Acoust. Sci. & Tech. 33, 1 (2012)
#2012 The Acoustical Society of Japan
PAPER
Relationship between civil aircraft noise
and community annoyance near Dubai International Airport
Hussein M. Elmehdi
Applied Physics Department, University of Sharjah,
PO Box: 27272 Sharjah, United Arab Emirates (UAE)
( Received 1 November 2010, Accepted for publication 27 June 2011 )
Abstract: According to Airport Council International (ACI) traffic statistics for 2002, Dubai
International Airport is the second fastest growing airport in the world. In 2007, it catered to more than
36 million passengers, with approximately 1,000 daily flight events, including takeoffs and landings.
In this paper, we report the first assessment of community annoyance caused by civil aircraft noise
exposure at nine sites around Dubai International Airport (United Arab Emirates). Our aim is to assess
the relationship between aircraft noise levels and annoyance responses in Dubai. To accomplish our
goal, we have adapted the WECPNL and Ldn as the aircraft noise indices in Dubai, and the percentage
of highly annoyed responses (%HA) has been used to assess the dose–response relationship of aircraft
noise. %HA was obtained using social surveys that were carried out at nine sites within close
proximity of the airport utilizing the ISO/TS 15666-2003 questionnaire. Subjects ranging between 20
and 65 years in age were randomly selected. Results show that 41% of the respondents said that they
are highly annoyed, a percentage considered high but in agreement with similar studies carried out
near major airports in other countries.
Keywords: Airport noise, Annoyance, Dose-response, Dubai
PACS number: 43.50.Qp, 43.50.Rq, 43.50.Lj [doi:10.1250/ast.33.6]
1.
INTRODUCTION
The number of air passengers is predicted to grow by
4.3% up to the year 2015 [1,2]. As a result the number of
flights will continue to increase, especially in developing
areas such as the city of Dubai, United Arab Emirates
(UAE), whose airport is considered as the second fastest
growing airport in the world. The airport handles close to
1,000 daily events, including takeoffs and landings [3,4],
which are distributed throughout the day and night (see
Table 1), with approximately the same number of landings
and takeoffs. Such a high volume of events consequently
leads to an increase in noise pollution in the vicinity of the
airport. This has raised concerns about the adverse health
effects on people living areas close to the airport. Several
organizations, such as the World Health Organization
(WHO), [5] have reported that exposure to high noise
levels leads to induced hearing impairment; interference
with speech communication and performance; sleep disturbance; and cardiovascular and physiological effects. The
latest of these studies is one on hypertension and exposure
e-mail: hmelmehdi@sharjah.ac.ae
6
to noise near airports (HYENA), in which the relationship
between exposure to noise generated by aircraft and road
traffic near airports and the risk of hypertension was
assessed [6]. The study revealed statistically significant
effects of to aircraft noise on blood pressure.
The number of individuals exposed to aircraft noise is
difficult to estimate, but it is safe to say that a large number
of houses are within the airport vicinity, where the noise
levels in these areas produce sound pressure levels (SPLs)
Ldn of 65 dB on the A scale or higher. These values are
higher than the value of 57 dB on the same scale, which is
considered to cause a high percentage of community
annoyance [7]. It should be noted that Ldn is the parameter
used as an indicator of the onset of what is referred to as
‘‘community annoyance’’ in early studies (e.g., Schultz, [8],
who showed a strong correlation between this figure and
annoyance. In Dubai, the airport is situated in the heart of
the city (see Fig. 1), with commercial as well as residential
bulidings in some areas within a few hundred meters of the
runway.
