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      Saliva cortisol in relation to aircraft noise exposure: pooled-analysis results from seven European countries

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          Abstract

          Background

          Many studies have demonstrated adverse effects of exposure to aircraft noise on health. Possible biological pathways for these effects include hormonal disturbances. Few studies deal with aircraft noise effects on saliva cortisol in adults, and results are inconsistent.

          Objective

          We aimed to assess the effects of aircraft noise exposure on saliva cortisol levels and its variation in people living near airports.

          Methods

          This study focused on the 1300 residents included in the HYENA and DEBATS cross-sectional studies, with complete information on cortisol sampling. All the participants followed a similar procedure aiming to collect both a morning and an evening saliva cortisol samples. Socioeconomic and lifestyle information were obtained during a face-to-face interview. Outdoor aircraft noise exposure was estimated for each participant’s home address. Associations between aircraft noise exposure and cortisol outcomes were investigated a priori for male and female separately, using linear regression models adjusted for relevant confounders. Different approaches were used to characterize cortisol levels, such as morning and evening cortisol concentrations and the absolute and relative variations between morning and evening levels.

          Results

          Statistically significant increases of evening cortisol levels were shown in women with a 10-dB(A) increase in aircraft noise exposure in terms of LA eq, 16h (exp(β) = 1.08; CI95% = 1.00–1.16), L den (exp(β) = 1.09; CI95% = 1.01–1.18), L night (exp(β) = 1.11; CI95% = 1.02–1.20). A statistically significant association was also found in women between a 10-dB(A) increase in terms of L night and the absolute variation per hour (exp(β) = 0.90; CI95% = 0.80–1.00). Statistically significant decreases in relative variation per hour were also evidenced in women, with stronger effects with the L night (exp(β) = 0.89; CI95% = 0.83–0.96) than with other noise indicators. The morning cortisol levels were unchanged whatever noise exposure indicator considered. There was no statistically significant association between aircraft noise exposure and cortisol outcomes in men.

          Conclusions

          The results of the present study show statistically significant associations between aircraft noise exposure and evening cortisol levels and related flattening in the (absolute and relative) variations per hour in women. Further biological research is needed to deepen knowledge of the pathway between noise exposure and disturbed hormonal regulation, and specially the difference in effects between genders.

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          Most cited references46

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          Protective and Damaging Effects of Mediators of Stress: Elaborating and Testing the Concepts of Allostasis and Allostatic Load

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            Why do we respond so differently? Reviewing determinants of human salivary cortisol responses to challenge.

            Stress and stress-related health impairments are major problems in human life and elucidating the biological pathways linking stress and disease is of substantial importance. However, the identification of mechanisms underlying a dysregulation of major components of the stress response system is, particularly in humans, a very challenging task. Salivary cortisol responses to diverse acute challenge paradigms show large intra- and interindividual variability. In order to uncover mechanisms mediating stress-related disorders and to potentially develop new therapeutic strategies, an extensive phenotyping of HPA axis stress responses is essential. Such a research agenda depends on substantial knowledge of moderating and intervening variables that affect cortisol responses to different stressors and stimuli. The aim of this report is, therefore, to provide a comprehensive summary of important determinants of, in particular, human salivary cortisol responses to different kinds of laboratory stimuli including acute psychosocial stress as well as pharmacological provocation procedures. This overview demonstrates the role of age and gender, endogenous and exogenous sex steroid levels, pregnancy, lactation and breast-feeding, smoking, coffee and alcohol consumption as well as dietary energy supply in salivary cortisol responses to acute stress. Furthermore, it briefly summarizes current knowledge of the role of genetic factors and methodological issues in terms of habituation to repeated psychosocial stress exposures and time of testing as well as psychological factors, that have been shown to be associated with salivary cortisol responses like early life experiences, social factors, psychological interventions, personality as well as acute subjective-psychological stress responses and finally states of chronic stress and psychopathology.
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              Aircraft and road traffic noise and children's cognition and health: a cross-national study.

