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Night noise guidelines for Europe - WHO/Europe - World Health ...

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EFFECTS ON HEALTH<br />

93<br />

Current evidence does seem to suggest that environmental <strong>noise</strong> exposure, especially at<br />

higher levels, is related to mental health symptoms and possibly raised anxiety and<br />

consumption of sedative medication, but there is little evidence that it has more serious<br />

effects. Further research is needed on mental health effects at very high <strong>noise</strong> levels.<br />

Existing studies may be confounded either by prior selection of subjects out of (or<br />

into) noisy areas as a result of <strong>noise</strong> exposure, or by confounding between <strong>noise</strong> exposure,<br />

socioeconomic deprivation, and psychiatric disorder. It is also possible that people<br />

underestimate or minimize the effects of <strong>noise</strong> on health through optimism bias<br />

(Hatfield and Soames Job, 2001) and that this is particularly protective <strong>for</strong> mental<br />

health.<br />

The evidence is not strong <strong>for</strong> the association between <strong>noise</strong> exposure and mental ill<br />

health. What evidence there is suggests that <strong>noise</strong> exposure may be responsible <strong>for</strong> psychological<br />

symptoms above 70 dB(A) L eq . Almost all studies have only examined the<br />

effects of daytime <strong>noise</strong> on mental health, but it is possible that night-time <strong>noise</strong>, during<br />

sleep time, may have effects on mental health at lower levels than daytime <strong>noise</strong>.<br />

The most powerful evidence of <strong>noise</strong> on mental health comes from studies of military<br />

aircraft <strong>noise</strong>. There is also some evidence that intense road traffic <strong>noise</strong> may lead to<br />

psychological symptoms. There is no evidence of any effects of railway <strong>noise</strong> on mental<br />

health.<br />

4.9 THE SEVERITY OF SELF-REPORTED SLEEP<br />

DISTURBANCE<br />

4.9.1 INTRODUCTION<br />

In section 2.1.2 of Chapter 2 of this report, it is stated that sleep disturbance caused<br />

by <strong>noise</strong> may either be diagnosed (Environmental Sleep Disorder: ICSD 780-52-6) or<br />

self-reported. Although self-reported sleep disturbance is subjective by definition, its<br />

observed occurrence correlates with <strong>noise</strong> levels as well as with important diagnostic<br />

criteria <strong>for</strong> ICSD 780-52-6. It appears justified to consider self-reported sleep disturbance<br />

as an impairment of health, especially if indicated by representative population<br />

samples in social surveys. Furthermore, section 4.1 of Chapter 4 of this report gives a<br />

quantitative relationship between <strong>noise</strong> level L night and the percentage of population<br />

that reports a disturbed sleep of high, medium or low disturbance intensity.<br />

But an open question concerns severity: even if night-time <strong>noise</strong> causes large percentages<br />

of the population to declare themselves as highly sleep-disturbed, this could nevertheless<br />

represent an almost negligible loss of health, if the mean severity of self-reported<br />

sleep disturbance were negligible in comparison with commonly accepted diseases.<br />

Attempts have been made to give an answer to this important question, using <strong>WHO</strong>’s<br />

concept of disability weights (Murray et al., 1996) as a basis <strong>for</strong> severity comparisons.<br />

4.9.2 AN ASSESSMENT OF DISABILITY WEIGHTS<br />

A Swiss study (Müller-Wenk, 2002) aimed at determining a disability weight <strong>for</strong><br />

sleep disturbance due to road traffic <strong>noise</strong>. For this purpose, a description of road-<br />

NIGHT NOISE GUIDELINES FOR EUROPE

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