Harita Dergisi, Temmuz 2023; 170: 23-40
RESEARCH ARTICLE / ARAŞTIRMA MAKALESİ
Spatio-temporal Analysis of Sentinel-5P Data of Konya City Between 20192021
(2019-2021 Yılları Arası Konya İli Sentinel-5P Verilerinin Mekâna-Zamana Dayalı Analizi)
Hasan Bilgehan MAKİNECİ*
, Duygu ARIKAN
, Damlanur ALKAN
, Lütfiye KARASAKA
Konya Teknik Üniversitesi, Mühendislik ve Doğa Bilimleri Fakültesi, Harita Mühendisliği, Konya
*Sorumlu yazar: hbmakineci@ktun.edu.tr, darikan@ktun.edu.tr, dalkan@ktun.edu.tr, lkarasaka@ktun.edu.tr
Received (Geliş Tarihi): 09.04.2023
Accepted (Kabul Tarihi): 20.07.2023
bozmaktadır. Bu nedenle kirlilik miktarının düzenli
olarak izlenmesi ve gerekli önlemlerin alınması
gerekmektedir. Bu amaçla gerçekleştirilen bu
çalışmada, uzaktan algılama verileri kullanılarak Konya
ilinde 2019-2021 yılları arasındaki kirletici gazların
durumu incelenmiştir. Veriler, Avrupa Uzay Ajansı
(ESA) tarafından yörüngeye fırlatılan Sentinel-5
Precursor
(S5P)
uydusuna
bağlı
TROPOMI
algılayıcısından elde edilmiştir. Bu algılayıcıdaki
sensörler tarafından çeşitli atmosferik gazlara (ozon,
metan, karbon monoksit, nitrojen dioksit, kükürt dioksit
ve formaldehit) ait zamansal değişim belirlenebilir. Bu
amaçla Google Earth Engine (GEE) platformu ile S5P
Düzey-2 verilerine ulaşılmış ve her bir veriyi elde etmek
için farklı kodlar yazılmıştır. Daha sonra çalışma bölgesi
için veri elde etme işlemi tamamlanmıştır. Çalışma alanı
için belirlenen tarihler arasındaki aylık karbon monoksit,
ozon, amonyak ve nitrojen dioksit gazları miktarları
grafiklerde gösterilmiş ve her yıl için haritalar üretilmiştir.
Sonuç olarak geniş sulak alanlarda ve ormanlık
alanlarda metan gazının görülmediği, NO2, O3 ve CO
gazlarının minimum değerlerinin yaz aylarında, CH4
gazının ise kış aylarında olduğu tespit edilmiştir. İl
merkezinin batısı ile güneyi arasında kalan bölgenin
havayı kirletici gazlar açısından en sağlıklı bölge olduğu
da belirlendi.
ABSTRACT
Uncontrolled energy consumption by human beings,
such as the increase in the demand for the gases used
for heating purposes in houses, the rise in the number
of industrial production facilities, and the uncontrollable
levels of the gases emitted from the exhausts of motor
vehicles, are among the causes that trigger chemical
gas formation in the atmosphere. Increases in air
pollution threaten people's health and disrupt ecological
balances. For this reason, regularly monitoring the
amount of pollution and taking the necessary
precautions is crucial. In this study, which was
conducted for this reason, the state of polluting gases
between 2019-2021 in the province of Konya was
examined using remote sensing data. The data were
obtained from the TROPOMI instrument attached to the
Sentinel-5 Precursor (S5P) satellite launched into orbit
by the European Space Agency (ESA). Various
atmospheric gases (ozone, methane, carbon monoxide,
nitrogen dioxide, sulfur dioxide, and formaldehyde) can
be detected by the sensors in this device. For this
purpose, S5P Level-2 data was accessed via the
Google Earth Engine (GEE) platform, and different
codes were written to obtain each data. Then, the data
collection for the study region was completed. The
monthly amount of carbon monoxide, ozone, methane,
and nitrogen dioxide gases for the study area between
the specified dates are shown in the graphs, and maps
are produced for each year. As a result, it has been
determined that methane gas is not observed in
extensive wetlands and forest areas, and the minimum
values of NO2, O3, and CO gases are in the summer
months and CH4 gas in the winter months. It has also
been determined that the region between the west and
the south of the city center is the healthiest region in
terms of air pollutant gases.
Anahtar Kelimeler: Google Earth Engine, Kirletici
Gazlar, Konya Hava Kalitesi, Sentinel-5P, TROPOMI
uydusu
1. INTRODUCTION
In recent studies, polluting air emissions have
been associated with meteorological conditions
and human activities (Balmes, 2019; Cheung, et
al., 2020; Kurata, et al., 2020; Lu, et al., 2019;
Ghasempour, et al., 2021). The seasonal and
temporal analysis of different meteorological
parameters, and the relationship between the
atmosphere and air temperature in urban areas,
has been supported by several studies in the
literature (Arıkan & Yıldız, 2022; Ghasempour, et
al., 2021; Safarianzengir, et al., 2020; Sager,
2019; Sobhani & Zengir, 2019; Sobhani & Zengir,
2020). Researchers have determined that the
primary purpose for this is to determine which
factors influence the air temperature in the
atmosphere during the day in urban areas. In
Keywords: Google Earth Engine, Konya Air Quality,
Pollutant Gases, Sentinel-5P, TROPOMI Satellite
ÖZ
Konutlarda ısınma amaçlı kullanılan gazlara olan
talebin artması, endüstriyel üretim tesislerinin sayısının
artması, motorlu taşıtların egzozlarından çıkan gazların
kontrol
edilemeyen
seviyelere
ulaşması
gibi
insanoğlunun kontrolsüz enerji tüketimi, atmosferde
kimyasal gaz oluşumunu tetikleyen nedenler
arasındadır. Hava kirliliğindeki artışlar insan sağlığını
tehdit etmekte ve çevresel yaşam dengelerini
To cite this article/Atıf: Makineci, H.B., Arıkan, D., Alkan, D., & Karasaka, L. (2021). Spatio-temporal Analysis of Sentinel-5P Data
of Konya City Between 2019-2021. Harita Dergisi, 170, 23-40
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Harita Dergisi, Temmuz 2023; 170: 23-40
Spatio-Temporal Analysis of Sentinel-5P Data of Konya City Between 2019-2021
addition, as a result of these studies, the factors
that cause air pollution events in urban areas are
identified.
