Noise sensitivity and future risk of illness and mortality
Introduction
Recently there have been several studies linking prolonged aircraft noise exposure to increased risk of cardiovascular and stroke mortality (Huss et al., 2010, Hansell et al., 2013). These studies are part of accumulating evidence that both aircraft noise exposure and road traffic noise exposure are related to an increased risk of cardiovascular disease and mortality (Sorensen et al., 2011, Sorensen et al., 2012, Floud et al., 2013). The putative mechanism behind these associations is thought to relate to the stress hypothesis where prolonged noise exposure leads to increased stress responses, hypertension and increased risk of cardiovascular disease (Babisch, 2008, Jarup et al., 2008, Munzel et al., 2014).
The most frequent response to environmental noise is annoyance, which is a mixture of reported discomfort, anger and feelings of intrusion. Exposure response relationships have been found for road, rail and aircraft noise in which the degree of annoyance rises with increasing noise levels (Miedema and Vos, 1998). Annoyance has also been suggested as a possible moderating factor of the effects of noise on cardiovascular disease — as a subjective indicator of the degree of disturbance from noise that amplifies the stress response to sound (Babisch et al., 2013). However, noise annoyance levels are probably inadequate as a proxy for noise levels in associations with health outcomes. This is because there are non-acoustic factors, that may account for at least 35% of the variance in annoyance such as personality factors, attitudes to the noise source and perceptions of malfeasance related to the source of the noise (Job, 1988). Despite this, noise annoyance is associated with health outcomes, especially psychiatric disorder. In cross sectional studies it has been suggested that prior ill-health may lead to increased levels of annoyance and not the other way round (Tarnopolsky et al., 1980, Stansfeld et al., 1993). This has been explained as people who feel unwell being likely to be less tolerant of environmental discomfort.
Noise sensitivity, as a stable response to noise in general, is an independent predictor of the annoyance response to environmental noise (Job, 1999, Paunović et al., 2009, van Kamp et al., 2004). It has been postulated that noise sensitivity might be an indicator of vulnerability to environmental stressors, so that highly sensitive people might be more prone to develop illness when exposed to environmental noise (Stansfeld, 1992).
It is of interest to understand whether noise sensitivity does indicate vulnerability to ill-health, especially that attributable to noise, as this has implications for public health policy on reducing noise and advising noise sensitive individuals of the potential consequences of noise exposure. This is best attempted in longitudinal analyses. A single question on annoyance to noise in general was included in the first phase of the Whitehall II Study of British civil servants. We examined whether this question, which is an indicator of noise sensitivity (Job, 1999), is a predictor of future cardiovascular morbidity and mortality and psychiatric disorder. We hypothesised that with increased levels of noise sensitivity there would be a greater risk of both cardiovascular disease and psychiatric morbidity adjusting for ill-health at baseline.
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Participants
The Whitehall II study was established between 1985 and 1988 with a target population of all male and female civil servants, aged between 35 and 55 years, in twenty London based civil service departments. 10,308 civil servants were examined in phase 1 of the study — 6895 men and 3413 women with a response rate of 73%, the true response rate was higher because around 4% of the invited employees had moved before the study and were not eligible for inclusion. The noise sensitivity question was only
Results
There were 3630 individuals in the sample, 49% were men. Overall, 48% of participants were sensitive, being highly bothered by noise in general. Noise sensitivity or being highly bothered by noise was more common in the 50–55 year age group (OR = 1.20 (95% CI 1.01–1.43)) relative to the 34–39 year age group. Women tend to be more sensitive relative to men (OR = 1.21 (95% CI 1.06–1.39)). Those in the lowest employment grade tend to be less sensitive than those in the highest employment grade (OR = 0.63
Discussion
Being highly sensitive to noise in general was more common in 50–55 year olds, women, and those of high employment grade, similar to findings in a national UK survey (Clark et al., 2014). As has been found previously in the literature, there were cross-sectional associations between high noise sensitivity and self-rated health and psychological distress (Tarnopolsky et al., 1980, Stansfeld et al., 1993). Being highly sensitive did not predict angina pectoris, non-fatal myocardial
Conclusions
Future research should be pursued in several directions. First, there is a need for a replication of these findings in a cohort study with noise exposure measures as well as noise sensitivity. In particular the associations between noise sensitivity and cardiovascular outcomes should be explored further in people of less advantaged social position. Less advantaged social position may be a marker for exposure to environmental stressors including noise exposure. If there is an association with
Acknowledgements
We thank all participating Civil Service departments and their welfare, personnel, and establishment officers; the Occupational Health and Safety Agency; the Council of Civil Service Unions; all participating civil servants in the Whitehall II study; all members of the Whitehall II study team. The first two phases of the Whitehall II study were supported by grants from the Medical Research Council; British Heart Foundation; Health and Safety Executive; Department of Health; National Heart Lung
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