About the Authors:
Sungjin Park
Roles Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Project administration, Resources, Visualization, Writing – original draft, Writing – review & editing
Affiliation: Department of Occupational and Environmental Medicine, Cheonan Medical Center, Cheonan, Korea
ORCID logo http://orcid.org/0000-0002-9240-9684
Jung Ran Choi
Roles Conceptualization, Methodology, Project administration, Validation, Writing – original draft, Writing – review & editing
Affiliation: Institute of Genomic Cohort, Wonju College of Medicine, Yonsei University, Wonju, Korea
Sung-Kyung Kim
Roles Conceptualization, Data curation, Investigation, Writing – review & editing
Affiliations Department of Occupational and Environmental Medicine, Wonju Severance Christian Hospital, Wonju College of Medicine, Yonsei University, Wonju, Korea, Department of Preventive Medicine, Wonju College of Medicine, Yonsei University, Wonju, Korea, Institute of Occupational and Environmental Medicine, Wonju College of Medicine, Yonsei University, Wonju, Korea
Solam Lee
Roles Writing – review & editing
Affiliation: Department of Preventive Medicine, Wonju College of Medicine, Yonsei University, Wonju, Korea
Kyungsuk Lee
Roles Writing – review & editing
Affiliation: National Academy of Agricultural Science, Rural Development Administration, Jeonju, Korea
Jang-Young Kim
Roles Supervision, Validation, Writing – review & editing
Affiliations Institute of Genomic Cohort, Wonju College of Medicine, Yonsei University, Wonju, Korea, Division of Cardiology, Internal Medicine, Wonju College of Medicine, Yonsei University, Wonju, Korea
Sung-Soo Oh
Roles Conceptualization, Data curation, Investigation, Project administration, Writing – review & editing
Affiliations Department of Occupational and Environmental Medicine, Wonju Severance Christian Hospital, Wonju College of Medicine, Yonsei University, Wonju, Korea, Department of Preventive Medicine, Wonju College of Medicine, Yonsei University, Wonju, Korea, Institute of Occupational and Environmental Medicine, Wonju College of Medicine, Yonsei University, Wonju, Korea
Sang-Baek Koh
Roles Conceptualization, Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Project administration, Software, Supervision, Writing – review & editing
* E-mail: [email protected]
Affiliations Institute of Genomic Cohort, Wonju College of Medicine, Yonsei University, Wonju, Korea, Department of Occupational and Environmental Medicine, Wonju Severance Christian Hospital, Wonju College of Medicine, Yonsei University, Wonju, Korea, Department of Preventive Medicine, Wonju College of Medicine, Yonsei University, Wonju, Korea, Institute of Occupational and Environmental Medicine, Wonju College of Medicine, Yonsei University, Wonju, Korea, Center for Global Health and Social Medicine, Institute of Poverty Alleviation and International Development, Yonsei University, Wonju, Korea
Introduction
Atherosclerosis is a systemic disorder that develops gradually and is characterized by chronic inflammation of the blood vessels [1], which may lead to fatal complications such as myocardial infarction or coronary artery disease [2]. Several risk factors for atherosclerosis include family history, aging, obesity, physical inactivity, hypertension, diabetes mellitus, and hyperlipidemia [3].
With the recently growing concern and interest for environmental chemicals, pesticide exposure is emerging as a risk factor for atherosclerosis [4,5]. Although pesticide exposure has been linked with cardiovascular diseases [6,7] and serum levels of organochlorine (OC) pesticides are associated with several forms of atherosclerosis [8,9], the association between pesticide exposure and atherosclerosis is unclear. Moreover, previous studies on this issue have not provided consistent results [10], prompting the need for further investigation.
One main reason for the insufficient evidence in this field would be adversities to accurately assess exposure to pesticides. The exposure assessment using biomarkers of pesticides has been used restrictively due to the low specificity of metabolites and technological constraints [11]. As an alternative option, the assessment of pesticide exposure using questionnaires of patient recall of exposure is the only available approach to estimate cumulative exposure in lifetime [12]. This alternative measurement of pesticide exposure has been widely utilized to evaluate the effects of pesticides on several health outcomes [13,14].