Ghasempour et al., 2021b). Makineci (2022)
conducted a study on the region’s air pollution by
using S5P data and terrestrial stations on the
Anatolian and European parts of İstanbul, the
metropolitan city of Türkiye. As a result of the
study, in which ground stations and remote
sensing data were used, consistent results were
revealed for two different centers of air pollution.
Stratoulias and Nuthammachot (2020) found a
strong positive correlation between data from
ground stations for an urban area and data from
S5P.
Air pollution refers to the fact that air pollutants
in the atmosphere reach a level above average
due to human or natural causes, and their
presence in the atmosphere in density, amount,
and time that may adversely affect human health,
living life, and ecological balance. In other words,
it is expressed as the deterioration of the natural
composition of the air. Artificial sources of air
pollution occur as a result of human activities. As
a result of heating, transportation, and industry,
there is an increase in the number of pollutants
emitted into the atmosphere. Heating boilers and
solid, liquid, and gas fuel stoves for heating, ships,
motor vehicles, railways, and airplanes in the field
of transportation, processes carried out in the
industry and power plants that produce thermal
and hydraulic energy have a direct negative effect
on air pollution (Ibbetson, Symonds, &
Hutchinson). In contrast, natural sources of air
pollution are natural events (URL-2). Particularly
prevalent examples of natural sources are
earthquakes, forest fires, volcanic eruptions, dust
storms, swamps, oceans, and seas. Air pollutants
from natural events do not linger in the
atmosphere for long. Investigation of changes in
the concentration of carbon monoxide, nitrogen
dioxide, ozone, and methane, known as air
pollutants, is seen as a threat to human health, the
ecosystem,
biodiversity,
and
climate
(Safarianzengir et al., 2020). For this reason,
monitoring polluting gases and examining their
effects on humans and the environment is
necessary.
In line with the findings obtained from the
studies, the consistency of the terrestrial and
remote sensing data in determining anthropogenic
emissions is observed. As a result, it has been
concluded that satellite images can be used to
detect pollutants, present the spatial distribution of
gases and particles that cause air pollution, cover
large areas, and provide repeated measurements
due to the cost of establishing ground-based
stations in the studies. In addition, S5P satellite
data have benefited from the amount of gas
released into the atmosphere and find solutions to
the problems such as in studies on forest fires
(Arikan & Yildiz, 2023; Singh et al., 2021), in the
detection of oil refineries and fields (Farahat,
2022), and in explaining the relationship between
air pollution and diseases (Arıkan & Yıldız, 2021;
Balmes, 2019; Ibbetson et al., 2020; Kurata et al.,
2020; Lu et al., 2019).
Since air pollution is a global issue, the whole
world must reduce their emissions of polluting
gases to the minimum level locally. For this
purpose, a comprehensive analysis of air pollution
in Konya, Türkiye's largest city, was carried out to
contribute to the literature. Temporal and spatial
analyzes of methane (CH4), ozone (O3), carbon
monoxide (CO), and nitrogen dioxide (NO2) gases,
which are the primary air pollutants within the
borders of Konya Province, were conducted
between July 2019 and December 2021, using the
Google Earth Engine (GEE) platform and the
obtained S5P data. The air quality of Konya
province was monitored monthly between 20192021 by dividing the data into separate equal grids
(25 x 25 m). It has been attempted to determine
the increase or decrease of the pollutants in the
30-month period and the responsible factor. The
fact that there is no other research in the literature
that maps the air pollutants of Konya for such a
long period by using the GEE platform on the S5P
satellite since the data began to be published to
the users encouraged this study. The density of
the data, the long-term spatio-temporal analysis,
High-resolution Sentinel-5P (S5P) TROPOMI
satellite data have recently gained popularity in air
quality monitoring research (Singh et al., 2021;
Wang, et al., 2022). The S5P, developed to use
institutes in the Netherlands, the United Kingdom,
Finland, and Germany for scientific studies, was
launched into orbit in 2017 on a seven-year
operation (Farahat, 2022). The satellite data have
a spatial resolution of 3.5 × 5.5 km and a temporal
resolution with daily periods (Theys et al., 2017).
Thanks to this remote sensing platform, spatial
and temporal analyzes, and monitoring of air
quality variability are carried out more
comprehensively. Griffin et al. (2019) found a high
correlation between the vertical column density of
NO2 gas and ground-based observations. In the
study by Wang et al. (2022), NO2, CO, and CO2
gases were used to compare the data results
produced by ground observations and remote
sensing techniques (Ghasempour et al., 2021a;
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Hasan Bilgehan MAKİNECİ, Duygu ARIKAN, Damlanur ALKAN, Lütfiye KARASAKA
and the study's wide scope can be said to be the
study's original aspect.
