nbsp;years and the younger sub-group was relatively small.\u003c/p\u003e \u003cp\u003eThe biological pathway of platelet activation following PM\u003csub\u003e2.5\u003c/sub\u003e exposure remains unclear. A previous study showed that PM\u003csub\u003e2.5\u003c/sub\u003e exposure increased the methylation levels of CpG sites, with the function related to platelet activation, inflammation and oxidative stress\u003csup\u003e[\u003cspan citationid=\"CR14\" class=\"CitationRef\"\u003e14\u003c/span\u003e]\u003c/sup\u003e. Furthermore, more oxidative stress after PM\u003csub\u003e2.5\u003c/sub\u003e exposure reflected in an increased level of reactive oxygen species, which can also promote platelet activation, has been hypothesized as a possible mechanism\u003csup\u003e[\u003cspan citationid=\"CR14\" class=\"CitationRef\"\u003e14\u003c/span\u003e]\u003c/sup\u003e. Previous studies showed PM exposure was also associated with changes in fibrinogen levels, extracellular vesical release and miRNA content\u003csup\u003e[\u003cspan citationid=\"CR29\" class=\"CitationRef\"\u003e29\u003c/span\u003e]\u003c/sup\u003e; however, the biological pathway related to platelet activation or pro-thrombosis requires further research.\u003c/p\u003e \u003cp\u003eThis is the first cohort study in Northeast China to study the association between long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure and platelet counts. The large number of participants gave stable results, as shown by our sensitivity analysis. The abundant information from questionnaire and blood tests gave an assessment of a wide range of potential confounders, which allowed us to better characterize the associations and find new modifiers. Although this was a multi-center cohort study, all tests of platelet counts were from one laboratory, thus there was no heterogeneity in outcome definition, making our results reliable. However, there were some limitations in this study. First, although previous study demonstrated the predictive value of platelet counts for thrombosis and cardiovascular diseases\u003csup\u003e[\u003cspan citationid=\"CR30\" class=\"CitationRef\"\u003e30\u003c/span\u003e]\u003c/sup\u003e, using platelet counts alone to represent coagulation might limit the specificity blood coagulation assessment and future study should include more specific biomarkers. However, low test cost and easy availability make platelet counts more suitable for large-scale epidemiological studies compared to other biomarkers. Second, participants in our cohort were comparatively older than in previous studies, which might have resulted in a stronger correlation between PM\u003csub\u003e2.5\u003c/sub\u003e exposure and platelet elevation. Third, PM\u003csub\u003e2.5\u003c/sub\u003e level was comparatively higher than those reported in other countries, which might also explain the stronger correlation between PM\u003csub\u003e2.5\u003c/sub\u003e exposure and platelet elevation in our study, although this allowed us to investigate health effects of PM\u003csub\u003e2.5\u003c/sub\u003e exposure across a wider range.\u003c/p\u003e "},{"header":"5. Conclusion","content":" \u003cp\u003eWe explored the associations between long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure and platelet counts based on a prospective cohort study in Northeast China. We found long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure was associated with elevated platelet count. Gender, race and diabetes status interacted with the effect of long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure on platelet counts. Our findings add evidence concerning the potential biological mechanisms responsible for the relationship between air pollution exposure and cardiovascular disease. We recommend more epidemiological study on the interactions of air pollution exposure with race and disease status, and more basic research on the biological pathway of platelet count elevation after air pollution exposure.