In this paper, we report the results of the first phase of
an extensive study aimed at studying the effect of aircraft
noise in the vicinity of Dubai International Airport. The
H. M. ELMEHDI: NOISE ANNOYANCE ASSESSMENT NEAR DUBAI AIRPORT
Table 1 Traffic at Dubai Internationaly .
y
Time of day
Average number of
flights
7:00–19:00
19:00–22:00
22:00–24:00
00:00–07:00
260
105
80
200
Taken from the arrival and departure tables from the Dubai
International Website over a 7-day period [4].
which is characterized by major discrimination against
very low frequency sounds, was used because it closely
simulates the perception of the human ear. For example,
a constant SPL of 57 dB indicates that the average noise
produced by the source over the measurement period,
which ranges from 1 to 24 h, is 57 dB. All SPL measurements reported in this paper were obtained using the A
scale. The meters were placed either on rooftops or in an
area clear of any obstacles. The meter was mounted on a
tripod 1.5 m above ground level and at least 3 m away from
any reflecting surfaces. Since the airport is quite busy
throughout the day and night, measurements were performed at different times during the day and night. To
confirm reproducibility, measurements were repeated at
least three different times during the week.
To analyze the community response to aircraft noise
around the airport, we used the weighted equivalent
continuous perceived noise level (WECPNL), which is
given by the following expression [13]:
WECPNL ¼ [dB(A)]ave þ 10 log10 ðNÞ 27;
Fig. 1 Aerial view of Dubai International Airport [9].
study was started in August 2007 and comprises two
phases. In the first phase, we use an integrated sound level
meter to measure the noise levels at nine sites near the
airport, with the goal of adding 13 more sites by the end of
2008. In the second phase, we assessed the annoyance level
by means of social and socio-acoustic surveys. The
questionnaire used in the survey is ISO/TS 15666-2003
(ISO Store Order #: 924549) [10]. The sites were chosen in
areas close to the airport with more emphasis on residential
neighborhoods.
2.
MATERIALS AND METHODS
2.1. Noise Measurement
As reported previously [11], noise levels were assessed
using a Nor140 precision portable sound level meter (made
by Norsonic, Norway). The meter is a device that responds
to sound, similar to the human ear, and provides reproducible measurements of sound levels. It consists of a
microphone and electronics fitted with three sound weightings A, B and C. The meter detects sounds and converts
them into electrical signals via electronic circuits, from
which the meter displays a digital reading for sound levels
in any of the three weighted scales [12]. The A-weighting,
ð1Þ
where [dB(A)]ave stands for the energy mean of all peak
levels of any day, and N ¼ N2 þ 3N3 þ 10ðN1 þ N4Þ,
where N1 is the total number of aircraft between 0:00 a.m.
and 7:00 a.m., N2 is the number of aircraft between
7:00 a.m. and 7:00 p.m., N3 is the number of aircraft
between 7:00 p.m. and 10:00 p.m., and N4 is the total of
aircraft between 10:00 p.m. and 12:00 p.m. In addition to
WECPNL, we also calculated the day-night average sound
level (Ldn ), which is given by [see, for example,
refs. 13,14]
15
9
100:1Lday þ
100:1ðLnight þ10Þ ; ð2Þ
Ldn ¼ 10 log
24
14
Ldn represents the average noise level over a 24-h period,
with a 10 dB ‘‘penalty’’ in the night time hours (10 p.m. to
7 a.m.) to account for the fact that people typically find
noise more disturbing at night while they are trying to
sleep. The Ldn descriptor is useful for measuring the impact
that road noise might have on establishments that may be
constantly occupied such as homes. Both WECPNL and
Ldn were used to assess the relationship between annoyance
and public response.
2.2. Social Survey
For each selected site, an average of 23 surveys were
collected from residents living 100–150 m from each site.