Therefore, this study aimed to explore the association between pesticide exposure and the risk of atherosclerosis using a questionnaire which has been validated to measure exposure to pesticides [15,16]. Since carotid intima-media thickness (CIMT) is a useful indicator of atherosclerosis [17] and cardiovascular events [18], the risk of atherosclerosis was estimated using CIMT.
Methods and materials
Study population
This study is a part of the Korean Genome and Epidemiology Study (KoGES), a population-based prospective study aimed to identify risk factors of widespread chronic diseases such as hypertension, diabetes, metabolic syndrome, cardiovascular disease, and atherosclerosis. KoGES has been employed for a wide range of research on health problems of rural populations [19,20]. This cross-sectional study was conducted based on baseline survey data of the Korea Farmers Cohort Study. The first wave was conducted between November 2005 and January 2008.
Participants of the study were the residents of the rural regions of Wonju and Pyeongchang, Gangwon-do, Korea, comprising farmers, farm managers, and other occupations. All participants provided written informed consent prior to enrollment. Of the total 3,162 participants who were included in the baseline survey, 2,568 remained after excluding those with no available information on pesticide exposure. Schedule unavailability and space limitations in the carotid ultrasonography clinic decreased the number of participants to 501 individuals, each of whom voluntarily agreed to undergo carotid ultrasonography. Finally, 477 individuals were included in the statistical analysis after 16 participants with a history of myocardial infarction or stroke and 8 who were on medication for dyslipidemia were excluded (Fig 1). This study was approved by the Institutional Review Board of Wonju Severance Christian Hospital.
[Figure omitted. See PDF.]
Fig 1. Flowchart of study population the KoGES data.
https://doi.org/10.1371/journal.pone.0232531.g001
Data collection
Participants of the baseline survey were interviewed by skilled interviewers using standardized questionnaires and inspected by thorough medical examinations. The questionnaires included age, sex, personal medical history (cardiovascular events such as myocardial infarction and stroke and pharmacological treatment of hypertension, diabetes, and dyslipidemia), and lifestyle behavior (smoking, drinking, and exercise). Comprehensive health examinations included anthropometric and blood pressure measurement, venous blood sampling, urine analysis, and carotid ultrasonography for CIMT. Additional details about data compilation have been mentioned elsewhere [21]. Information on pesticide exposure was collected using a revised questionnaire developed by the Agricultural Health Study [22].
Covariates
Participants were divided into three groups based on their ages: 1) 39–49 years, 2) 50–59 years, and 3) ≥60 years. Obesity was defined as body mass index of ≥25 kg/m2. Current smoking, alcohol consumption, and exercise were treated as dichotomous variables. Current medication for chronic diseases, such as hypertension and diabetes, was also included in the analysis.
Assessment of pesticide exposure
Interviewers used a modified questionnaire developed by the Agricultural Health Study [22] to obtain information about pesticide use or exposure from the respondents. Participants were asked about their experience in farming, using pesticides, as well as the number of years of pesticide use and the number of days of pesticide use in a year.
Because multiple factors may influence the level of exposure to pesticides, the questionnaires for pesticide exposure assessment include action of pesticide use (e.g., application, mixing), mode of application (e.g., hand spray, backpack), use of personal protective equipment (PPE) (e.g., rubber gloves, respirators), and personal work practices and hygiene (e.g., changing into clean clothes or taking a bath after pesticide use). Accordingly, the intensity of exposure and cumulative exposure index (CEI) were generated as follows [22]:
For mixing status, two groups were made (never mixed and mixed, rated 0 and 9, respectively), and eight categories were grouped for the application method (never applied, aerial-aircraft, in furrow/banded, boom on tractor, backpack, hand spray, mist blower/fogger, and airblast, which had six scales, assigned 0, 1, 2, 3, 8, 9, 9, and 9, respectively). Repair status of equipment was divided into two groups (yes or no), and PPE was scored according to the type and use of protective equipment. Supplemental information has been provided elsewhere [22,23].