              Exposure to environmental stressors can impair children's health and their cognitive development. The effects of air pollution, lead, and chemicals have been studied, but there has been less emphasis on the effects of noise. Our aim, therefore, was to assess the effect of exposure to aircraft and road traffic noise on cognitive performance and health in children. We did a cross-national, cross-sectional study in which we assessed 2844 of 3207 children aged 9-10 years who were attending 89 schools of 77 approached in the Netherlands, 27 in Spain, and 30 in the UK located in local authority areas around three major airports. We selected children by extent of exposure to external aircraft and road traffic noise at school as predicted from noise contour maps, modelling, and on-site measurements, and matched schools within countries for socioeconomic status. We measured cognitive and health outcomes with standardised tests and questionnaires administered in the classroom. We also used a questionnaire to obtain information from parents about socioeconomic status, their education, and ethnic origin. We identified linear exposure-effect associations between exposure to chronic aircraft noise and impairment of reading comprehension (p=0.0097) and recognition memory (p=0.0141), and a non-linear association with annoyance (p<0.0001) maintained after adjustment for mother's education, socioeconomic status, longstanding illness, and extent of classroom insulation against noise. Exposure to road traffic noise was linearly associated with increases in episodic memory (conceptual recall: p=0.0066; information recall: p=0.0489), but also with annoyance (p=0.0047). Neither aircraft noise nor traffic noise affected sustained attention, self-reported health, or overall mental health. Our findings indicate that a chronic environmental stressor-aircraft noise-could impair cognitive development in children, specifically reading comprehension. Schools exposed to high levels of aircraft noise are not healthy educational environments.
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                Author and article information

                Contributors
                0033 4 72 14 25 30 , clemence.baudin@ifsttar.fr
                Journal
                Environ Health
                Environ Health
                Environmental Health
                BioMed Central (London )
                1476-069X
                27 November 2019
                27 November 2019
                2019
                : 18
                : 102
                Affiliations
                [1 ]Univ Lyon, Université Claude Bernard Lyon1, ifsttar, umrestte, umr t_9405, Cité des Mobilités, 25 avenue François Mitterrand, F-69675 Bron, France
                [2 ]Now at: Technical Agency for Information on Hospital Care, Lyon, France
                [3 ]ISNI 0000 0004 1937 0626, GRID grid.4714.6, Institute of Environmental Medicine, Karolinska Institute, ; Stockholm, Sweden
                [4 ]ISNI 0000 0004 0554 9748, GRID grid.425100.2, Federal Environment Agency, ; Berlin, Germany
                [5 ]Environmental Health Unit, Agency for Health Protection, Pavia, Italy
                [6 ]ISNI 0000 0001 2163 3825, GRID grid.413852.9, Hospices Civils de Lyon GH Sud CBAPS Laboratoire de Biochimie, ; Pierre Bénite, France
                [7 ]Currently retired, Bron, France
                [8 ]ISNI 0000 0001 2322 8188, GRID grid.249503.9, IFSTTAR, Planning, Mobilities and Environment Department, Dynamics of Mobility Changes Team, ; Bron, France
                [9 ]ISNI 0000 0001 2155 0800, GRID grid.5216.0, Department of Hygiene, , Epidemiology and Medical Statistics Faculty of Medicine, National and Kapodistrian, University of Athens, ; Athens, Greece
                [10 ]ISNI 0000 0001 2208 0118, GRID grid.31147.30, National Institute of Public Health and Environmental Protection, ; Bilthoven, the Netherlands
                [11 ]ISNI 0000 0001 2322 8188, GRID grid.249503.9, IFSTTAR, Transport, Health and Safety Department, ; Bron, France
                [12 ]ISNI 0000 0004 1937 0626, GRID grid.4714.6, Institute of Environmental Medicine, Karolinska Institute, ; Stockholm, Sweden
                [13 ]ISNI 0000 0004 1936 9377, GRID grid.10548.38, Stress Research Institute, Faculty of Social Sciences, Stockholm University, ; Stockholm, Sweden
                [14 ]ISNI 0000 0001 2155 0800, GRID grid.5216.0, Nurses School, National and Kapodistrian, University of Athens, ; Athens, Greece
                [15 ]ISNI 0000 0004 1936 8411, GRID grid.9918.9, Centre for Environmental Health and Sustainability, University of Leicester, ; Leicester, UK
                Author information
                http://orcid.org/0000-0002-2240-1548
                Article
                540
                10.1186/s12940-019-0540-0
                6882169
                31775752
                a169f133-48dc-4e29-923c-d83ea195be4d
                © The Author(s). 2019

                Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License ( http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The Creative Commons Public Domain Dedication waiver ( http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.

                History
                : 9 May 2019
                : 28 October 2019
                Categories
                Research
                Custom metadata
                © The Author(s) 2019

                Public health
                epidemiology,aircraft noise exposure,saliva cortisol
                Public health
                epidemiology, aircraft noise exposure, saliva cortisol

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