2. MATERIALS AND METHODS
a. Study Area and Workflow
Konya which is located in the Central Anatolia
region of Türkiye and has the largest surface area
(38 873 km²), was chosen as the study area. The
city is located between 36°41' and 39°16' north
latitudes and 31°14' and 34°26' east longitudes
(Figure 1).
In the city, which is influenced by the
continental climate, the summer is dry and hot,
while the winter is extremely cold and has heavy
snowfall. Rainfall is seen throughout the city in the
spring and winter seasons. The city is located at
an altitude of 1016 m above sea level. Due to the
mountains surrounding the city, the effect of the
wind is limited and causes fog/smoke
condensation in the city (Kunt & Dursun, 2016).
This causes polluted air to accumulate in the city.
According to 2022 population data, it is
Türkiye's sixth most populous city, with 2 296 347
people. Although the primary economic income
source of the region is known as agricultural
production, it has also acquired the reputation of
an industrial production city due to the increasing
industrialization in recent years. The city trades
quickly with other central provinces in the country
thanks to its widespread transportation lines. It
also contributes to the national economy by
producing goods in a variety of sectors
(agricultural machinery and equipment, defense
and automotive industry, food, etc.).
SEYDİŞEHİR
Figure 1. (a) (b) Study area (Figure 1. (a)
Produced by the General Directorate of Mapping))
b. S5P Data
The data obtained from the TROPOMI device
connected to the Sentinel-5 satellite by the
European Space Agency was used in this study.
Various atmospheric gases (ozone, methane,
carbon monoxide, nitrogen dioxide, sulfur dioxide,
and formaldehyde) are detected and monitored by
the sensors in this device (Slagter, et al., 2020;
Veefkind et al., 2012). The satellite's primary
purpose, launched on October 13, 2017, is to
collect atmospheric measurements with high
spatio-temporal resolution for air quality, ozone,
UV radiation, climate monitoring, and forecasting
(Safarianzengir et al., 2020). It scans the Earth
daily and records images with a coverage area of
7 km × 3.5 km. The satellite, expected to have a
seven-year operational life, is in the low-orbiting
satellite class with an orbital reference altitude of
824 km. It is in a sun-synchronous orbit with the
equatorial transit at the nodal point rising at 13:30
local time, with an orbital inclination of
approximately 98.7 degrees in polar orbit. The
While these factors contribute to the
development of the city, their effects on airpolluting gases should also be identified. For this
reason, in this study, the air pollution of Konya
province was investigated temporally and spatially
by using S5P satellite data. Sentinel-5 data of
NO2, CO, O3, and CH4 polluting gases were
obtained from the GEE platform within the
specified date range for analysis.
Each gas with the same temporal and spatial
resolution used in the study has been analyzed
with charts, then visualized and represented on
maps. The workflow diagram of the study is
presented in Figure 2.
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Spatio-Temporal Analysis of Sentinel-5P Data of Konya City Between 2019-2021
orbital cycle is 16 days. The satellite is equipped
with the most advanced TROPOMI instrument for
measuring the ultraviolet-visible (270–500 nm),
near-infrared (675–775 nm), and short-wave
infrared (2305–2385 nm) spectral bands (Rohi &
Ofualagba, 2020; Safarianzengir et al., 2020). The
TROPOMI spectrometer in Sentinel 5P measures
high
spectral
UV
luminance
(https://sentinels.copernicus.eu/web/sentinel/miss
ions/sentinel-5p). The download of Sentinel-5P
Level-2 data was carried out through the GEE
platform, an infrastructure of Google. A separate
coding process was carried out for each pollutant
gas. L2 level data received from the Sentinel
satellite is defined at the L3 level through GEE.
Therefore, Spatial Resolution corresponds to
around 1 km. This platform is a web service
developed for spatial analysis (Gorelick et al.,
2017). It has gained popularity in remote sensing
studies in recent years because it is free to use
and provides easy access to data (Farahat, 2022;
Singh et al., 2021). In addition, GEE (Li et al.,
2022), which enables extensive data processing,
offers its users the opportunity to create and save
their catalogs. Query and evaluation processes
are also carried out through the functional
structures in the system (Gorelick et al., 2017).
gases. From 2019 to 2021, 118 images were
obtained for all of the used gases. Then, the
downloaded images were opened in the GIS
environment and visualized (Figure 11, Figure 12,
Figure 13, Figure 14 and Figure 15).
In order to eliminate the gaps seen in the
methane gas daily data and to create a standard
for all gases, a three-day data format was
downloaded. Three-day data yield more
meaningful results, so the gaps in the daily data
are not filled with interpolation, based on the
principle of producing maps entirely from S5P
sensor data. In the GEE platform, there is a preacceptance assumption that the data will be
downloaded for three days.
The NO2 (nitrogen dioxide) vertical column,
CH4 (methane) column average dry air mixing
ratio, total O3 (ozone) atmospheric column
between the surface and upper atmosphere, and
CO (carbon monoxide) column data for 2019-2021
are downloaded as offline (OFFL). This is primarily
because it should contain data from a single orbit.
Additionally, only the OFFL feature is available for
CH4 data. In this study, data on certain monthly
days were downloaded for each gas using the
median code in GEE. This path was followed as
there was a lack of data on certain days for some
Figure 2. Workflow of research
Table 1. Sentinel-5P data used in research.