This comprised a return rate of 76%, since we have
distributed 30 surveys in each site, which covered almost
all of the occupied houses within the selected site. As will
be discussed further in the next section, the majority of the
respondents were males, which is typical in a conservative
Islamic and Arab culture, where most of the house hold
7
Acoust. Sci. & Tech. 33, 1 (2012)
affairs are handled by men. The questionnaire included
questions about the demographics, noise annoyance,
interference with daily activities, and psychological as
well as physiological health-related problems, and the
general reaction to aircraft noise. We used the scale
developed for the ISO/TS 15666-2003 questionnaire [8],
which employs a scale from 0 to 10, ranging from not
annoyed at all, slightly annoyed, moderately annoyed,
very annoyed to extremely annoyed. The questionnaire
was made available in Arabic and English and it was left
up to the randomly selected subjects to choose the
language.
It should be noted that the randomly chosen had
no prior knowledge of the questionnaire. Subjects must
have lived on their property for at least 12 months. The
interviews were carried out face-to-face, and for residents
who were not available, we came back to interview them
on a different day. The streets selected for this study are
located in the proximity of the airport: Al Twar, Mirdif, AlRashedya, Al-Muraqabat, and Qarhoud. Many subjects
raised questions about the purpose of the questionnaire and
it was made clear to everyone that it was a research study
that will be published but will have no impact on
improving or reducing the noise level. Subjects were
offered the Arabic translation of the survey to help them
understand the questions, but all collected surveys were
completed in English. It should be noted that the vast
majority of UAE residents speak English very well, as was
evident from the small number of people who required the
Arabic translation of the questionnaire. In addition, the
subjects interviewed were all residents of the UAE who
had lived near the airport for an extended period of time (at
least 12 months) and were very familiar with cultural and
social values of the UAE. The questionnaire was composed
of three parts: a general part, which documents the site
number, the date, and the noise level reading; part two,
which includes questions about the demographics for each
respondent; part three, which includes the following
question:
Thinking about the last 12 months or so, what best shows
how much you are bothered, disturbed, or annoyed by
aircraft noise?
8
Table 2 Responses to questionnaire.
13%
15%
31%
41%
Not at all
annoyed
slightly
annoyed/Moderately
annoyed
Very
annoyed
Extremely
annoyed
Fig. 2 %HA as a function of WECPNL. The middle line
is a polynomial fit to the data and the upper and lower
lines represent the 95% confidence limits. The solid
squares are our data, while the open squares are from
[16], and the open triangle from [25].
3.
RESULTS AND DISCUSSION
The respondents were demographically distributed as
follows: 27% female and 73% male. 43% ranged from
20 to 40 years of age, 42% were 40–60 years of age, and
the remaining 15% were above 60 years of age. 86% of
the interviewees were married with children, which is a
reasonable number considering the conservative Islamic
nature of the UAE. The results to the annoyance scale
question are summarized in Table 2.
WHO recommends the adoption of the percentage of
respondents who felt highly annoyed (%HA) as an indicator
of the health effects of noise (annoyance) and its adverse
health effects [5,15]. Europe and North America, as well as
Australia, also have adopted %HA as the annoyance
indicator [16–18]. Since there are no regulations in the
UAE, to our knowledge, that clearly indicate, which index
to use, we will adopt WECPNL as a physical descriptor of
aircraft noise. We will also use the Ldn indicator to compare
our results with the work of other researchers. In this study,
we have adopted the cutoff of 72% [8,19–23], which
includes very annoyed and highly annoyed.
Figure 2 shows %HA and the corresponding WECPNL
values, which were calculated using Eq. (1), along with
95% confidence limits for all sites. Each point in the figure
H. M. ELMEHDI: NOISE ANNOYANCE ASSESSMENT NEAR DUBAI AIRPORT
tion of the noise descriptors WECPNL and Ldn and their
relationship to community annoyance revealed that 41% of
respondents felt highly annoyed, 31% rather annoyed, 15%
slightly annoyed, and only 13% of the respondents felt not
annoyed by aircraft noise near the airport. To assess the
health impact of such percentages, we examined the
number of %HA respondents and the WECPNL value
at each site. It was found that there is a very strong
relationship between WECPNL and %HA, which agrees
with the conclusion of other researchers. Similar analysis
using Ldn showed a similar trend. We are currently taking
measurements at 13 more sites, and we plan to interview
more people to further support these results.