\u003c/p\u003e "},{"header":"Declarations","content":" \u003cp\u003e \u003ch2\u003eConflicts of interest\u003c/h2\u003e \u003cp\u003eThe authors declare that they have no competing financial interests.\u003c/p\u003e \u003ch2\u003eEthics approval and consent to participate\u003c/h2\u003e \u003cp\u003eThe protocol of this study was approved by the Institutional Review Board of Shengjing Hospital of China Medical University in 2017 (No. 2017PS190K).\u003c/p\u003e \u003ch2\u003eFunding\u003c/h2\u003e \u003cp\u003eThis work was supported by the National Key R\u0026amp;D Project of China (Grant number 2017YFC0907401, 2017) and the 345 Talent Project of Shengjing Hospital of China Medical University.\u003c/p\u003e \u003ch2\u003eAuthors\u0026rsquo; contributions\u003c/h2\u003e \u003cp\u003eZhang Hehua analyzed the data and wrote the paper; Zhao Yuhong designed the study process and reviewed the work.\u003c/p\u003e \u003ch2\u003eAcknowledgments\u003c/h2\u003e \u003cp\u003eWe thank the participants of the cohort for their kind cooperation and all cohort team workers for their hard work. We thank the Bureau of Meteorology and the Environmental Protection Bureau for providing original data of daily pollutant concentrations.\u003c/p\u003e "},{"header":"References","content":"\u003col\u003e\u003cli\u003e \u003cspan\u003eHamanaka RB, Mutlu GM. Particulate Matter Air Pollution: Effects on the Cardiovascular System[J]. Front Endocrinol (Lausanne). 2018;9:680.\u003c/span\u003e \u003c/li\u003e \u003cli\u003e \u003cspan\u003ePope CR, Turner MC, Burnett RT, et al. Relationships between fine particulate air pollution, cardiometabolic disorders, and cardiovascular mortality[J]. Circ Res. 2015;116(1):108\u0026ndash;15.\u003c/span\u003e \u003c/li\u003e \u003cli\u003e \u003cspan\u003eLiang S, Zhao T, Hu H, et al. Repeat dose exposure of PM2.5 triggers the disseminated intravascular coagulation (DIC) in SD rats[J]. Sci Total Environ. 2019;663:245\u0026ndash;53.\u003c/span\u003e \u003c/li\u003e \u003cli\u003e \u003cspan\u003eWu S, Deng F, Wei H, et al. 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Inhal Toxicol. 2012;24(12):831\u0026ndash;8.\u003c/span\u003e \u003c/li\u003e \u003cli\u003e \u003cspan\u003eDabass A, Talbott EO, Venkat A, et al. Association of exposure to particulate matter PM2.5 air pollution and biomarkers of cardiovascular disease risk in adult NHANES participants (2001\u0026ndash;2008). Int J Hyg Environ Health. 2016;219:301\u0026ndash;10.\u003c/span\u003e \u003c/li\u003e \u003cli\u003e \u003cspan\u003ePoursafa P, Kelishadi R. Air pollution, platelet activation and atherosclerosis. Inflamm Allergy Drug Targets. 2010;9:387\u0026ndash;92.\u003c/span\u003e \u003c/li\u003e \u003cli\u003e \u003cspan\u003ePergoli L, Cantone L, Favero C, et al. Extracellular vesicle-packaged miRNA release after short-term exposure to particulate matter is associated with increased coagulation. Part Fibre Toxicol. 2017;14(1):32.\u003c/span\u003e \u003c/li\u003e \u003cli\u003e \u003cspan\u003eAllen N, Barrett TJ, Guo Y, et al. 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Atherosclerosis. 2019;282:11\u0026ndash;8.