Data Type
Temporal Resolution
Spatial Resolution
O3
First 3 days of every month
1113.2 meters
CH4
First 4 days of every month
1113.2 meters
CO
First 10 days of every month
1113.2 meters
NO2
First 10 days of every month
1113.2 meters
26
Calibration Type
Radiometric and
Geometric Calibrated
Radiometric and
Geometric Calibrated
Radiometric and
Geometric Calibrated
Radiometric and
Geometric Calibrated
Harita Dergisi, Temmuz 2023; 170: 23-40
Hasan Bilgehan MAKİNECİ, Duygu ARIKAN, Damlanur ALKAN, Lütfiye KARASAKA
c. Statistical analysis
can be expressed as oil and natural gas systems,
agricultural activities, coal mining, stationary and
mobile incineration, wastewater treatment, and
specific industrial processes. Swamps can be an
example of natural causes (Lorente et al., 2021).
Thanks to the near-infrared (NIR) and short-wave
infrared (SWIR) spectral bands found in satellites,
CH4 gas is observed through its spread on the
Earth's surface and atmosphere. Data from
TROPOMI measurements are recorded with the
RemoTeC algorithm (Lorente et al., 2021). The
residence time of this gas in the atmosphere has
been determined as approximately ten years (Hu
et al., 2018).
After obtaining the data, all visual base maps
were gridded after trimming, and classification
processes were applied to the leading data
visualized in the GIS environment. The value
corresponding to the midpoint of each grid was
then calculated. Following the calculation, the
thirty-month data of the values corresponding to
the grid midpoints according to the months were
tabulated. In Table 1, there are blank values for
different data types in some months of the data
consisting of 332 points. Gaps without data were
not included in the statistical analysis of the study.
No interpolation was applied to the non-data
regions, and their values were left as naught.
When the July 2019 - December 2021 data for
the whole of Konya were examined (Figure 3), it
was determined that the highest amount of CH4
was in September 2021, with 1900 mg/m3. When
the maximum and minimum values of methane
gas are examined within each month, it is
understood that the mean is 40 mg/m3. Since
methane gas is seen primarily as a result of
heating, there is a standard distribution across
urban areas. In addition, it has been determined
that CH4 release is not significantly affected by
season because a balanced graphic curve was
obtained in the summer and winter seasons.
Among the values obtained in Table 1, the
maximum, minimum, mean, and median values
were determined according to each data type.
Additionally, standard deviation (StD.) values
were calculated for the analysis.
3. RESULTS
a. Findings Obtained for CH4 Gas
Methane gas (CH4) is the greenhouse gas with
the most critical polluting effect after carbon
dioxide (Hu et al., 2018). Therefore, it is a type of
gas that causes global warming at a higher rate
than other pollutants (Stocker, 2014). CH4 gas is
emitted into the atmosphere, either by natural or
anthropogenic resources. Anthropogenically, it
In the time period of the study, 6,925 mg/m3
minimum StD. values in July 2021 and 12,658
mg/m3 maximum StD. values in April 2020 were
determined (Figure 4).
Figure 3. CH4 Data Analysis (Minimum, Maximum, Mean and Median Values)
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Spatio-Temporal Analysis of Sentinel-5P Data of Konya City Between 2019-2021
b. Findings Obtained for CO Gas
values are presented in Figure 6. The highest
amount of CO in the monthly period was
determined in April 2020, and the maximum was
reached with a value of 0.1818 mol/m2 in that
month. The lowest amount of CO in the study
period was recorded in November 2020, with a
value of 0.1255 mol/m2. It is worth mentioning that
the change in temperature because, as can be
seen from the graph, while there is a decrease in
the amount of CO in the winter, it increases in the
summer.
CO gas remains in the atmosphere for less
time (by approximately two months) than methane
gas. It is a product of incomplete combustion
encountered in building heating, coal power
generation, wood and grass burning, vehicles, and
biomass burning (Ghahremanloo, Lops, Choi, &
Mousavinezhad, 2021). About 40% of CO is
naturally generated (volcanic eruptions, natural
gas emissions, degradation of plants and animals,
forest fires, and 60% results from the consumption
of fossil fuels, garbage disposal systems, tobacco
smoke, and coal fires (Kaplan, Avdan, & Avdan,
2019). Graphs were created each month from the
CO findings obtained to cover the entire study
area. Monthly maximum, minimum, mean and
median values are given in Figure 5, and StD.
According to the StD. values of CO gas, it
reached maximum levels of 0.0042 mol/m2 in the
same period (April 2020) as methane gas. It has
been detected at a minimum in December 2020
with 0.0005 mol/m2.
Figure 4. CH4 Data Analysis (StD. Values)
Figure 5. CO Data Analysis (Minimum, Maximum, Mean and Median Values)
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Hasan Bilgehan MAKİNECİ, Duygu ARIKAN, Damlanur ALKAN, Lütfiye KARASAKA
Figure 6. CO Data Analysis (StD. Values)
c. Findings Obtained for NO2 Gas
to the StD. values in 30 months, A minimum of
0.0005 mol/m2 was obtained in December 2020,
and a maximum of 0.0046 mol/m2 was obtained in
April 2020.
Nitrogen oxides (NOx) are generally the type of
gas that occurs during combustion (Ialongo, Virta,
Eskes, Hovila, & Douros, 2020). The leading
sources of this type of gas are natural (lightning
strikes) and anthropogenic pollution (burning of
agricultural fields, burning fossil fuels, industrial
production, and emissions from vehicle exhaust)
sources (Hashim, et al., 2021; Ialongo et al.,
2020).
