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Potential health risks of exposure to noise from personal music ...

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Health <strong>risks</strong> <strong>from</strong> <strong>exposure</strong> <strong>to</strong> <strong>noise</strong> <strong>from</strong> <strong>personal</strong> <strong>music</strong> playersby <strong>exposure</strong> <strong>to</strong> aircraft and road-traffic <strong>noise</strong> and speech <strong>noise</strong> at 66 dB(A) L equ during 15min <strong>exposure</strong> time while reading a text and tested for memory <strong>of</strong> the text an hour lateror a week later. For aircraft <strong>noise</strong> there was impaired memory also <strong>from</strong> 15 min <strong>exposure</strong><strong>to</strong> 55 dB(A) L equ .For chronic aircraft <strong>noise</strong> <strong>exposure</strong> the Munich study (Hygge et al. 2002) and the RANCHstudy (Stansfeld et al. 2005) indicated that children exposed <strong>to</strong> chronic aircraft <strong>noise</strong>showed cognitive deficits compared <strong>to</strong> children not having been exposed <strong>to</strong> chronicaircraft <strong>noise</strong>. It was also found that the children at the old airport in Munich, who got rid<strong>of</strong> aircraft <strong>noise</strong>, improved their cognitive performance. Thus, there was somereversibility in the negative effects <strong>of</strong> <strong>noise</strong> on cognition when the <strong>noise</strong> ceased. To whatextent this recovery is dependent upon the age <strong>of</strong> the children in question (11-12 years)and the accompanying continuing growth in cognitive development, we do not know.Thus, short time <strong>exposure</strong> (15 min) <strong>to</strong> <strong>noise</strong> with average levels <strong>of</strong> 65 dB(A), impairsmemory and learning. Long-time chronic <strong>exposure</strong> <strong>to</strong>, at least aircraft <strong>noise</strong>, indicate thatthere will be statistically significant impairments <strong>of</strong> memory and language skills when the<strong>noise</strong> levels increase <strong>from</strong> around or below 55 <strong>to</strong> above 60 dB(A) L equ .3.9.1.2. Attention and distractionUse <strong>of</strong> <strong>music</strong> is sometimes employed <strong>to</strong> distract <strong>from</strong> a noisy working environment, andsometimes this is beneficial. One reason for this <strong>to</strong> happen is that the more boring,repetitive and simple a task is, the more will it benefit, both in quality and quantity, <strong>from</strong>being performed in <strong>noise</strong> (Kryter 1994). On the other hand, the more complex anddifficult the task is, the more it is prone <strong>to</strong> be hampered by excessive sounds.When the <strong>noise</strong> is preferred <strong>music</strong> <strong>from</strong> PMP one would in addition expect more <strong>of</strong> aperceived comfort. Further, when the <strong>music</strong> <strong>from</strong> the PMP also masks distracting soundsin the environment, devoid <strong>of</strong> relevant information or warning characteristics, it will mostlikely be a subjective advantage <strong>to</strong> listen <strong>to</strong> the PMP rather than <strong>to</strong> shut it <strong>of</strong>f. On theother hand, the more cognitively demanding the task is, the more it is dependent uponspeech communication, and the more there are <strong>of</strong> potential warning sounds in the closeenvironment, the more <strong>to</strong> the disadvantage <strong>of</strong> the task performance and the security <strong>of</strong>the listener the PMP-listening is.With regard <strong>to</strong> attention, there is always a risk that the sound <strong>of</strong> the <strong>music</strong> listened t<strong>of</strong>rom the PMP will acoustically mask warning sounds e.g. <strong>from</strong> approaching cars, streetcrossings or reversing trucks. Even if the <strong>music</strong> is not in a physical sense masking thewarning sound, the focused attention on the <strong>music</strong> will <strong>from</strong> time <strong>to</strong> time make thelistener inattentive <strong>to</strong> other sounds, some <strong>of</strong> which my be warning sounds.3.9.1.3. School performanceThere are a several cross-sectional studies that have reported a covariation between high<strong>noise</strong> levels (<strong>from</strong> aircraft or road traffic) and low grades or low levels <strong>of</strong> schoolachievement (Cohen et al. 1981, Cohen et al. 1986, Green et al. 1982, Evans andMaxwell 1997, Haines et al. 2001a, Haines et al. 2001b, Haines et al. 2001c, Haines etal. 2002, Maser et al. 1978, Stansfeld et al. 2005). However, cross-sectional studiessuffer <strong>from</strong> two possible short-comings. The first is the differential socio-demographiccomposition <strong>of</strong> the <strong>noise</strong> dose groups, which may favour children in quiet middle-classhousing and living areas. Adjusting statistically for the social class effects may not besufficient <strong>to</strong> control for this. The second is the possible confound between being exposed<strong>to</strong> <strong>noise</strong> both while learning and when tested for what is learnt. Noise at testing maylower the test scores without learning being effected, but the effects <strong>of</strong> <strong>noise</strong> on learningand performing can not be disentangled. Thus, cross-sectional studies are not the bestplatform for a strong inference on cause-effect relationships.56

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