\u003c/span\u003e \u003c/li\u003e\u003c/ol\u003e"}],"fulltextSource":"","fullText":"","funders":[],"hasAdminPriorityOnWorkflow":false,"hasManuscriptDocX":true,"hasOptedInToPreprint":true,"hasPassedJournalQc":"","hasAnyPriority":false,"hideJournal":true,"highlight":"","institution":"","isAcceptedByJournal":false,"isAuthorSuppliedPdf":false,"isDeskRejected":"","isHiddenFromSearch":false,"isInQc":false,"isInWorkflow":false,"isPdf":false,"isPdfUpToDate":true,"isWithdrawnOrRetracted":false,"journal":{"display":true,"email":"[email protected]","identity":"researchsquare","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":true,"externalIdentity":"","sideBox":"","snPcode":"","submissionUrl":"/submission","title":"Research Square","twitterHandle":"researchsquare","acdcEnabled":true,"dfaEnabled":false,"editorialSystem":"","reportingPortfolio":"","inReviewEnabled":false,"inReviewRevisionsEnabled":true},"keywords":"particulate matter, air pollution, platelet counts, cohort study","lastPublishedDoi":"10.21203/rs.3.rs-52543/v1","lastPublishedDoiUrl":"https://doi.org/10.21203/rs.3.rs-52543/v1","license":{"name":"CC BY 4.0","url":"https://creativecommons.org/licenses/by/4.0/"},"manuscriptAbstract":"\u003cp\u003eAssociations between air pollution exposure and platelet counts have been inconsistent in previous studies, and there have been few studies of effects of long-term exposure in Asian populations. We explored the associations between long-term PM\u003csub\u003e2.5\u003c/sub\u003e (particulate matter\u0026thinsp;\u0026lt;\u0026thinsp;2.5\u0026nbsp;\u0026micro;m) exposure and platelet counts using a prospective cohort study in Northeast China. We used a logistic regression model to analyze the effects of different PM\u003csub\u003e2.5\u003c/sub\u003e increments and platelet count elevation. Mixed linear models were used to analyze the association between PM\u003csub\u003e2.5\u003c/sub\u003e concentration and platelet counts. Interaction and stratified analyses were also conducted. Results showed that every 1\u0026nbsp;\u0026micro;g/m\u003csup\u003e3\u003c/sup\u003e increment of PM\u003csub\u003e2.5\u003c/sub\u003e exposure was associated with 0.29% (95%CI: 0.25\u0026ndash;0.32%) increase in platelet counts and 10% (95%CI: 8\u0026ndash;12%) higher risk of platelet elevation. Effects of long-term PM\u003csub\u003e2.5\u003c/sub\u003e exposure on platelet elevation were stronger in male participants, of Han ethnicity, and without diabetes. Our findings add more evidence to the potential biological mechanisms responsible for the effect of air pollution exposure on cardiovascular disease.\u003c/p\u003e","manuscriptTitle":"Effects of long-term particulate matter exposure on platelet counts in adults of Northeast China","msid":"","msnumber":"","nonDraftVersions":[{"code":1,"date":"2020-08-05 22:21:40","doi":"10.21203/rs.3.rs-52543/v1","editorialEvents":[{"type":"communityComments","content":0}],"status":"published","journal":{"display":true,"email":"[email protected]","identity":"researchsquare","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":true,"externalIdentity":"","sideBox":"","snPcode":"","submissionUrl":"/submission","title":"Research Square","twitterHandle":"researchsquare","acdcEnabled":true,"dfaEnabled":false,"editorialSystem":"","reportingPortfolio":"","inReviewEnabled":false,"inReviewRevisionsEnabled":true}}],"origin":"","ownerIdentity":"afeeb5bc-9d9b-403b-b096-56c5f98c132c","owner":[],"postedDate":"August 5th, 2020","published":true,"recentEditorialEvents":[],"rejectedJournal":[],"revision":"","amendment":"","status":"posted","subjectAreas":[{"id":248526,"name":"Health Economics \u0026 Outcomes Research"},{"id":248527,"name":"Health Policy"}],"tags":[],"updatedAt":"2020-08-05T22:23:48+00:00","versionOfRecord":[],"versionCreatedAt":"2020-08-05 22:21:40","video":"","vorDoi":"","vorDoiUrl":"","workflowStages":[]},"version":"v1","identity":"rs-52543","journalConfig":"researchsquare"},"__N_SSP":true},"page":"/article/[identity]/[[...version]]","query":{"redirect":"/article/rs-52543","identity":"rs-52543","version":["v1"]},"buildId":"7rjqhiLT3MXkJMwkYKINL","isFallback":false,"isExperimentalCompile":false,"dynamicIds":[84888],"gssp":true,"scriptLoader":[]}

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