ç. Findings Obtained for O3 Gas
The O3 concentration commonly found in the
air consists of the photochemical interaction of the
precursor gases (nitrogen oxides, volatile organic
compounds) (Hashim et al., 2021). In cases of
exposure to O3 gas, airway inflammation, and
respiratory disorders can be observed in living
things due to oxidative stress (Adhikari & Yin,
2020). The magnitude and rate of O3 emissions
depend on atmospheric conditions and seasonal
factors (Hashim et al., 2021).
NO2 gas increases the symptoms of respiratory
diseases (such as coughing, wheezing, or
difficulty breathing) by affecting human health
(Stratoulias & Nuthammachot, 2020). In addition,
it causes acid rain by interacting with water,
oxygen, and other chemicals in the atmosphere
(Hashim et al., 2021). This occurrence weakens
the soil and reduces productivity in agricultural
activities. In areas where nitrogen dioxide
increases, the air becomes hazy, and there is
even a decrease in visibility.
O3 emission appears to be directly proportional
to NOx. If O3 is high in a region, NOx is also found
to be high, or vice versa (Hashim et al., 2021). On
the other hand, while the amount of NOx is high in
urban areas with high traffic density, reductions in
O3 emissions are observed. This is because the
gas density in urban areas is transported toward
rural areas (Dentener et al., 2020). Due to the
increase in temperatures and the contribution of
sun rays to the formation of O3, seasonal changes
cause a decrease in O3 gas (Stratoulias &
Nuthammachot, 2020). As determined in Figure 9,
while O3 was at its maximum levels in April 2020
and 2021, it appears to have been at minimum
levels in October, November, and December.
When the StD. values for O3 are examined (Figure
10), the minimum value of 0.0004 mol/m2 and
maximum value of 0.0040 mol/m2 were obtained
in December 2020 and April 2020, respectively.
When the results of the Std. values of all gases
are examined, it can be determined that the
Figures 7 and 8 display the time series of NO 2
measurements used in the analysis, covering the
period from July 2019 to December 2021. In
Figure 7, the maximum, minimum, median, and
mean values of the daily monthly data are given,
while in Figure 8, the StD. the graph is shown.
While the maximum level of NO2 in the studied
period was observed in April 2020 with a value of
0.18176 mol/m2, the minimum level was observed
in November 2020 with a value of 0.11895 mol/m2.
It can be said that there is a seasonal effect in NO2
gas. As shown in Figure 7, while there is an
increase in the amount of this gas in the spring
season (April, May), there is a decrease in the
autumn season (October, November). According
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Spatio-Temporal Analysis of Sentinel-5P Data of Konya City Between 2019-2021
maximum and minimum values of all gases are
observed in the same months. In all gases, the
maximum level was reached in April 2020. While
the minimum CO, NO2, and O3 gas are December
2020, the time when CH4 gas is minimum is July
2021.
Figure 7. NO2 Data Analysis (Minimum, Maximum, Mean and Median Values)
Figure 8. NO2 Data Analysis (StD. Values)
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Hasan Bilgehan MAKİNECİ, Duygu ARIKAN, Damlanur ALKAN, Lütfiye KARASAKA
Figure 9. O3 Data Analysis (Minimum, Maximum, Mean and Median Values)
Figure 10. O3 Data Analysis Results (StD. Values)
d. Produced Map Outcomes
When the CH4 gas map is examined between
the years 2019-2021, it is seen that no data is
recorded in the wetlands. The main reason for this
is that the effect of methane gas is mainly seen in
swamps, reeds, or garbage areas. When the
maps of NO2 and O3 gases are examined, it has
been determined that the amount of NO 2 is high
and the amount of O3 is low in the parts where the
transportation lines are located. It has been
determined that O3 emissions are primarily
concentrated in rural areas. As seen in Figure 11,
while the amount of O3 gas increases relatively in
rural areas in the northern parts of the city, it is
found in lower amounts in the southern parts of the
city where the altitude is high.
In this study, S5P satellite images taken from
the GEE platform were converted to raster and
vector maps in order to interpret the air pollutants
in the Konya Province in spatio-temporal time. In
order to determine the seasonal effect of all
polluting gases used in the study, map outputs
were produced by choosing the beginning of
spring and the beginning of autumn. The most
striking point is that the amount of polluting gas is
high in the parts of the transportation networks on
all maps. It can be said that pollutants vary
according to the seasons and are also related to
latitude, longitude, and altitude values.
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Figure 11. September 2019 Air Quality Map of Konya (A-CH4, B-O3, C-CO, D-NO2)
Spatio-Temporal Analysis of Sentinel-5P Data of Konya City Between 2019-2021
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Figure 12. May 2020 Air Quality Map of Konya (A-CH4, B-O3, C-CO, D-NO2)
Hasan Bilgehan MAKİNECİ, Duygu ARIKAN, Damlanur ALKAN, Lütfiye KARASAKA
33
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Figure 13. September 2020 Air Quality Map of Konya (A-CH4, B-O3, C-CO, D-NO2)
Spatio-Temporal Analysis of Sentinel-5P Data of Konya City Between 2019-2021
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Figure 14. May 2021 Air Quality Map of Konya (A-CH4, B-O3, C-CO, D-NO2)
Hasan Bilgehan MAKİNECİ, Duygu ARIKAN, Damlanur ALKAN, Lütfiye KARASAKA
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Figure 15. September 2021 Air Quality Map of Konya (A-CH4, B-O3, C-CO, D-NO2)
Spatio-Temporal Analysis of Sentinel-5P Data of Konya City Between 2019-2021
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Hasan Bilgehan MAKİNECİ, Duygu ARIKAN, Damlanur ALKAN, Lütfiye KARASAKA
The amount of all pollutants in 2020 is less than
in other years. This is due to the epidemic disease
(COVID-19), which spread worldwide during this
period, showing its impact on Türkiye. As a result
of the restrictions put in place to prevent the
spread of the epidemic, it was determined that the
impact of the pollutant gases decreased. It has
also been determined that the number of
pollutants in 2021 were higher than in other years
(Figure 12 and Figure 13). This rise has also
become meaningful due to the gradual removal of
the measures taken for the epidemic. In 2020,
methane gas was standard in the northern part of
the city. The white parts in the methane gas map
are the part where the data is not recorded.