Several factors related with pesticide exposure were included in the analysis, such as one’s experience of being a farmer, of using pesticides, the number of years and days of using pesticide, and CEI of pesticide exposure. Both the duration (<1, 1–20, and ≥20 years) and frequency (0, 1–10, and ≥10 average days per year) of pesticide use were divided into three groups each. Similarly, both intensity level and CEI of pesticide exposure were split into three groups using the median value (0, lower than the median, and higher than the median).
Measurement of CIMT & atherosclerosis
As mentioned previously [24], a “brightness” mode ultrasound system (Vivid 7, General Electric Vingmed) and a transducer with 12 MHz frequency and longitudinal two-dimensional ultrasonography imaging were used to inspect the carotid artery. The imaging technique of ultrasound determined the thickness of the bilateral carotid intima-media. The far wall of the carotid artery was separated into two bright lines by a hypoechoic space. A software for semi-automated edge detection was applied to determine CIMT between the leading edge of the first bright line and that of the second bright line (between lumen-intima interface and media-adventitia interface). Values of CIMT exceeding 2 cm were assessed 1 cm proximal to the bulb. The average of maximal values of CIMT on the bilateral sides was used as an indicator of subclinical atherosclerosis [21,25].
Because CIMT is regarded as a predictor of cardiovascular incidents and is often used as a marker of subclinical atherosclerosis [26], we defined atherosclerosis as CIMT ≥0.9 mm [21,27].
Statistical analysis
SAS software version 9.4 (SAS Institute, Inc., Cary, North Carolina) was applied to all analyses. Chi-square tests were used to show significant associations between CIMT and pesticide exposure. Multiple logistic regression analyses were used to compute odds ratios (ORs), 95% confidence intervals (CIs), and c-statistic. Adjusted models included several risk factors for atherosclerosis, including sex, age, obesity, smoking status, alcohol intake, regular exercise, and pharmacological treatment of hypertension or diabetes. C-statistic is an indicator with predictive power considered equal to that of the receiver operating characteristic curve. It ranges from 0.5 to 1, where a randomly predictive model has a value of 0.5 and a perfectly predictive model has a value of 1. For all analyses, p-value <0.05 was determined as having statistical significance.
Results
Table 1 describes general characteristics of the study population. Most participants in this study were men; were in their 50s; were of normal weight; and did not smoke, drink alcohol, or exercise regularly. Only 13% of the population was being treated pharmacologically for hypertension or diabetes, and 9% had an increased CIMT of ≥0.9 mm. A comparison of the groups with and without CIMT measurement data is shown in S1 Table. Among all variables, only age group differed significantly between the two groups (p = 0.0431); the individuals with CIMT measurements were younger than those without CIMT measurements. This indicated possible underestimation of CIMT risk due to the generally younger participants of the group with CIMT measurements.
[Figure omitted. See PDF.]
Table 1. General description of the study population (N = 477).
https://doi.org/10.1371/journal.pone.0232531.t001
Table 2 shows factors related to pesticide exposure that were significantly associated with increased CIMT. Number of participants with CIMT of ≥0.9 mm was significantly higher in those who had been a farmer, a history of pesticide use, or higher or lower cumulative exposure.
[Figure omitted. See PDF.]
Table 2. CIMT according to pesticide exposure.
https://doi.org/10.1371/journal.pone.0232531.t002
Table 3 shows ORs and 95% CIs for atherosclerosis according to pesticide exposure from the model adjusted for sex, age, obesity, smoking, alcohol intake, exercise, and the pharmacological treatment of hypertension or diabetes. In the adjusted model, those who had been a farmer (OR 3.25 95% CI 1.51–6.98), used any pesticides (OR 3.42 95% CI 1.63–7.16), used pesticides for 10 times a year or more (OR 2.55 95% CI 1.21–5.39), and had a higher CEI (OR 3.63 95% CI 1.65–7.97) were significantly associated with an increased risk of atherosclerosis. The risk of atherosclerosis was not significantly associated with the prolonged duration of pesticide use, pesticide use of <10 times per year, and intensity level of pesticide exposure.
[Figure omitted. See PDF.]