ACKNOWLEDGMENTS
Fig. 3 %HA as a function of Ldn .
represents the calculated WECPNL value at each site and
the corresponding number of %HA respondents at that site.
The figure clearly indicates a tendency for the percentage
of highly annoyed people to rise as the value of WECPNL
increased. This result was expected and in agreement with
the results obtained by other researchers (e.g., [14,17–20]).
Ldn , which was calculated using Eq. (2), is shown in
Fig. 3. It should be noted that Ldn includes background
noise levels, such as that arising from vehicular traffic
noise. To account for the background noise levels,
researchers recommend subtracting 13 dB from the
WECPNL values, i.e., Ldn ¼ WECPNL 13, [16,24].
After subtraction, the values of the calculated Ldn seem
to be lower than those obtained using Eq. (2), which may
be partly due to the fact that the background noise level
(transportation) is high, as reported previously [9]. This
means that the 13 dB offset may be different for the UAE.
The annoyance levels near Dubai International were found
to be high but comparable to the findings of similar studies
carried out near various airports around the world including
Korea [16], Sweden [17], Italy [24], USA [26], Taiwan
[27], Spain [28], Canada [29], India [30], and Chile [31].
4.
CONCLUSIONS
The general public in the UAE are increasingly aware
of environmental noise and its adverse health effects. In
addition, WHO has recognized annoyance as one of the
environmental health indicators that must be accounted for
before deciding on various community projects and
development plans. Guidelines for noise limits have been
drafted in order to protect the general public from exposure
to annoyance sources. Among these annoyance sources is
aircraft noise, which has a high impact on people living
in close proximity to an airport. At nine sites near Dubai
International, where the volume of aircraft activities is
considered among the highest in the world, our investiga-
The author is grateful for the financial support provided
by the College of Graduate Studies and Research at the
University of Sharjah. The author is also grateful for the
assistance of Mrs. Nawal Nayfeh for translating the survey
to Arabic.
REFERENCES
[1] http://www.dubaiairport.com/DIA/English/TopMenu/About+
DIA/Facts+and+Figures/
[2] http://www.ameinfo.com/143493.html
[3] http://en.wikipedia.org/wiki/Dubai International Airport
[4] Calculated from the arrival-departure schedule over several days
(see:
http://www.dubaiairport.com/DIA/English/MainMenu/
Flight+Information/Arrival-Departure/)
[5] WHO Guidelines to Community Noise, World Health Organization (WHO), Switzerland, 1999. Available at: http://
www.who.int/docstore/peh/noise/guidelines2.html.
[6] L. Jarup et al. (The HYENA Team), ‘‘Hypertension and
exposure to noise near airports: the HYENA study,’’ Environ.
Health Perspect., 116, 329–333 (2008).
[7] E. A. M. Franssen, C. M. A. G. van Wiechen, N. J. D.
Nagelkerke and E. Lebret, ‘‘Aircraft noise around a large
international airport and its impact on general health and
medication use,’’ Occup. Environ. Med., 61, 405–413 (2004).
[8] T. Schultz, ‘‘Synthesis of social surveys on noise annoyance,’’
J. Acoust. Soc. Am., 64, 377–405 (1987).
[9] http://commons.wikimedia.org/wiki/Image:Dubai Airport.jpg
[10] Assessment of noise annoyance by means of social and socioacoustic surveys Document Number: ISO/TS 15666:2003.
(ISO Store Order #: 924549) (2003).
[11] H. M. Elmehdi and N. Nayfeh, ‘‘Noise levels near roads of
major cities of the United Arab Emirates,’’ The 19th Int.
Congr. Acoust. — ICA07MADRID (2007).
[12] M. L. Davis and S. J. Masten, Principles of Environmental
Engineering and Sciences (McGraw Hill, New York, 2004).