Kadınhanı, Sarayönü, and Yunak are the districts
where methane gas is seen at high levels. When
the methane gas values in March 2021 are
examined, it is seen that there are increases in the
Karapınar district. Since this region is a reed and
swamp area, methane gas increased due to the
decrease in water and the resulting drought
(Figure 14 and Figure 15).
significant correlation between the COVID-19
outbreak and NO2 gas. In addition, in their
analysis on a national basis, they found that NO2
gas showed a considerable decrease in the
lockdown period, except for regular periods
(Ghasempour et al., 2021a).
The situation of four polluting gases over a 30month period has been examined using satellite
data. In the study, national air quality ground
station data were also downloaded. However, due
to the lack of data on ground stations, it was not
used in the analysis. In this study, analyses and
discussions were carried out using only S5P
satellite data due to factors such as missing
terrestrial station data (disorder in stations) or
stations representing a spatially narrow region.
In recent years, air quality research has
become one of the critical research topics due to
the increase in air pollution, the adverse effects of
air pollution on living health, and the availability of
rapid and reliable evaluation of air quality with
remote sensing satellites. The findings are of great
importance to everyone because of the issue’s
impact on human health and ecological order.
Clean air is a vital element for the survival of all
living things. For this reason, in this study, the
pollutant gases in the Konya province were
analyzed temporally and spatially using S5P
satellite data from July 2019 to March 2021. As a
result, over a 30-month period, the regions in
which the pollutants are found and the months
when the pollutants are at maximum and minimum
levels have been determined. It has been
documented that it is possible to collect
information about pollutants not only temporally
but also spatially, thanks to satellite data.
In their study, Kaplan et al. (2019) and
Ghasempour et al. (2021) examined countrybased polluting gases. Thus, using the Sentinel5P satellite, they showed that the pollution of a
large-scale region could be detected. This study
discussed the temporal analysis of the states of
polluting gases in small-scale cities, and their
detectability was revealed. In addition, more
gases were analyzed together, and their relations
with each other were established. As in this study,
the GEE platform was used to obtain the data. It
has been seen that GEE is easy to use and access
data, and it can be preferred for accessing S5P
data in future studies.
5. CONCLUSIONS
4. DISCUSSIONS
The air quality in the atmosphere decreases
because the smoke content that results from the
combustion of fuels such as diesel and gas pollute
the environment from factories and houses in
winter, including the pollutants that are the subject
of the research. In addition, pollutants are
observed more intensely in the atmosphere in
winter due to the effect of wind (air reversal
phenomenon) compared to warmer seasons.
When the gases released in the winter and those
released in the summer are compared, it has been
determined that the pollutants in hot weather are
much more dangerous in terms of air quality. This
is because gases such as NO2 from motor
vehicles accumulate in the lower parts of the
atmosphere during the summer months, and this
is a factor that directly affects human health.
ORCID
Hasan Bilgehan MAKİNECİ
https://orcid.org/0000-0003-3627-5826
Duygu ARIKAN
https://orcid.org/0000-00019976-7479
Damlanur ALKAN
https://orcid.org/0000-00022013-0262
Lütfiye KARASAKA
https://orcid.org/00000002-2804-3219
In the study (Ghasempour et al., 2021b)
conducted to detect and analyze NO2 gas from
S5P data, researchers were able to notice a
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Spatio-Temporal Analysis of Sentinel-5P Data of Konya City Between 2019-2021
REFERENCES
Ghasempour, F., Sekertekin, A., & Kutoglu, S. H.
(2021). Google Earth Engine based spatiotemporal analysis of air pollutants before and
during the first wave COVID-19 outbreak over
Turkey via remote sensing. Journal of Cleaner
Production, 319, 128599.
Adhikari, A., & Yin, J. (2020). Short-term effects of
ambient ozone, PM2. 5, and meteorological
factors on COVID-19 confirmed cases and
deaths in Queens, New York. International
Journal of Environmental Research and Public
Health,
17(11),
4047.
doi:https://doi.org/10.3390/ijerph17114047
Ghasempour, F., Sekertekin, A., & Kutoglu, H.
(2021). Effect of first wave COVID-19 outbreak
lockdown measures on satellite-based
tropospheric NO2 over Mersin Province,
Turkey. Intercontinental
Geoinformation
Days, 2, 16-19.
Arikan, D., & Yildiz, F. (2023). Investigation of
Antalya forest fire's impact on air quality by
satellite images using Google earth engine.
