city on six main roads, the results shows that their pro-
posed system can effectively monitor PM2.5 concen-
trations while moving. In Zagreb, (Marjanovi
´
c et al.,
2017) conducted a study using the carry of air mon-
itor wearable devices following a predefined route.
The predefined route was chosen to include 2 major
roads with heavy traffic, a park, a residential area, and
a business area. it was concluded that air pollution
is strongly depending on the traffic exposure. Some
studies have done the experiment on one road to mea-
sure and evaluate the pollution produced by traffic.
In (Moutinho et al., 2020), measurements were taken
along a highway in Atlanta.The results obtained were
compared to measurements that were taken in an ur-
ban area around Atlanta, observing that the concen-
trations of CO and NO2 in the highway were 35%
and 57% higher than the urban background concentra-
tions, respectively. In Pakistan, (Aamer et al., 2018)
conducted a data-set containing around 25000 sam-
ples during a month in a road segment between 2
cities. It was observed that humidity and temper-
ature are negatively correlated against NO2 and in-
herently affect the NO2 balance in air. Other stud-
ies have taken their measurements from fixed loca-
tions either on long or short term. (Gunawan et al.,
2018) developed a portable device placed in three dif-
ferent locations, a hostel, a university, and a roadside.
The obtained results were compared to a dataset gen-
erated by air quality monitoring station at the same
time of the experiment, showing that different places
can have different AQI value even though they are
nearby to each other. (Spandana and Shanmughasun-
dram, 2018) took place in Amrita University, India, to
determine the pollution level inside the campus and
also in a metro city (Bengaluru). The results indi-
cated that the university atmosphere is less polluted
than Bengaluru. (Duangsuwan et al., 2018) measured
the AQI in just 2 points (Bangkok Yai district, and
Pathumwan district, Bangkok.) from Oct. 7 to Oct.
13, 2017. The results showed that the AQI level has
not exceeded 100, making it a safe zone for people.
An Android-based application was implemented by
(Ghosh et al., 2019) that uses the built-in microphone
sensor to capture ambient noise levels and the GPS
sensor for identifying the location, and for validation
they compared the data collected by the application
with sound level meter (Meco-970P 3). The outcome
of this test was illustrated, and the variation of the
application results compared to the sound meter was
in the range of ±3 dB, which clarify the efficient of
the mobiles’ microphone sensors for detecting noise
pollution. (Marjanovi
´
c et al., 2017) proposed a real-
time system to monitor air and noise pollution. They
implemented a mobile application which uses mobile
phone’s microphone to collect noise data and con-
verts the recorded sound pressure to dB and shows
the equivalent sound pressure level for each second in
dB. The results showed that the average noise level
is higher 3dB at the rush hours due to the increas-
ing numbers of vehicles. AQI is the unit or the way
of communication between the institutes responsible
for calculating air pollution level and the public. AQI
is targeting many gasses and sources of air pollu-
tion like (Carbon Monoxide, Lead, Nitrogen Oxides,
Ozone, Particulate matter including PM2.5 and PM10
and Sulfur dioxide). Air quality standards were set
by the US Environmental Protection Agency (EPA)
and were divided into two parts (epa, ); Primary stan-
dards, which were set for the public health protection,
as protecting the health of “sensitive” groups such as
asthmatics, children, and the elderly people, and the
secondary standards, which provide protection to the
public welfare, this includes preventing reduced vis-
ibility and damage to animals, crops, vegetation, and
buildings. Parts per million by volume (PPM), parts
per billion by volume (PPB), and micro-grams per cu-
bic meter of air µg/m3 are the units of AQI measure-
ment. For noise levels, the WHO set guideline val-
ues based on specific environment and large health
impacts (Berglund et al., 2000). The guideline val-
ues are presented taking into consideration all harmful
health effects identified in a particular environment.
The negative effects of noise exposure refer to tempo-
rary or long-term impairment of physical, psycholog-
ical, or social functioning. Decibels (dB) is the unit of
measuring sound or noise level. No study was found
to monitor air or noise pollution in Cairo, Egypt. All
the devices located in Cairo are stationary with a high
cost and only one that is a real-time device, but it only
monitors and measures Pm2.5 concentration in the air
from Katameya Heights in New Cairo city(cit, ). Only
one study took place in Egypt for monitoring noise
pollution, particularly in Alexandria in 2009, (Ghat-
tas, 2009). The literature has proven that no data was
collected in a city-scale. It’s either collected indoors
or in specifically selected regions inside the cities. In
this paper, we aim to generate a dataset for both air
and noise pollution, as it will be the first dataset doc-
umentation for these types of pollution inside Cairo.
Our approach will be as follows; regarding air pol-
lution measurement we are measuring the concentra-
tion of Carbon Dioxide and Nitrogen Oxide as they
are the common gasses that are emitted from vehicles
on the road. In addition of the concentration of PM10
in air, this will be done inside New Cairo City in 2
locations. For noise pollution measurement, a mobile
application was developed and distributed among the
public. The application will have access to the mo-
Real Life Pollution Measurement of Cairo
223