Difference between revisions of "Noise exposure around the Schiphol airport"

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m (moved Noise exposure to Noise exposure around the Schiphol airport: Old title was too broad.)
 
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If you need help about filling in a variable open the link at the end of this paragraph in a new window. Otherwise, just delete this paragraph and start writing. [[Heande:Help:Variable]]
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{{Release||. Should the Schiphol case be released as a whole, although nobody is actually improving the pages?}}
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'''Scope'''<br>
 
'''Scope'''<br>
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'''Noise exposure''' gives the number of people exposed to different levels of noise in the vicinity of Schiphol airport
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'''Noise exposure''' gives the number of people exposed to different levels of noise in the vicinity of Schiphol airport in the Netherlands
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[[Category:Exposures]]
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[[category:Kuopio workshop]]
  
 
== Description ==
 
== Description ==
  
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In Lu & Morrell (2006) the level of noise is measured in Kosten unit (KU). 10 KU was used as the background level. Number of residences  within the noise contour 20-10 KU is missing from their data (unavailable).
 
  
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The Lden value is approximately equal to (0.5*Kosten unit+41) (Dassen et al. (2000) in Franssen et al. (2004))
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Noise is one of the most important environmental effects of aviation activities, the largest impact of which is realised in the community surrounding the airport (Lu & Morrell 2006). Factors affecting noise exposure and impact include the characteristics of the settlement in the vicinity of the airport, and the quality and quantity of airtraffic (aircraft and engine types, time of day, flight paths, landing and take-off procedures) and related activities.  
  
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Visser et al (2005) published a noise map (although this is probably not the original place of publication).
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Noise disturbance is difficult to evaluate as it is open to subjective reactions. Its impact is not a lasting one on the actual environment, but it can have significant adverse effects on people living close to an airport, including: interference with communication, sleep disturbance, annoyance responses, learning acquisition, performance effects and cardiovascular and psycho-physiological effects. [http://www.eurocontrol.int/environment/public/standard_page/noise.html]
  
  
 
=== References ===
 
=== References ===
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* Schiphol Group (2002). Gebruiksplan Schiphol 2001. The Netherlands. In:Lu, C. & Morrell, P. (2006). Determination and applications of environmental costs at different sized airports - aircraft noise and engine emissions
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* Lu, C. & Morrell, P. (2006). Determination and applications of environmental costs at different sized airports - aircraft noise and engine emissions. Transportation 33:45-61.
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*Otto Visser, Joop H van Wijnen and Flora E van Leeuwen: Incidence of cancer in the area around Amsterdam Airport Schiphol in 1988–2003: a population-based ecological study. BMC Public Health 2005, 5:127 doi:10.1186/1471-2458-5-127
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*ANOTEC Consulting, S.L. Study on Current and Future Aircraft Noise Exposure at and around Community Airports - Final Report – http://ec.europa.eu/transport/air_portal/environment/studies/doc/aircraft_noise.pdf
  
 
== Definition ==
 
== Definition ==
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=== Data ===
 
=== Data ===
  
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'''Schiphol Group (2002):'''
 
  
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Kosten unit (KU): number of residences
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'''Residences within noise contour at Schiphol (Lu & Morrell 2006)'''
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Kosten unit (Ke): number of residences
 
*>65: 14
 
*>65: 14
 
*60-65: 33
 
*60-65: 33
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*20-25: 55634
 
*20-25: 55634
  
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[[image:Noise exposure Schiphol.JPG]]
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Lden value is approximately equal to (0.5*Kosten unit+41)
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Lnight can be calculated as Lden+10
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The average number of people living in a house for several years is 2,26 in 2006 (Dutch National
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Statistics).
  
 
=== Formula ===
 
=== Formula ===
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== Result ==
 
== Result ==
  
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{{category:Kuopio workshop}}
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{|{{prettytable}}
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! Ke
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! Lden
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! Lnight
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! Inhabitants
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|-----
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| >65
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| >73.5
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| >83.5
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| 32
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|-----
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| 60-65
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| 71-73.5
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| 81-83.5
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| 75
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|-----
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| 55-60
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| 68.5-71
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| 78.5-81
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| 158
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|-----
 +
| 50-55
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| 66-68.5
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| 76-78.5
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| 909
 +
|-----
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| 45-50
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| 63.5-66
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| 73.5-76
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| 3786
 +
|-----
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| 40-45
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| 61-63.5
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| 71-73.5
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| 7589
 +
|-----
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| 35-40
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| 58.5-61
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| 68.5-71
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| 8717
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|-----
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| 30-35
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| 56-58.5
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| 66-68.5
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| 30598
 +
|-----
 +
| 25-30
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| 53.5-56
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| 63.5-66
 +
| 99548
 +
|-----
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| 20-25
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| 51-53.5
 +
| 61-63.5
 +
| 125733
 +
|-----
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|}
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[[category:Intarese]]

Latest revision as of 16:49, 16 May 2011

Template:Release Scope
Noise exposure gives the number of people exposed to different levels of noise in the vicinity of Schiphol airport in the Netherlands

Description

Noise is one of the most important environmental effects of aviation activities, the largest impact of which is realised in the community surrounding the airport (Lu & Morrell 2006). Factors affecting noise exposure and impact include the characteristics of the settlement in the vicinity of the airport, and the quality and quantity of airtraffic (aircraft and engine types, time of day, flight paths, landing and take-off procedures) and related activities.

Noise disturbance is difficult to evaluate as it is open to subjective reactions. Its impact is not a lasting one on the actual environment, but it can have significant adverse effects on people living close to an airport, including: interference with communication, sleep disturbance, annoyance responses, learning acquisition, performance effects and cardiovascular and psycho-physiological effects. [1]


References

Definition

Causality

List of parents:

Data

Residences within noise contour at Schiphol (Lu & Morrell 2006)

Kosten unit (Ke): number of residences

  • >65: 14
  • 60-65: 33
  • 55-60: 70
  • 50-55: 402
  • 45-50: 1675
  • 35-40: 3358
  • 35-40: 3857
  • 30-35: 13539
  • 25-30: 44048
  • 20-25: 55634

Lden value is approximately equal to (0.5*Kosten unit+41)

Lnight can be calculated as Lden+10


The average number of people living in a house for several years is 2,26 in 2006 (Dutch National Statistics).

Formula

Analytica_id:

<anacode></anacode>

Unit

Result

Ke Lden Lnight Inhabitants
>65 >73.5 >83.5 32
60-65 71-73.5 81-83.5 75
55-60 68.5-71 78.5-81 158
50-55 66-68.5 76-78.5 909
45-50 63.5-66 73.5-76 3786
40-45 61-63.5 71-73.5 7589
35-40 58.5-61 68.5-71 8717
30-35 56-58.5 66-68.5 30598
25-30 53.5-56 63.5-66 99548
20-25 51-53.5 61-63.5 125733
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