Remote Sensing Applications: Society and
Environment,
100922.
doi:https://doi.org/10.1016/j.rsase.2023.10092
2
Ghahremanloo, M., Lops, Y., Choi, Y., &
Mousavinezhad, S. (2021). Impact of the
COVID-19 outbreak on air pollution levels in
East Asia. Science of the Total Environment,
754,
142226.
doi:https://doi.org/10.1016/j.scitotenv.2020.14
2226
Arıkan, D., & Yıldız, F. (2021, Mayıs). An Analysis
of NO2 Emission During COVID-19 Period in
Turkey. 11. Türkiye Ulusal Fotogrametri ve
Uzaktan Algılama Birliği (TUFUAB) Teknik
Sempozyumu, 6-9, Mersin, Türkiye.
Gorelick, N., Hancher, M., Dixon, M.,
Ilyushchenko, S., Thau, D., & Moore, R.
(2017). Google Earth Engine: Planetary-scale
geospatial analysis for everyone. Remote
Sensing of Environment, 202, 18-27.
doi:https://doi.org/10.1016/j.rse.2017.06.031
Arıkan, D., & Yıldız, F. (2022,Ekim). Landsat-8
Uydusu
Kullanılarak
2018-2021
Yılları
Arasında İstanbul'daki Kentsel Isı Adasının
İncelenmesi. 362-372, İzmir, Türkiye.
Balmes, J. R. (2019). Household air pollution from
domestic combustion of solid fuels and health.
Journal of Allergy and Clinical Immunology,
143(6),
1979-1987.
doi:https://doi.org/10.1016/j.jaci.2019.04.016
Griffin, D., Zhao, X., McLinden, C. A., Boersma,
F., Bourassa, A., Dammers, E., . . . Fioletov, V.
(2019). High‐resolution mapping of nitrogen
dioxide with TROPOMI: First results and
validation over the Canadian oil sands.
Geophysical Research Letters, 46(2), 10491060.
doi:
https://doi.org/10.1029/2018GL081095
Cheung, C. W., He, G., & Pan, Y. (2020).
Mitigating the air pollution effect? The
remarkable decline in the pollution-mortality
relationship in Hong Kong. Journal of
Environmental Economics and Management,
101,
102316.
doi:https://doi.org/10.1016/j.jeem.2020.10231
6
Ghasempour, F., Sekertekin, A., & Kutoglu, S. H.
(2021). Google Earth Engine based spatiotemporal analysis of air pollutants before and
during the first wave COVID-19 outbreak over
Turkey via remote sensing. Journal of Cleaner
Production,
319,
128599.
doi:
https://doi.org/10.1016/j.jclepro.2021.128599
Dentener, F., Emberson, L., Galmarini, S.,
Cappelli, G., Irimescu, A., Mihailescu, D., van
den Berg, M. (2020). Lower air pollution during
COVID-19 lock-down: improving models and
methods estimating ozone impacts on crops.
Philosophical Transactions of the Royal
Society
A,
378(2183),
20200188.
doi:https://doi.org/10.1098/rsta.2020.0188
Hashim, B. M., Al-Naseri, S. K., Al-Maliki, A., & AlAnsari, N. (2021). Impact of COVID-19
lockdown on NO2, O3, PM2. 5 and PM10
concentrations and assessing air quality
changes in Baghdad, Iraq. Science of the Total
Environment,
754,
141978.
doi:https://doi.org/10.1016/j.scitotenv.2020.14
1978
Farahat, A. (2022). The Impact of the 2020 Oil
Production
Fluctuations
on
Methane
Emissions over the Gulf Cooperation Council
(GCC) Countries: A Satellite Approach.
Atmosphere,
13(1),
11.
doi:https://doi.org/10.3390/atmos13010011
38
Harita Dergisi, Temmuz 2023; 170: 23-40
Hasan Bilgehan MAKİNECİ, Duygu ARIKAN, Damlanur ALKAN, Lütfiye KARASAKA
Hu, H., Landgraf, J., Detmers, R., Borsdorff, T.,
Aan de Brugh, J., Aben, I., . . . Hasekamp, O.
(2018). Toward global mapping of methane
with TROPOMI: First results and intersatellite
comparison to GOSAT. Geophysical Research
Letters,
45(8),
3682-3689.
doi:
https://doi.org/10.1002/2018GL077259
Lu, M., Schmitz, O., Vaartjes, I., & Karssenberg,
D. (2019). Activity-based air pollution exposure
assessment:
differences
between
homemakers and cycling commuters. Health &
place,
60,
102233.
doi:https://doi.org/10.1016/j.healthplace.2019.
102233
Ialongo, I., Virta, H., Eskes, H., Hovila, J., &
Douros,
J.
(2020).
Comparison
of
TROPOMI/Sentinel-5
Precursor
NO
2
observations
with
ground-based
measurements in Helsinki. Atmospheric
Measurement Techniques, 13(1), 205-218.
doi:https://doi.org/10.5194/amt-13-205-2020
Makineci, H. B. (2022). İstanbul İli Merkez
İlçelerindeki NO2 ve CO Emisyonlarının
Uzaktan Algılama ve Yersel İstasyon Verileri
Kullanılarak İncelenmesi. Türkiye Uzaktan
Algılama
Dergisi,
4(2),
62-74.
https://doi.org/10.51489/tuzal.1160333
Rohi, G., & Ofualagba, G. (2020). Autonomous
monitoring, analysis, and countering of air
pollution using environmental drones. Heliyon,
6(1),
e03252.
doi:https://doi.org/10.1016/j.heliyon.2020.e032
52
Ibbetson, A., Symonds, P., & Hutchinson, E.