Table 3. Association between increased risk of atherosclerosis and pesticide exposure.
https://doi.org/10.1371/journal.pone.0232531.t003
Discussion
This study’s findings suggest that the increased risk of atherosclerosis was significantly associated with pesticide exposure using CIMT and pesticide exposure assessment based on questionnaires. The pesticide exposure-related factors, including farming history, history of pesticide use, pesticide use of ≥10 times per year, and a higher level of CEI, were significantly associated with increased CIMT, after adjustment for sex, age, obesity, smoking status, alcohol intake, regular exercise, and current medication for hypertension or diabetes.
The result of this study seems similar to that of recent studies. A previous study reported that OC pesticides were related to the higher prevalence of peripheral artery diseases [8] and that elevated serum levels of OC pesticides were associated with the risk of atherosclerosis [9]. Meanwhile, other researchers found contrasting results wherein lower mortality from coronary artery disease was seen with higher exposure to herbicides [10]; and no significant relationship was reported between OC pesticides, polychlorinated biphenyls, and CIMT [4].
Atherosclerosis is accompanied by the accumulation and oxidation of low-density lipoproteins (LDLs) in the vessel walls. The inflammatory process begins at the site of oxidation with the accumulation of pro-inflammatory cytokines and immunocytes such as monocytes and T-lymphocytes [4].
Although the mechanism between pesticide exposure and atherosclerosis development is barely understood, increased levels of oxidative stress and alterations in lipid homeostasis may explain this process. Some experimental evidence suggests that OC and organophosphate (OP) pesticides contribute to the development of atherosclerosis through increased levels of reactive oxygen species, depletion of antioxidant defensive system, and increased peroxidation of lipids [28]. The findings of one study of Korean farmers [21] were in accordance with the abovementioned mechanism, which elucidated the role of oxidative stress in the pathway from pesticide exposure to subclinical atherosclerosis. Polychlorinated biphenyls pesticide was observed to influence the development of atherosclerosis by mediating endothelial dysfunction and increasing sensitivity to oxidative stress [8]. Additional evidence from experimental data suggested that OC pesticides accelerate the atherosclerotic process via direct oxygen toxicity to oxidize LDLs into a pro-atherogenic form and that OP pesticides disrupt the uptake and transport of cholesterols [28].
In this study, CIMT of ≥0.9 mm was employed to define atherosclerosis as it was validated by several studies [21,26,29]. CIMT is used as an indicator of progressive changes of atherosclerosis in general vessels as well as coronary arteries [26,30]. For patients with medical disorders, increased CIMT can be used as a complementary predictor of cardiovascular events [18,31]. Although it has been widely used because of its simplicity and usefulness, it also has several drawbacks, including the lack of standardized approach for measurement and low accuracy in assessing atherosclerosis. Therefore, future studies including other complementing markers such as carotid plaque and artery intima-media complex as well as CIMT are necessary to reflect diverse aspects of atherosclerosis.
Our study has several limitations. First, the nature of this study contained a cross-sectional design and thus could not establish a causal relationship; however, our findings can show the association between atherosclerosis and pesticide exposure, prompting the need for research on other possible risk factors. Second, detailed information on pesticides including their types, half-lives, and biological mechanisms was not included. At the survey phase of collecting information, participants were asked to answer specific questions on the duration and the types of pesticides they used, including the names of chemicals or products, partial product names, manufacturer names, targets or purposes, and formulation of products. Unfortunately, they had difficulty in describing them accurately [32] and, thus, most of them failed to answer the items correctly. However, studies have been performed on health effects of pesticide exposure using this method to evaluate exposure without the information on the type of pesticides [13,14,33,34]. Finally, only 501 of 2568 (approximately 20%) individuals who completed the pesticide exposure assessment agreed to undergo CIMT measurements for inclusion in this study. However, as shown in S1 Table, the general characteristics (except for age group) and pesticide-related factors did not differ significantly between the study population and the excluded group without CIMT measurement. Therefore, the selection bias in this study is considered not substantial, although it cannot be neglected.
This study suggests that pesticide exposure, which may occur occupationally in agricultural settings, plays a role in the development of atherosclerosis. Prospective studies with a larger sample size should be conducted to further investigate the effects of pesticide exposure on the risk of atherosclerosis.
