Sleep disturbance (noise related): Difference between revisions
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'''Scope''' | '''Scope''' | ||
'''Sleep disturbance''' describes the way people are sleep disturbed by noise | '''Sleep disturbance''' describes the way people are sleep disturbed by noise from the Schiphol airport, the Netherlands. | ||
[[Category:Health effects]] | |||
[[Category:Impacts]] | |||
[[category:Kuopio workshop]] | |||
== Description == | == Description == | ||
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Percentage of people sleep disturbed to some degree (mildly, moderately, severily). | Percentage of people sleep disturbed to some degree (mildly, moderately, severily). | ||
Revision as of 21:52, 14 March 2007
Scope
Sleep disturbance describes the way people are sleep disturbed by noise from the Schiphol airport, the Netherlands.
Description
Sleep disturbance relates to the number of people being sleep disturbed to some degree by being exposed to noise. Several effects of noise on sleep, varying in severity (and evidence burden), have been measured:
- primary effects like difficulties falling asleep, awakenings, sleep stage changes and instantaneous arousal effects during the sleep (temporary increase in blood pressure,
heart rate, vasoconstriction, release of stress hormones in the blood, increased motility);
- secondary or ‘after effects’ measured the next day: decrease of perceived sleep quality, increased fatigue and decrease in mood and performance;
- long-term effects on well being: increased medication use, or chronic annoyance.
References
Van Kempen et al (2005), Selection and evaluation of exposure-effectrelationships for health impact assessment in the field of noise and health [1].
Definition
Necessary input: Number of people exposed to different dB levels from a certain source (eg road transport, air traffic, rail, etc) at night time, expressed in Lnight.
Necessary model: A model that estimates the number of people being sleep disturbed (mildly, moderately, or severely) by a certain noise source.
Example model: Relations derived by Miedema et al (ref). See under Formula.
Necessary input: A questionnaire assessing the level of noise annoyance in the exposed population. Questions in surveys differ. In order to obtain comparable disturbance measures the scales are translated into a scale from 0 to 100. Cut-off points to assess the percentage of highly sleep disturbed persons are used, [variable: Annoyance | analogue to the definitions of percentage (highly) annoyed persons].
(Further references not provided here now)
Not covered here
Causality
List of parents:
List of daughters:
Data
None, should be based on noise exposure data
Formula
Miedema aircraft sleep disturbance relationships:
Valid for Lden between 45-75 dB(A)
- % Mildly sleep disturbed = 4.465 – 0.411 * Lnight + 0.01395 * Lnight 2
- % Moderately sleep disturbed = 13.714 – 0.807 * Lnight + 0.01555 * Lnight 2
- % Severily sleep disturbed = 18.147 – 0.956 * Lnight + 0.01482 * Lnight 2
Unit
Noise: Lnight - The equivalent sound level over night-time (23.00 pm – 07.00 am).
Sleep disturbance: Percentage of people sleep disturbed to some degree
Result
Percentage of people sleep disturbed to some degree (mildly, moderately, severily).