(2020). Data to support small area health
impact modelling of air pollution in the United
Kingdom. Data in brief, 29, 105148.
doi:https://doi.org/10.1016/j.dib.2020.105148
Kaplan, G., Avdan, Z. Y., & Avdan, U. (2019).
Spaceborne nitrogen dioxide observations
from the sentinel-5P TROPOMI over Turkey.
Multidisciplinary digital publishing institute
proceedings,
18(1),
4.
doi:https://doi.org/10.3390/ECRS-3-06181
Safarianzengir, V., Sobhani, B., Yazdani, M. H., &
Kianian, M. (2020). Monitoring, analysis and
spatial and temporal zoning of air pollution
(carbon monoxide) using Sentinel-5 satellite
data for health management in Iran, located in
the Middle East. Air Quality, Atmosphere &
Health,
13,
709-719.
doi:https://doi.org/10.1007/s11869-02000827-5
Kunt, F., & Dursun, Ş. (2016). Air pollution
modelling of Konya City center by using
artificial intelligence methods. Wulfenia
Journal, 23(11), 76-87.
Sager, L. (2019). Estimating the effect of air
pollution on road safety using atmospheric
temperature
inversions.
Journal
of
Environmental Economics and Management,
98,
102250.
doi:https://doi.org/10.1016/j.jeem.2019.10225
0
Kurata, M., Takahashi, K., & Hibiki, A. (2020).
Gender differences in associations of
household and ambient air pollution with child
health: evidence from household and satellitebased
data
in
Bangladesh.
World
Development,
128,
104779.
doi:https://doi.org/10.1016/j.worlddev.2019.10
4779
Singh, S., Singh, H., Sharma, V., Shrivastava, V.,
Kumar, P., Kanga, S., . . . Singh, S. K. (2021).
Impact of forest fires on air quality in Wolgan
Valley, New South Wales, Australia—a
mapping and monitoring study using Google
Earth
engine.
Forests,
13(1),
4.
doi:https://doi.org/10.3390/f13010004
Li, C., Chen, W., Wang, Y., Wang, Y., Ma, C., Li,
Y., Zhai, W. (2022). Mapping winter wheat with
optical and SAR images based on Google
earth engine in Henan Province, China.
Remote
Sensing,
14(2),
284.
doi:https://doi.org/10.3390/rs14020284
Slagter, B., Tsendbazar, N.-E., Vollrath, A., &
Reiche, J. (2020).
Mapping wetland
characteristics using temporally dense
Sentinel-1 and Sentinel-2 data: A case study in
the St. Lucia wetlands, South Africa.
International Journal of Applied Earth
Observation and Geoinformation, 86, 102009.
doi:https://doi.org/10.1016/j.jag.2019.102009
Lorente, A., Borsdorff, T., Butz, A., Hasekamp, O.,
Schneider, A., Wu, L., . . . Pollard, D. F. (2021).
Methane
retrieved
from
TROPOMI:
improvement of the data product and validation
of the first 2 years of measurements.
Atmospheric Measurement Techniques, 14(1),
665-684. doi:https://doi.org/10.5194/amt-14665-2021
39
Harita Dergisi, Temmuz 2023; 170: 23-40
Spatio-Temporal Analysis of Sentinel-5P Data of Konya City Between 2019-2021
Sobhani, B., & Zengir, V. S. (2019). Investigation
hazard effect of monthly ferrrin temperature on
agricultural products in north bar of Iran. The
Iraqi Journal of Agricultural Science, 50(1),
320-330.
doi:https://doi.org/10.36103/ijas.v50i1.298
Sobhani, B., & Zengir, V. S. (2020). Modeling,
monitoring and forecasting of drought in south
and southwestern Iran, Iran. Modeling Earth
Systems and Environment, 6, 63-71.
doi:https://doi.org/10.1007/s40808-01900655-2
Stocker, T. (2014). Climate change 2013: the
physical science basis: Working Group I
contribution to the Fifth assessment report of
the Intergovernmental Panel on Climate
Change: Cambridge university press.
Stratoulias, D., & Nuthammachot, N. (2020). Air
quality development during the COVID-19
pandemic over a medium-sized urban area in
Thailand. Science of the Total Environment,
746,
141320.
doi:https://doi.org/10.1016/j.scitotenv.2020.14
1320
Theys, N., De Smedt, I., Yu, H., Danckaert, T., van
Gent, J., Hörmann, C., . . . Romahn, F. (2017).
Sulfur dioxide retrievals from TROPOMI
onboard Sentinel-5 Precursor: algorithm
theoretical basis. Atmospheric Measurement
Techniques,
10(1),
119-153.
doi:https://doi.org/10.5194/amt-10-119-2017
Veefkind, J. P., Aben, I., McMullan, K., Förster, H.,
De Vries, J., Otter, G., . . . Kleipool, Q. (2012).
TROPOMI on the ESA Sentinel-5 Precursor: A
GMES mission for global observations of the
atmospheric composition for climate, air quality
and ozone layer applications. Remote Sensing
of
Environment,
120,
70-83.
doi:https://doi.org/10.1016/j.rse.2011.09.027
Wang, H., Gong, F.-Y., Newman, S., & Zeng, Z.C. (2022). Consistent weekly cycles of
atmospheric NO2, CO, and CO2 in a North
American megacity from ground-based,
mountaintop, and satellite measurements.
Atmospheric Environment, 268, 118809.
doi:https://doi.org/10.1016/j.atmosenv.2021.1
18809
40