Supporting information
[Figure omitted. See PDF.]
S1 Dataset.
https://doi.org/10.1371/journal.pone.0232531.s001
(XLS)
S1 File.
https://doi.org/10.1371/journal.pone.0232531.s002
(DOCX)
S2 File.
https://doi.org/10.1371/journal.pone.0232531.s003
(DOCX)
S1 Table. General characteristics of the participants who underwent CIMT measurements (study population) versus those who did not undergo CIMT measurements (excluded population).
https://doi.org/10.1371/journal.pone.0232531.s004
(DOCX)
Citation: Park S, Choi JR, Kim S-K, Lee S, Lee K, Kim J-Y, et al. (2020) Increased risk of atherosclerosis associated with pesticide exposure in rural areas in Korea. PLoS ONE 15(5): e0232531. https://doi.org/10.1371/journal.pone.0232531
1. Libby P, Ridker PM, Hansson GK, Leducq Transatlantic Network on A. Inflammation in atherosclerosis: from pathophysiology to practice. J Am Coll Cardiol. 2009;54: 2129–2138. pmid:19942084; Pubmed Central PMCID: PMC2834169.
2. Mallika V, Goswami B, Rajappa M. Atherosclerosis pathophysiology and the role of novel risk factors: a clinicobiochemical perspective. Angiology. 2007;58: 513–522. pmid:18024933.
3. Drager LF, Polotsky VY, Lorenzi-Filho G. Obstructive sleep apnea: an emerging risk factor for atherosclerosis. Chest. 2011;140: 534–542. pmid:21813534; Pubmed Central PMCID: PMC3198492.
4. Lind PM, van Bavel B, Salihovic S, Lind L. Circulating levels of persistent organic pollutants (POPs) and carotid atherosclerosis in the elderly. Environ Health Perspect. 2012;120: 38–43. pmid:22222676; Pubmed Central PMCID: PMC3261941.
5. Wahab A, Hod R, Ismail NH, Omar N. The effect of pesticide exposure on cardiovascular system: A systematic review. Int J Community Med Public Health. 2016;3: 1–10. https://doi.org/10.18203/2394-6040.ijcmph20151542.
6. Ha MH, Lee DH, Jacobs DR. Association between serum concentrations of persistent organic pollutants and self-reported cardiovascular disease prevalence: results from the National Health and Nutrition Examination Survey, 1999–2002. Environ Health Perspect. 2007;115: 1204–1209. pmid:17687448; Pubmed Central PMCID: PMC1940073.
7. Goncharov A, Haase RF, Santiago-Rivera A, Morse G, Akwesasne Task Force on the E, McCaffrey RJ, et al. High serum PCBs are associated with elevation of serum lipids and cardiovascular disease in a Native American population. Environ Res. 2008;106: 226–239. pmid:18054906; Pubmed Central PMCID: PMC2258089.
8. Min JY, Cho JS, Lee KJ, Park JB, Park SG, Kim JY, et al. Potential role for organochlorine pesticides in the prevalence of peripheral arterial diseases in obese persons: results from the National Health and Nutrition Examination Survey 1999–2004. Atherosclerosis. 2011;218: 200–206. pmid:21620405.
9. Mangum LC, Mangum LH, Chambers JE, Ross MK, Meek EC, Wills RW, et al. The association of serum trans-nonachlor levels with atherosclerosis. J Toxicol Environ Health A. 2016;79: 210–220. pmid:26953872; Pubmed Central PMCID: PMC4902318.
10. Schreinemachers DM. Mortality from ischemic heart disease and diabetes mellitus (type 2) in four U.S. wheat-producing states: a hypothesis-generating study. Environ Health Perspect. 2006;114: 186–193. pmid:16451853; Pubmed Central PMCID: PMC1367830.
11. Maroni M, Colosio C, Ferioli A, Fait A. Biological monitoring of pesticide exposure: A review. Introduction. Toxicology. 2000;143: 1–118. pmid:10675783.