[13] H. M. E. Miedema and C. G. Oudshoorn, ‘‘Annoyance from
transportation noise: relationship with exposure metrics Ldn
and Lden and their confidence intervals,’’ Environ. Health
Perspect., 109, 409–416 (2001).
[14] M. J. Crocker, Handbook of Noise and Vibration Control (John
Wiley & Sons, Inc., New York, 2007) p. 1530.
[15] ICAO, International Standards and Recommended Practices
Environmental Protection Annex 16, International Civil Aviation Organization (1971).
[16] C. Lim, J. Kim, J. Hong, S. Lee and S. Lee, ‘‘The relationship
9
Acoust. Sci. & Tech. 33, 1 (2012)
[17]
[18]
[19]
[20]
[21]
[22]
[23]
[24]
between civil aircraft noise and community annoyance in
Korea,’’ J. Sound Vib., 299, 575–586 (2007).
R. Rylander and M. Bjorkman, ‘‘Annoyance by aircraft noise
around small airports,’’ J. Sound Vib., 205, 533–537 (1997).
H. M. E. Miedema and H. Vos, ‘‘Exposure-response relationships for transportation noise,’’ J. Acoust. Soc. Am., 104, 3432–
3445 (1998).
H. Yoshioka, ‘‘Evaluation and prediction of airport noise in
Japan,’’ J. Acoust. Soc. Jpn. (E), 21, 341–344 (2000).
WG 2 Dose-Effect (European Commission), ‘‘Position paper
on dose response relationships between transportation noise
and annoyance’’ (2002.2).
R. Guski, ‘‘Personal and social variables as co-determinants of
noise annoyance,’’ Noise Health, 3, April–June (1999).
H. M. E. Miedema and H. Vos, ‘‘Demographic and attitudinal
factors that modify annoyance from transportation noise,’’
J. Acoust. Soc. Am., 105, 3336–3344 (1999).
W. G. Health & Socio-Economic Aspects (European Commission), ‘‘Position paper on dose-effect relationships for
night-time noise’’ (2004.11).
H. Sakai and S. Sato, ‘‘Measurements of regional environmental noise by use of PC-based system. An application to the
noise near aircraft,’’ J. Sound Vib., 241, 57–68 (2001).
10
[25] J. M. Fields, R. G. de Jong, T. Gjestland, R. S. Flindell, F. Job,
S. Kurra, P. Lercher, M. Vallet, T. Yano, R. Guski, U.
Felscher-suhr and R. Schumer, ‘‘Standardized general-purpose
noise reaction questions for community noise surveys: Research and a recommendation,’’ J. Sound Vib., 242, 641–679
(2001).
[26] P. D. Schomer, ‘‘Noise monitoring in the vicinity of general
aviation airports,’’ J. Acoust. Soc. Am., 74, 1764–1772 (1983).
[27] T. N. Wu and T. S. Yu, ‘‘Aircraft noise, hearing ability and
annoyance,’’ Arch. Environ. Health, 50, 452–456 (1995).
[28] A. Garcia and L. J. Faus, ‘‘The community exposure to aircraft
noise around six Spanish airports,’’ J. Sound Vib., 164, 45–52
(1993).
[29] D. S. Michaud, S. E. Keith and D. McMurchy, ‘‘Noise
annoyance in Canada,’’ Noise Health, 7(27), pp. 39–47 (2005).
[30] J. K. Upaghyay and V. K. Jain, ‘‘Aircraft-induced noise levels
in some residential areas of Delhi,’’ Environ. Monit. Assess.,
56, 195–207 (1999).
[31] A. Marzzano and M. Recuero, ‘‘Application of pilot survey in
population exposed to noise levels produced by air operations
of the International Airport Arturo Merino Benitez of Santiago
Chile,’’ 19th Int. Congr. Acoust. — ICA07MADRID (2007).