Night noise guidelines for Europe - WHO/Europe - World Health ...
Night noise guidelines for Europe - WHO/Europe - World Health ...
Night noise guidelines for Europe - WHO/Europe - World Health ...
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EFFECTS ON HEALTH<br />
67<br />
and cohort studies on the association between <strong>noise</strong> level and incidence of IHD. In<br />
cross-sectional studies, IHD prevalence was assessed by clinical symptoms of angina<br />
pectoris, myocardial infarction, ECG abnormalities as defined by <strong>WHO</strong> criteria<br />
(Rose and Blackburn, 1968), or from self-reported questionnaires regarding<br />
doctor-diagnosed heart attack. In longitudinal studies, IHD incidence was assessed<br />
by clinical myocardial infarction as obtained from hospital records, ECG measurements<br />
or clinical interviews. The majority of studies refer to road traffic <strong>noise</strong>.<br />
With regard to IHD, the evidence of an association between community <strong>noise</strong> and<br />
IHD risk has increased since a previous review (Babisch, 2000). There is not much<br />
indication of a higher IHD risk <strong>for</strong> subjects who live in areas with a daytime average<br />
sound pressure level of less than 60 dB(A) across the studies. For higher <strong>noise</strong><br />
categories, a higher IHD risk was relatively consistently found amongst the studies.<br />
Statistical significance was rarely achieved. Some studies permit reflections on<br />
dose–response relationships. These mostly prospective studies suggest an increase<br />
in IHD risk at <strong>noise</strong> levels above 65–70 dB(A), the relative risks ranging from 1.1<br />
to 1.5 when the higher exposure categories were grouped together. Noise effects<br />
were larger when mediating factors like residence time, room orientation and window-opening<br />
habits were considered in the analyses. This accounts <strong>for</strong> an induction<br />
period (Rose, 2005) and improves exposure assessment. The results appear as<br />
consistent when subjective responses of disturbance and annoyance are considered,<br />
showing relative risks ranging from 0.8 to 2.7 in highly<br />
annoyed/disturbed/affected subjects. However, these findings may be of lower<br />
validity due to methodological issues.<br />
4.5.8 MEDICATION AND DRUG CONSUMPTION<br />
Table A8 of the major report (Babisch, 2006) gives the results of studies on the<br />
relationship between drug consumption and community <strong>noise</strong>. Medication was<br />
primarily investigated with respect to aircraft <strong>noise</strong>. A significant prevalence ratio<br />
<strong>for</strong> medication with cardiovascular drugs of 1.4 was found in the sample of<br />
Amsterdam Schiphol Airport (Knipschild, 1977a). The results of the “drug survey”,<br />
where the annual data of the pharmacies regarding the purchase of cardiovascular<br />
drugs were analysed (repeated cross-sectional survey), supported this<br />
finding. An increase in drug purchase over time in the exposed areas and not in<br />
the less exposed was found. This refers to the purchase of cardiovascular and<br />
antihypertensive drugs, as well as the purchase of hypnotics, sedatives and<br />
antacids (Knipschild and Oudshoorn, 1977). Furthermore a dependency with<br />
changes in night flight regulations was found (decrease after reduction of night<br />
flights). A large recent study around Amsterdam Schiphol Airport found only a<br />
slightly higher risk of self-reported medication with cardiovascular drugs, including<br />
antihypertensive drugs (relative risk 1.2), in subjects exposed to aircraft <strong>noise</strong><br />
where the <strong>noise</strong> level L den exceeded 50 dB(A) (Franssen et al., 2004).<br />
Dose–response relationships across <strong>noise</strong> levels (L den =