12. Lee YH, Cha ES, Moon EK, Kong KA, Koh SB, Lee YK, et al. Reliability of self-reported information by farmers on pesticide use. J Prev Med Public Health. 2010;43: 535–542. pmid:21139414.
13. Kim JY, Park SJ, Kim SK, Kim CS, Kim TH, Min SH, et al. Pesticide exposure and cognitive decline in a rural South Korean population. PLoS One. 2019;14: e0213738. pmid:30897108; Pubmed Central PMCID: PMC6428296.
14. Park S, Kim SK, Kim JY, Lee K, Choi JR, Chang SJ, et al. Exposure to pesticides and the prevalence of diabetes in a rural population in Korea. Neurotoxicology. 2019;70: 12–18. pmid:30367900.
15. Coble J, Arbuckle T, Lee W, Alavanja M, Dosemeci M. The validation of a pesticide exposure algorithm using biological monitoring results. J Occup Environ Hyg. 2005;2: 194–201. pmid:15764542.
16. Thomas KW, Dosemeci M, Coble JB, Hoppin JA, Sheldon LS, Chapa G, et al. Assessment of a pesticide exposure intensity algorithm in the agricultural health study. J Expo Sci Environ Epidemiol. 2010;20: 559–569. pmid:19888312; Pubmed Central PMCID: PMC2935660.
17. de Groot E, Hovingh GK, Wiegman A, Duriez P, Smit AJ, Fruchart JC, et al. Measurement of arterial wall thickness as a surrogate marker for atherosclerosis. Circulation. 2004;109: III33–38. pmid:15198964.
18. Stein JH, Korcarz CE, Hurst RT, Lonn E, Kendall CB, Mohler ER, et al. Use of carotid ultrasound to identify subclinical vascular disease and evaluate cardiovascular disease risk: a consensus statement from the American Society of Echocardiography Carotid Intima-Media Thickness Task Force. Endorsed by the Society for Vascular Medicine. J Am Soc Echocardiogr. 2008;21: 93–111; quiz 189–190. pmid:18261694.
19. Youn YJ, Lee NS, Kim JY, Lee JW, Sung JK, Ahn SG, et al. Normative values and correlates of mean common carotid intima-media thickness in the Korean rural middle-aged population: the Atherosclerosis RIsk of Rural Areas iN Korea General Population (ARIRANG) study. J Korean Med Sci. 2011;26: 365–371. pmid:21394304; Pubmed Central PMCID: PMC3051083.
20. Ahn MS, Kim JY, Youn YJ, Kim SY, Koh SB, Lee K, et al. Cardiovascular parameters correlated with metabolic syndrome in a rural community cohort of Korea: the ARIRANG study. J Korean Med Sci. 2010;25: 1045–1052. pmid:20592897; Pubmed Central PMCID: PMC2890882.
21. Yoon JH, Kim JY, Park JK, Ko SB. Oxidative damage markers are significantly associated with the carotid artery intima-media thickness after controlling for conventional risk factors of atherosclerosis in men. PLoS One. 2015;10: e0119731. pmid:25806957; Pubmed Central PMCID: PMC4373810.
22. Dosemeci M, Alavanja MC, Rowland AS, Mage D, Zahm SH, Rothman N, et al. A quantitative approach for estimating exposure to pesticides in the Agricultural Health Study. Ann Occup Hyg. 2002;46: 245–260. pmid:12074034.
23. Lee KM, Park SY, Lee K, Oh SS, Ko SB. Pesticide metabolite and oxidative stress in male farmers exposed to pesticide. Ann Occup Environ Med. 2017;29: 5. pmid:28265414; Pubmed Central PMCID: PMC5331740.
24. Lee JH, Kim JY, Kim KM, Lee JW, Youn YJ, Ahn MS, et al. A prospective study of epicardial adipose tissue and incident metabolic syndrome: the ARIRANG study. J Korean Med Sci. 2013;28: 1762–1767. pmid:24339706; Pubmed Central PMCID: PMC3857372.
25. Takasu J, Budoff MJ, Katz R, Rivera JJ, O'Brien KD, Shavelle DM, et al. Relationship between common carotid intima-media thickness and thoracic aortic calcification: the Multi-Ethnic Study of Atherosclerosis. Atherosclerosis. 2010;209: 142–146. pmid:19782983; Pubmed Central PMCID: PMC2830343.
26. Ham SY, Song JW, Shim JK, Soh S, Kim HJ, Kwak YL. Prognostic role of carotid intima-media thickness in off-pump coronary artery bypass surgery. Sci Rep. 2018;8: 11385. pmid:30061728.
27. Mancia G, De Backer G, Dominiczak A, Cifkova R, Fagard R, Germano G, et al. 2007 Guidelines for the management of arterial hypertension: The Task Force for the Management of Arterial Hypertension of the European Society of Hypertension (ESH) and of the European Society of Cardiology (ESC). J Hypertens. 2007;25: 1105–1187. pmid:17563527.
28. Mangum LC. Pesticide toxicants and atherosclerosis: Role of oxidative stress and dysregulated lipid metabolism in human monocytes and macrophages. PhD diss., Mississippi State University. 2015. Available: https://search.proquest.com/docview/1679463756?accountid=15179.
29. Ataoglu HE, Saler T, Uzunhasan I, Yenigun M, Yigit Z, Temiz LU, et al. Additional value of carotid artery intima-media thickness in cardiovascular risk assessment by Framingham risk-score in Type 2 diabetes: a retrospective cohort study. J Diabetes. 2009;1: 188–193. pmid:20923538.
30. Pignoli P, Tremoli E, Poli A, Oreste P, Paoletti R. Intimal plus medial thickness of the arterial wall: a direct measurement with ultrasound imaging. Circulation. 1986;74: 1399–1406. pmid:3536154.
31. Johri AM, Hétu M-F, Nambi V. Carotid plaque or CIMT: what is the future for carotid US imaging? Curr Cardiovasc Risk Rep. 2014;8: 386. https://doi.org/https://doi.org/10.1007/s12170-014-0386-5.
32. Cha ES, Jeong M, Lee WJ. Agricultural pesticide usage and prioritization in South Korea. J Agromedicine. 2014;19: 281–293. pmid:24959760.
33. Li J, Dong L, Tian D, Zhao Y, Yang H, Zhi X, et al. Association between pesticide exposure intensity and self-rated health among greenhouse vegetable farmers in Ningxia, China. PLoS One. 2018;13: e0209566. pmid:30576364; Pubmed Central PMCID: PMC6303074.
34. Koh SB, Kim TH, Min S, Lee K, Kang DR, Choi JR. Exposure to pesticide as a risk factor for depression: A population-based longitudinal study in Korea. Neurotoxicology. 2017;62: 181–185. pmid:28720389.
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer
© 2020 Park et al. This is an open access article distributed under the terms of the Creative Commons Attribution License: http://creativecommons.org/licenses/by/4.0/ (the “License”), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited. Notwithstanding the ProQuest Terms and Conditions, you may use this content in accordance with the terms of the License.
Abstract
Atherosclerosis is a progressive inflammation in systemic vessels, and pesticide exposure has been emerging as its risk factor. This cross-sectional study investigated the association between pesticide exposure and the risk of atherosclerosis in a rural population in Korea using carotid intima-media thickness (CIMT). This study used dataset from the baseline survey of the Korea Farmers Cohort Study between November 2005 and January 2008, and the final analysis included 477 participants. Well-structured questionnaires were used to estimate pesticide exposure. CIMT ≥ 0.9 mm was established for carotid atherosclerosis. Multiple logistic regression analyses were undertaken to evaluate the association between pesticide exposure and atherosclerosis, adjusting demographic and health-related confounders. Even after adjustments, the increased risk of atherosclerosis was significantly associated with pesticide exposure, such as a lifetime history of farming (odds ratio [OR] 3.25 95% confidence interval [CI] 1.51–6.98), a history of using pesticide (OR 3.42 95% CI 1.63–7.16), using pesticide 10 times or more annually (OR 2.55 95% CI 1.21–5.39), and higher cumulative exposure index level (OR 3.63 95% CI 1.65–7.97). Further prospective studies are required to elucidate effects of pesticide exposure on the risk of atherosclerosis.
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer