# Investigation on the Impacts of COVID-19 Lockdown and Influencing Factors on Air Quality in Greater Bangkok, Thailand

Authors: Parichat Wetchayont
Journal: Advances in Meteorology
 (2021)

---

## Abstract

With the outbreak of the COVID-19 pandemic around the world, many countries announced lockdown measures, including Thailand. Several scientific studies have reported on improvements in air quality due to the impact of these COVID-19 lockdowns. This study aims to investigate the effects of the COVID-19 lockdown and its driving influencing factors on air pollution in Greater Bangkok, Thailand, using in situ measurements. Overall, PM2.5, PM10, O3, and CO concentrations presented a significant decreasing trend during the COVID-19 outbreak year based on three periods: the Before Lockdown, Lockdown, and After Lockdown periods, for PM2.5: −0.7%, −15.8%, and −20.7%; PM10: −4.1%, −31.7%, and −6.1%; and O3: −0.3%, −7.1%, and −4.7%, respectively, compared to the same periods in 2019. CO concentrations, especially which had increased by 14.7% Before Lockdown, decreased by −8.0% and −23.6% during the Lockdown and After Lockdown periods, respectively. Meanwhile, SO2 increased by 54.0%, 41.5%, and 84.6%, and NO2 increased by 20.1%, 3.2%, and 26.6%, respectively, for the Before Lockdown, Lockdown, and After Lockdown periods. PCA indicated a significant combination effect of atmospheric mechanisms that were strongly linked to emission sources such as traffic and biomass burning. It has been demonstrated that the COVID-19 lockdown did pause some of these anthropogenic emissions, i.e., traffic and commercial and industrial activities, but not all of them. Even low traffic emissions, on their own, did not cause an absolute reduction in air pollution since there are several primary emission sources that dominate the air quality over Greater Bangkok. Finally, these findings highlight the impact of COVID-19 lockdown measures not only on air pollution levels but on their effects on air pollution characteristics, as well.


---

## Body

## 1. Introduction

The entire world has been battling with the coronavirus since the first case was reported on December 31, 2019, in Wuhan, China. Ultimately, the coronavirus was declared a pandemic by the World Health Organization (WHO) on March 11, 2020 [1] as COVID-19 spread. As of updated numbers, on December 28, 2020, there were 81,264,631 reported positive cases and 1,774,317 deaths worldwide, including Thailand [2]. Soon after COVID-19 was discovered, lockdown measures and social distancing started being used as a global pandemic action plan to prevent COVID-19 from spreading. In Thailand, government authorities announced COVID-19 prevention and control actions, including lockdown and curfew hours, for the whole country from March 26, 2020, to May 31, 2020. These COVID-19 lockdown measures decreased human activities, especially in the traffic, industrial, and energy production sectors, which assumes a corresponding decrease in anthropogenic emissions of air pollution. Generally, air quality is indicated by several pollutants such as surface ozone (O3) levels, emissions of NOx, CO, and SO2, and aerosol emissions (PM10 and PM2.5). Many research studies have reported on improvements in air quality due to the effects of COVID-19 lockdown measures [3–7]. For example, Xu et al. [8] indicated that effects of the COVID-19 outbreak presented positive feedback in reductions of average concentrations of atmospheric PM2.5 by −30.1%, PM10 by −40.5%, SO2 by −33.4%, CO by −27.9%, and NO2 by −61.4%, respectively, during February 2020 in Central China. Meanwhile, Southeast Asian cities such as Manila, Kuala Lumpur, and Singapore also reported decreasing trends of NO2 (−27% to −30%) and of PM10 (−26 to −31%), PM2.5 (−23 to −32%), NO2 (−63 to −64%), SO2 (−9 to −20%), and CO concentrations (−25 to −31%), respectively [9]. In addition, Nadzir et al. [3] found that, in Malaysia, CO dropped by −48.7%, but PM2.5 and PM10 increased by 60% and 9.7%, respectively, as their results indicated high AODs from Himawari-8 and NO2 concentrations from Aura-OMI satellite sensors. This was associated with massive biomass burning in northern Thailand and Laos during the Lockdown period (March 2020), which prevented exploration of the impact due to lockdown on air pollution in this region. Most of the research has been performed in the megacities, but Stratoulias and Nuthammachot [10] analyzed concentrations of air pollutants over a medium-sized city (in Songkhla Province) in Southern Thailand and found that concentrations of PM2.5 had changed by −21.8%, PM10 by −22.9%, NO2 by −33.7%, and O3 by −12.5% in the first 3 weeks of the lockdown compared to the respective prelockdown period. Kerimray et al. [11] presented the effects of the COVID-19 lockdown during traffic-free conditions in Kazakhstan, with a PM2.5 reduction of −21% and other gaseous pollutants down by −15% to −49%. Meanwhile, Filonchyk and Peterson [12] discovered that overall concentrations of air pollutants in Shanghai, China, were reduced during their lockdown period, though they were still higher than the World Health Organization (WHO) guidelines, indicating that there were other significant background sources. Zangari et al. [13] also presented impacts of the lockdown on PM2.5 and NO2 concentrations in New York City, indicating that they had decreased in the short term. However, using a linear time lag model, it indicated that there were no significant concentration changes in the long term. Moreover, Suhaimi et al. [14] suggested that NO2 and ambient temperature were the most significant air pollutant and meteorological factors during the COVID-19 outbreak in Kuala Lumpur.Recently, Bangkok has experienced winter pollution events with more frequency. Previous studies have mentioned that the most common sources of PM2.5 emissions in Bangkok are from biomass burning, traffic, and industrial activities, with varying concentrations caused by seasonal factors [15–17]. Moreover, Watcharavitoon et al. [18] presented spatial and temporal variation trends of gaseous air pollutant concentrations for O3, NOx, CO, and SO2 from 1996 to 2009 in Bangkok between residential and roadside areas. They reported seasonal trends of gaseous air pollutant concentrations which decreased from January to August and then increased from September to December. Gaseous air pollutant concentrations clearly presented higher concentration levels at the roadside areas than at the residential areas.Bangkok is a big city, with the 2020 population of the metropolitan area estimated at 10,539,415, with a high number of vehicles estimated at more than ten million (official accumulated number of registered vehicles) in 2020. When the people were largely restricted to their homes, there should have been greater reductions in vehicle emissions during the Lockdown period. And the same should have been true for the industrial sector. However, the COVID-19 lockdown’s impact on air quality in Bangkok is currently unknown. Therefore, this study aims to explore the effects and driving influencing factors of the COVID-19 lockdown measures on air quality in Greater Bangkok, Thailand, using in situ measurements with principal component analysis (PCA).


## 2. Materials and Methods

### 2.1. Study Area

Greater Bangkok refers to Bangkok, the capital, along with the surrounding provinces of Nakhon Pathom, Nonthaburi, Pathum Thani, Samut Prakan, and Samut Sakorn. Greater Bangkok covers an area of 7,762 km2 (100.20E to 100.9E, 13.0N to 14.0N) and is the center of economic development and an important industrial base for the surrounding provinces (Figure 1). Some industries in Samut Prakan, Samut Sakorn, and Pathum Thani have already become the main emission sources of atmospheric pollution from industry.Figure 1
Study area and the 23 PM2.5 automatic monitoring stations in Greater Bangkok, Thailand. The colored bar represents elevation above mean sea level in meters; roads are depicted as straight lines.


### 2.2. Ground-Based Air Pollution Monitoring, Traffic Index, and Fire Spots

Major air pollutants and aerosols including carbon monoxide (CO), ozone (O3), nitrogen dioxide (NO2), sulfur dioxide (SO2), and particulate matter with diameter lower than 10 μm (PM10) and 2.5 μm (PM2.5) concentration data were collected from the Pollution Control Department (PCD) of Thailand by observing 23 automatic monitoring sites [19]. The monitoring sites were almost all located in the Bangkok metropolitan area, as shown in Figure 1. Data were collected hourly from the period of January 1, 2019, to July 20, 2020, for both aerosols and gaseous pollutants. In addition, the traffic index refers as TI [20] for the same period, as the air pollutant dataset will be used to analyze the emission source from vehicles on the entire road network in Bangkok with a range of 0 to 10 (from free-flow to jam) to link air pollution with people movements. Moreover, in order to relate the emission source with biomass burning, active fire data from satellite observations by the Visible Infrared Imaging Radiometer Suite (VIIRS) were provided through NASA’s Fire Information for Resource Management System [21] at the same period as the air pollutants; in this study, it will be referred as the “Fire” factor.


### 2.3. Meteorological Dataset

It is not only emission sources that influence air quality, but meteorological factors also significantly impact the dilution and accumulation processes of pollutants emitted from local sources [22]. Therefore, to access the variations of air pollutants, meteorological factors must be examined. In this study, meteorological factors were obtained from the ECMWF’s fifth-generation Reanalysis (ERA5), the European Centre for Medium-Range Weather Forecasts [23]. The meteorological dataset contains total precipitation (TP), 2-meter air temperature (T2M), planetary boundary layer height (BLH), relative humidity (RH), surface pressure (SP), and wind speed (WS), which have a horizontal resolution of 0.25° × 0.25° at hourly temporal resolutions for the 2019–2020 period. The meteorological data were picked up at the same hour of the day as the sampling time for the air pollutants. Even though ERA5 data present insufficiency in representing the local meteorology at some monitoring sites, the data resolution seems to be applicable, as presented in the previous research for the impacts on meteorology by surface air pollution [24, 25].


### 2.4. Data Analysis Methods

Variations of air quality regarding the COVID-19 outbreak were investigated for three different periods, Before Lockdown (from January 1 to March 25), Lockdown (March 26 to May 31), and After Lockdown (June 1 to July 31). To evaluate the impact of COVID-19, the data of the year 2020 were compared to data of the year 2019 at the same period, with the data of the year 2019 being used as the baseline. Changes in the air pollutant levels were evaluated by comparing those 3 different periods in the year 2020 with 2019 at the same time (expressed in %) between the Before Lockdown, Lockdown, and After Lockdown periods. In order to access the influences between meteorological factors, the air pollutants and other accompanying parameters gave different responses between the three periods associated with the COVID-19 lockdown. We performed data analysis using a principal component analysis (PCA), which is a statistical multivariate analysis for data that features a large variable set. This method enables the researcher to identify correlations and patterns in a dataset by transforming them into a new smaller set of uncorrelated variables, namely, principal components (PCs), which still contain most of the information as the large set [26]. Therefore, by applying a PCA method to air pollutant concentrations and meteorological variables, a dataset could be obtained with the most significant variables, which could indicate the source of the pollutants and largely explain the variations in the air pollution [27]. In this study, the meteorological variables of T2M, SP, TP, RH, WS, and BLH; the major air pollutants: PM10, PM2.5, NO2, SO2, CO, and O3 concentrations; and the anthropogenic activities, TI and Fire, were taken up for analysis. The PCs created by PCA were rotated using an orthogonal rotation method (Varimax) to compute the explained variance matrix. The numbered PCs were selected according to an eigenvalue greater than or equal to 1. These PCs are a linear combination of the explanatory variables; therefore, Pearson correlation tests were used to determine the correlation between the PCs and the original variables as a loading factor. Significant variables were identified when the correlation value was greater than or equal to 0.3.


## 2.1. Study Area

Greater Bangkok refers to Bangkok, the capital, along with the surrounding provinces of Nakhon Pathom, Nonthaburi, Pathum Thani, Samut Prakan, and Samut Sakorn. Greater Bangkok covers an area of 7,762 km2 (100.20E to 100.9E, 13.0N to 14.0N) and is the center of economic development and an important industrial base for the surrounding provinces (Figure 1). Some industries in Samut Prakan, Samut Sakorn, and Pathum Thani have already become the main emission sources of atmospheric pollution from industry.Figure 1
Study area and the 23 PM2.5 automatic monitoring stations in Greater Bangkok, Thailand. The colored bar represents elevation above mean sea level in meters; roads are depicted as straight lines.


## 2.2. Ground-Based Air Pollution Monitoring, Traffic Index, and Fire Spots

Major air pollutants and aerosols including carbon monoxide (CO), ozone (O3), nitrogen dioxide (NO2), sulfur dioxide (SO2), and particulate matter with diameter lower than 10 μm (PM10) and 2.5 μm (PM2.5) concentration data were collected from the Pollution Control Department (PCD) of Thailand by observing 23 automatic monitoring sites [19]. The monitoring sites were almost all located in the Bangkok metropolitan area, as shown in Figure 1. Data were collected hourly from the period of January 1, 2019, to July 20, 2020, for both aerosols and gaseous pollutants. In addition, the traffic index refers as TI [20] for the same period, as the air pollutant dataset will be used to analyze the emission source from vehicles on the entire road network in Bangkok with a range of 0 to 10 (from free-flow to jam) to link air pollution with people movements. Moreover, in order to relate the emission source with biomass burning, active fire data from satellite observations by the Visible Infrared Imaging Radiometer Suite (VIIRS) were provided through NASA’s Fire Information for Resource Management System [21] at the same period as the air pollutants; in this study, it will be referred as the “Fire” factor.


## 2.3. Meteorological Dataset

It is not only emission sources that influence air quality, but meteorological factors also significantly impact the dilution and accumulation processes of pollutants emitted from local sources [22]. Therefore, to access the variations of air pollutants, meteorological factors must be examined. In this study, meteorological factors were obtained from the ECMWF’s fifth-generation Reanalysis (ERA5), the European Centre for Medium-Range Weather Forecasts [23]. The meteorological dataset contains total precipitation (TP), 2-meter air temperature (T2M), planetary boundary layer height (BLH), relative humidity (RH), surface pressure (SP), and wind speed (WS), which have a horizontal resolution of 0.25° × 0.25° at hourly temporal resolutions for the 2019–2020 period. The meteorological data were picked up at the same hour of the day as the sampling time for the air pollutants. Even though ERA5 data present insufficiency in representing the local meteorology at some monitoring sites, the data resolution seems to be applicable, as presented in the previous research for the impacts on meteorology by surface air pollution [24, 25].


## 2.4. Data Analysis Methods

Variations of air quality regarding the COVID-19 outbreak were investigated for three different periods, Before Lockdown (from January 1 to March 25), Lockdown (March 26 to May 31), and After Lockdown (June 1 to July 31). To evaluate the impact of COVID-19, the data of the year 2020 were compared to data of the year 2019 at the same period, with the data of the year 2019 being used as the baseline. Changes in the air pollutant levels were evaluated by comparing those 3 different periods in the year 2020 with 2019 at the same time (expressed in %) between the Before Lockdown, Lockdown, and After Lockdown periods. In order to access the influences between meteorological factors, the air pollutants and other accompanying parameters gave different responses between the three periods associated with the COVID-19 lockdown. We performed data analysis using a principal component analysis (PCA), which is a statistical multivariate analysis for data that features a large variable set. This method enables the researcher to identify correlations and patterns in a dataset by transforming them into a new smaller set of uncorrelated variables, namely, principal components (PCs), which still contain most of the information as the large set [26]. Therefore, by applying a PCA method to air pollutant concentrations and meteorological variables, a dataset could be obtained with the most significant variables, which could indicate the source of the pollutants and largely explain the variations in the air pollution [27]. In this study, the meteorological variables of T2M, SP, TP, RH, WS, and BLH; the major air pollutants: PM10, PM2.5, NO2, SO2, CO, and O3 concentrations; and the anthropogenic activities, TI and Fire, were taken up for analysis. The PCs created by PCA were rotated using an orthogonal rotation method (Varimax) to compute the explained variance matrix. The numbered PCs were selected according to an eigenvalue greater than or equal to 1. These PCs are a linear combination of the explanatory variables; therefore, Pearson correlation tests were used to determine the correlation between the PCs and the original variables as a loading factor. Significant variables were identified when the correlation value was greater than or equal to 0.3.


## 3. Results and Discussion

### 3.1. The Influence of COVID-19 Lockdown on Variations of Air Quality over Greater Bangkok

Figure2 presents a time series of the rolling 24-hour average of daily PM2.5 concentration variations on a daily scale for 23 measurement stations for the periods from March 1 to July 31 of 2019 and 2020 in Greater Bangkok, Thailand. The grey color represents the Lockdown period from March 26, 2020, to May 31, 2020. The concentrations of PM2.5, PM10, NO2, O3, SO2, and CO were compared between the 3 different periods: Before Lockdown (January 1–March 1), Lockdown (March 26–May 31), and After Lockdown (June 1–July 31). There were similarly significant seasonal variations in the PM2.5, PM10, NO2, O3, and CO concentrations, where the highest mean concentrations occurred in January during the Before Lockdown period for Greater Bangkok, then exhibited decreasing concentrations during the Lockdown and After Lockdown periods. While SO2 concentrations show a highly fluctuating time series throughout the year, especially in 2020, there were higher concentration levels and more fluctuation by degree than in 2019. As illustrated in Figure 3, changes in the mean concentration values of six major pollutants during the COVID-19 outbreak reveal that there were no substantial decreases in PM2.5 (−0.7%), PM10 (−4.1%), and O3 (−0.3%) concentrations during the Before Lockdown period with the previous year. But there were changes in SO2 (54.0%), NO2 (20.1%), and CO (14.7%) concentrations during the Before Lockdown period. Meanwhile, there were reductions in concentrations of PM2.5 (equaling −15.8%), PM10 (−31.7%), CO (−8.0%), and O3 (−7.1%) during the Lockdown period, and PM2.5 (by −20.7%), PM10 (−6.1%), CO (−23.6%), and O3 (−4.7%) during the After Lockdown period, when compared to the previous year. Stratoulias and Nuthammachot [10] similarly reported a decreasing range in PM2.5 and PM10 concentrations during the Lockdown period. On the other hand, NO2 and SO2 concentrations increased in this study during the Lockdown (3.2% and 41.5%) and in the After Lockdown period (26.6% and 84.6%) in 2019 and 2020, respectively. In contrast, Kanniah et al. [9] and Stratoulias and Nuthammachot [10] found that there were decreased concentrations of NO2, according to the Aura satellite in Malaysia and Southern Thailand. Generally, average concentrations of PM2.5, PM10, NO2, O3, and CO exhibit a decreasing trend from March to August [18], even in the previous years before the COVID-19 outbreak, as shown in Figure 2, except for SO2. Seasonal variations (summer and rainy seasons), denoted by rising temperatures and more frequent rains, caused decreasing air pollutant concentrations, excluding some periods when the air pollutant concentrations showed several peaks association with open biomass burning and traffic index peaks due to added anthropogenic pollutants during the harvest season [28] and road traffic congestion in Bangkok [29].Figure 2
Rolling 24-hour average of hourly air pollutant concentration variations of major air pollutants over 23 ground-based stations in Greater Bangkok for the years 2019 and 2020. Grey color highlights the Lockdown period from March 26, 2020, to May 31, 2020. (a) PM2.5. (b) PM10. (c) NO2. (d) O3. (e) SO2. (f) CO.
(a)(b)(c)(d)(e)(f)Figure 3
Impact of the COVID-19 lockdown on mean concentrations of air pollution: PM10, PM2.5, O3, NO2, SO2, and CO, at 23 ground-based measurements during the Before Lockdown, Lockdown, and After Lockdown periods in Bangkok, Thailand.In principle, air pollutant concentrations in the atmosphere fluctuate because of complex factors such as emission sources (TI and Fire) and meteorological factors (BLH, T2M, TP, WS, and RH) [30]. Anthropogenic sources and meteorological changes during the COVID-19 outbreak period were examined by comparing them with previous years, as shown in Table 1. During the Before Lockdown period, increases were seen in TI (4%), Fire (26%), WS (22%), and RH (14%), whereas there were decreases in BLH (−42%), TP (−99%), and T2M (−5%). Increased TI and Fire conditions in 2020 may have caused higher NO2, SO2, and CO concentrations than in 2019 at the same time. During the first weeks of lockdown, beginning in 2020, there was a sharp decrease in the TI due to limited transportation in Greater Bangkok; after that, the concentrations increased gradually until the end of June (Figure 4(a)). A similar trend was observed for NO2 (Figure 2(c)). As well, Fire (counts per day) within a 240 km radius of Bangkok city (Figure 4(b)) shows a high number in the first week of the Lockdown period. News reports indicate that there were great wildfires in northern Thailand at that time, which produced tons of aerosols and pollutants [31]. The hourly meteorological data of Greater Bangkok during the study period in 2019 were compared to those in 2020, and the results are shown in Table 1. As indicated in Figures 4(c)–4(h), there was no obvious change during the COVID-19 outbreak in terms of SP, T2M, WS, BLH, and TP from January to March 2020 compared with previous years. Whereas SP and RH during the Lockdown period were somehow higher than previous years, T2M and BLH were lower than those in previous years. As shown during the After Lockdown period, RH was higher, while BLH, TP, WS, and T2M were lower compared to previous years. According to the higher influence of long-range transported air masses in 2020 than in 2019, air pollutant levels over Greater Bangkok were affected not only by localization but also by the transport direction of air mass movements, as well. There were different predominant winds between the years 2019 and 2020. During the Lockdown period in 2019, the predominant winds were from the southwest part of Bangkok, which is a highly polluted area. Those predominant winds shifted to the south during the same time period in 2020, which brought a clean air mass from the Gulf of Thailand into Greater Bangkok, resulting in a decrease in air pollutant concentrations, even if it did not have formal lockdown measures. It should be noted that wind direction is a factor determining air pollutant levels.Table 1
Statistical description of meteorological factors; mean and standard deviation (SD) values in 2019 and 2020 over Greater Bangkok.
Before Lockdown 2019Before Lockdown 2020MeanSDMeanSDTI3.661.793.790.40Fire (counts/day)389.77338.04492.06303.68SP (mbar)1011.862.251012.111.90BLH (m)511.71428.72295.21160.70TP (mm)0.030.180.000.01WS (m/s)13.7511.5216.8111.30RH (%)72.7216.4482.8410.14T2M (°C)28.222.9226.931.07Lockdown 2019Lockdown 2020TI3.931.933.100.38Fire (counts/day)80.6881.87164.55326.44SP (mbar)1007.662.331009.691.73BLH (m)615.80371.17393.45130.12TP (mm)0.110.360.040.21WS (m/s)14.7711.3318.6411.30RH (%)72.3013.7583.483.70T2M (°C)30.812.5028.991.02After Lockdown 2019After Lockdown 2020TI4.291.943.820.63Fire (counts/day)8.728.657.847.60SP (mbar)1006.721.541007.132.73BLH (m)584.75350.74301.21125.16TP (mm)0.220.580.100.21WS (m/s)12.7410.708.665.67RH (%)76.8111.2585.305.29T2M (°C)29.952.1627.940.89Figure 4
Temporal variations of the traffic index (a), Fire spot count (b), surface pressure (c), air temperature at 2 meters (d), relative humidity (e), wind speed (f), boundary layer height (g), and total precipitation (h). Grey color highlights the Lockdown period from March 26, 2020, to May 31, 2020. Influence factors driving the improvements in air quality.
(a)(b)(c)(d)(e)(f)(g)(h)It is evident that the lockdown corresponding to COVID-19 has had an effect on average pollutant concentrations because of human activity restrictions since the lockdown measure began on March 26, 2020, in Greater Bangkok. Moreover, higher WS in 2020 could have helped to dilute the pollutant concentrations in the air [32]. In contrast, Kerimray et al. [11] reported no significant change in average PM2.5 concentrations during the COVID-19 lockdown when compared with previous years in Almaty, Kazakhstan. This is possibly because that they had a shorter period of lockdown (March 19, 2020–April 14, 2020) than in Bangkok; thus, the impact of COVID-19 cannot be compared well to Almaty. In addition, it was during the seasonal transition from summer to rainy seasons in Almaty, and PM2.5 concentrations may have been highly influenced by meteorological factors. In the After Lockdown period, there were decreases in both the source and meteorological variables, except for RH, which increased compared with the previous year. In addition, many studies report that O3 concentrations had increasing trends [33–35], while in this study we found decreasing O3 concentrations over Greater Bangkok. NO2 is an oxidation product from nitrogen oxides (NOx) and O3, which is emitted from combustion sources such as vehicle exhaust, industry, power plants, and residential heating [17]. Thus, this decrease in O3 could be due to greater increases in NO2 concentrations. It is noted that ship traffic along the main river in Bangkok, the Chao Phraya River, is an important logistic hub in Greater Bangkok and a significant emission source of NO2 concentrations. The ship traffic was reduced due to the lockdown too, so this also contributed to the reduction of O3 concentrations.Furthermore, different degrees of reduction in the pollutant concentrations point out that the decreasing pollution levels in three different periods cannot be explained by limited emissions only but depend on meteorological conditions too. To obtain the influence factors driving air quality improvements between expected emission sources, meteorological variables, and these six pollutants during the COVID-19 outbreak, this study used PCA to investigate in more detail, as shown in the following sections.


### 3.2. Influence Factors Driving the Improvements in Air Quality

In order to clarify what the main influence is between expected emission sources, meteorological parameters and the six pollutants during the COVID-19 outbreak will be explored in this section. To obtain a better understanding and interpretation of the data, the principal components (PCs) were subjected to a Varimax rotation matrix. Only components with an eigenvalue greater than 1 were determined as principal components (grey color), as shown in Table2. There are five major PCs in each subset period, comprising PC1, PC2, PC3, PC4, and PC5. The percentage of total variance represents how much the proportion of that PC explains the variation in air quality. In each period of the same year, the percentage of the total variance was slightly different. However, it had some significant differences between the Before Lockdown and the Lockdown periods. To obtain the factor loading, a Varimax rotation with Kaiser normalization (Figure 5) was computed, and a loading factor higher than 0.3 contained from the output becomes a principal component (PC). The results of PCA are summarized in Figure 5, presenting significant PC contributions. A loading factor of more than 0.70 is considered strong, a range of 0.50–0.69 is considered moderate, and a range of 0.31–0.49 is considered weak.Table 2
Total variance explaining the principal components of air pollutants and meteorological elements in 2019 and 2020 over Greater Bangkok.
2019BeforeLockdownAfterComponentEigen valueVariance (%)Cumulative (%)Eigen valueVariance (%)Cumulative (%)Eigen valueVariance (%)Cumulative (%)13.8427.4027.403.5025.0025.003.5825.6025.6022.5518.2045.602.3216.6041.602.2115.8041.4031.228.7054.401.349.5051.101.4410.3051.6041.087.7062.101.289.1060.301.349.5061.2051.027.3069.301.148.1068.401.168.3069.4060.835.9075.300.987.0075.400.876.2075.7070.825.8081.100.775.5080.800.846.0081.7080.664.7085.800.644.6085.400.574.1085.7090.614.4090.100.584.2089.600.533.8089.50100.453.2093.400.463.3092.800.453.2092.702020BeforeLockdownAfterComponentEigen valueVariance (%)Cumulative (%)Eigen valueVariance (%)Cumulative (%)Eigen valueVariance (%)Cumulative (%)15.1536.7036.703.5825.5025.503.2523.0023.0021.6711.9048.602.2015.7041.202.4317.2040.2031.228.7057.301.8413.1054.201.6811.9052.1041.097.8065.101.6111.5065.701.6211.5063.6050.966.8071.900.997.0072.801.158.1071.7060.896.4078.300.856.1078.800.876.1077.9070.866.1084.400.745.3084.100.805.7083.6080.604.3088.700.574.1088.200.614.3087.9090.483.5092.200.473.3091.500.523.7091.60100.433.1095.300.412.9094.400.423.0094.50Figure 5
Loading factors of 14 companies in 5 principal components and their estimated comprehensive eigenvalues. The colored bar represents the level of loading value and numeric shows the component loadings between each meteorological factor and a principal component. (a) Before Lockdown 2019. (b) Lockdown 2019. (c) After Lockdown 2019. (d) Before Lockdown 2020. (e) Lockdown 2020. (f) After Lockdown 2020.
(a)(b)(c)(d)(e)(f)During the Before Lockdown period, which denotes the winter season in Thailand, the PC1 and the PC2 could explain the variance by 27.4% and 18.2% for 2019 and by 36.7% and 11.9% for 2020, respectively. The results reveal some similarities between these two years, and there were significant mechanisms associated with air quality. PM10, NO2, and CO are dominant pollutant parameters that associate with the particular atmospheric mechanism of low T2M, BLH, and WS and high SP and RH. Hence, these atmospheric mechanisms reduce the ability of the pollutants to disperse from their sources [36]. These pollutants relating to unknown emissions, such as major and traffic-originated emissions, were minor sources in 2019, while in 2020, the major and minor pollutants were related to biomass burning and unknown emission sources, respectively. These results supporting the comparison of concentrations for PM2.5, PM10, and O3 in Section 3.1 between the two years are not significantly different. As mentioned before, the common sources of air pollution in Greater Bangkok are from biomass burning, traffic, and industrial activities, with varying concentrations due to seasonal factors [15–17]. Due to some limitations, emission-related data for the industrial sector were not available for this study. Thus, the unknown emission source might be from industrial or other sources. Moreover, the PC2 in 2019 shows moderate positive contributions of O3 and T2M, which indicates a strong oxidative air condition producing the formation of secondary particles, which could result in a positive loading factor of PM2.5 and O3. As well, in 2020, the PC2 exhibits moderate positive contributions of T2M but negative contributions of O3. This was mainly affected by photochemical reaction. The reaction system can produce NO2 (positive contribution) due to the reaction of NO with O3 [37]. Additionally, a comparison of the PC1 also explains the increase of NO2 and CO regarding higher positive contribution magnitudes in 2020 than those in 2019. As well, the PC5 had a higher contribution magnitude for SO2 in 2020 than in 2019, resulting in increased SO2 (Section 3.1).During the Lockdown period, which denotes the summer season in Thailand, there were significantly different major pollutant parameters contributing to the PC1 (25.0% and 25.5%) and PC2 (16.6% and 15.7%) for 2019 and 2020, respectively. In 2019, O3 contributed as a major pollutant (PC1) corresponding to photochemical reaction (NO2 + O2 ⟶ NO + O3), as seen in the strong contribution of T2M with the significant emission source of TI. This explains the correlations with temperature and, partly, with O3 concentrations that are commonly higher in summer [15]. PM2.5, PM10, NO2, SO2, and CO are minor pollutants (PC2) which relate to unknown emission sources, with the exception of SO2 and CO, which are associated with biomass burning (the PC4). Vice versa in 2020, the increases in PM2.5, PM10, NO2, and CO concentrations originated from unknown emission sources (PC1), accompanied by strong contributions from decreases in BLH, T2M, and WS. Meanwhile, the moderately negative O3 was related to chemical reaction (NO + O3 ⟶ NO2 + O2), becoming a minor mechanism (PC2) corresponding to the NO added from traffic (TI) and biomass burning (Fire) emissions. These results indicate some important evidence that explains the reduction of air pollutant concentrations in Section 3.1. With COVID-19 lockdown measures, people were largely restricted to their homes, and Greater Bangkok, with its high numbers of vehicles, should have had greater reductions in traffic emissions during the Lockdown period. Decreases in PM2.5, PM10, and CO concentrations in 2020 strongly contributed to the increased Fire (PC1) and the decreased TI (PC2), suggesting that changes in traffic emissions were more responsible for the improvements in air quality during the Lockdown period, especially fine particles, than biomass burning. On the other hand, increases in NO2 concentrations in 2020 (PC2) were significantly related to biomass burning. During the Lockdown period (March 2020), there were massive forest fires in northern Thailand, which reduced the impact of the lockdown on air pollution in that region. A report found an increase in some pollutants during the Lockdown period regarding forest fires in Malaysia [3, 10]. In addition, increased SO2 concentrations were associated with unknown emission sources, which were probably emitted from the industrial sector.During the After Lockdown period, which denotes the rainy season in Thailand, the PC1 and the PC2 could explain the variance by 25.6% and 15.8% for 2019 and 23.0% and 17.2% for 2020, respectively. In 2019, there were similar contributions of air pollutants with the Lockdown period in 2020, as seen with increases in O3 concentrations by the production of photochemical reactions being the major mechanism (PC1). Increased PM2.5, PM10, NO2, SO2, and CO concentrations were minor mechanisms (PC2). In 2020, PM2.5, PM10, NO2, SO2, and CO were major pollutants that originated from unknown sources, with the exception of the PC3, where SO2 concentrations were weakly associated with biomass burning. It can be noted that there were decreases in BLH, WS, and T2M, which are accumulative atmospheric conditions. Interestingly, there were significant decreases in both TI and Fire, while all pollutants except O3 concentrations had increasing trends. However, as the results in Section 3.1 explain, concentrations of PM2.5, PM10, and CO were still decreased to a lower degree during the After Lockdown period. Therefore, the results demonstrate that the improvement of air quality in Greater Bangkok after the easing of lockdown was a combined effect of other emission sources (industrial, household, etc.) and atmospheric mechanisms.All PCs during the lockdown of 2020 comprise important evidence that indicates the influence factors driving the improvement of air quality that were affected by the COVID-19 lockdown in Greater Bangkok. Atmospheric mechanisms play an important role in diluting or accumulating pollutant concentrations, while the emission sources influence the concentrations and type of major pollutants. Therefore, the COVID-19 lockdown measures influenced not only the air pollution levels but also affected the air pollution characteristics.


## 3.1. The Influence of COVID-19 Lockdown on Variations of Air Quality over Greater Bangkok

Figure2 presents a time series of the rolling 24-hour average of daily PM2.5 concentration variations on a daily scale for 23 measurement stations for the periods from March 1 to July 31 of 2019 and 2020 in Greater Bangkok, Thailand. The grey color represents the Lockdown period from March 26, 2020, to May 31, 2020. The concentrations of PM2.5, PM10, NO2, O3, SO2, and CO were compared between the 3 different periods: Before Lockdown (January 1–March 1), Lockdown (March 26–May 31), and After Lockdown (June 1–July 31). There were similarly significant seasonal variations in the PM2.5, PM10, NO2, O3, and CO concentrations, where the highest mean concentrations occurred in January during the Before Lockdown period for Greater Bangkok, then exhibited decreasing concentrations during the Lockdown and After Lockdown periods. While SO2 concentrations show a highly fluctuating time series throughout the year, especially in 2020, there were higher concentration levels and more fluctuation by degree than in 2019. As illustrated in Figure 3, changes in the mean concentration values of six major pollutants during the COVID-19 outbreak reveal that there were no substantial decreases in PM2.5 (−0.7%), PM10 (−4.1%), and O3 (−0.3%) concentrations during the Before Lockdown period with the previous year. But there were changes in SO2 (54.0%), NO2 (20.1%), and CO (14.7%) concentrations during the Before Lockdown period. Meanwhile, there were reductions in concentrations of PM2.5 (equaling −15.8%), PM10 (−31.7%), CO (−8.0%), and O3 (−7.1%) during the Lockdown period, and PM2.5 (by −20.7%), PM10 (−6.1%), CO (−23.6%), and O3 (−4.7%) during the After Lockdown period, when compared to the previous year. Stratoulias and Nuthammachot [10] similarly reported a decreasing range in PM2.5 and PM10 concentrations during the Lockdown period. On the other hand, NO2 and SO2 concentrations increased in this study during the Lockdown (3.2% and 41.5%) and in the After Lockdown period (26.6% and 84.6%) in 2019 and 2020, respectively. In contrast, Kanniah et al. [9] and Stratoulias and Nuthammachot [10] found that there were decreased concentrations of NO2, according to the Aura satellite in Malaysia and Southern Thailand. Generally, average concentrations of PM2.5, PM10, NO2, O3, and CO exhibit a decreasing trend from March to August [18], even in the previous years before the COVID-19 outbreak, as shown in Figure 2, except for SO2. Seasonal variations (summer and rainy seasons), denoted by rising temperatures and more frequent rains, caused decreasing air pollutant concentrations, excluding some periods when the air pollutant concentrations showed several peaks association with open biomass burning and traffic index peaks due to added anthropogenic pollutants during the harvest season [28] and road traffic congestion in Bangkok [29].Figure 2
Rolling 24-hour average of hourly air pollutant concentration variations of major air pollutants over 23 ground-based stations in Greater Bangkok for the years 2019 and 2020. Grey color highlights the Lockdown period from March 26, 2020, to May 31, 2020. (a) PM2.5. (b) PM10. (c) NO2. (d) O3. (e) SO2. (f) CO.
(a)(b)(c)(d)(e)(f)Figure 3
Impact of the COVID-19 lockdown on mean concentrations of air pollution: PM10, PM2.5, O3, NO2, SO2, and CO, at 23 ground-based measurements during the Before Lockdown, Lockdown, and After Lockdown periods in Bangkok, Thailand.In principle, air pollutant concentrations in the atmosphere fluctuate because of complex factors such as emission sources (TI and Fire) and meteorological factors (BLH, T2M, TP, WS, and RH) [30]. Anthropogenic sources and meteorological changes during the COVID-19 outbreak period were examined by comparing them with previous years, as shown in Table 1. During the Before Lockdown period, increases were seen in TI (4%), Fire (26%), WS (22%), and RH (14%), whereas there were decreases in BLH (−42%), TP (−99%), and T2M (−5%). Increased TI and Fire conditions in 2020 may have caused higher NO2, SO2, and CO concentrations than in 2019 at the same time. During the first weeks of lockdown, beginning in 2020, there was a sharp decrease in the TI due to limited transportation in Greater Bangkok; after that, the concentrations increased gradually until the end of June (Figure 4(a)). A similar trend was observed for NO2 (Figure 2(c)). As well, Fire (counts per day) within a 240 km radius of Bangkok city (Figure 4(b)) shows a high number in the first week of the Lockdown period. News reports indicate that there were great wildfires in northern Thailand at that time, which produced tons of aerosols and pollutants [31]. The hourly meteorological data of Greater Bangkok during the study period in 2019 were compared to those in 2020, and the results are shown in Table 1. As indicated in Figures 4(c)–4(h), there was no obvious change during the COVID-19 outbreak in terms of SP, T2M, WS, BLH, and TP from January to March 2020 compared with previous years. Whereas SP and RH during the Lockdown period were somehow higher than previous years, T2M and BLH were lower than those in previous years. As shown during the After Lockdown period, RH was higher, while BLH, TP, WS, and T2M were lower compared to previous years. According to the higher influence of long-range transported air masses in 2020 than in 2019, air pollutant levels over Greater Bangkok were affected not only by localization but also by the transport direction of air mass movements, as well. There were different predominant winds between the years 2019 and 2020. During the Lockdown period in 2019, the predominant winds were from the southwest part of Bangkok, which is a highly polluted area. Those predominant winds shifted to the south during the same time period in 2020, which brought a clean air mass from the Gulf of Thailand into Greater Bangkok, resulting in a decrease in air pollutant concentrations, even if it did not have formal lockdown measures. It should be noted that wind direction is a factor determining air pollutant levels.Table 1
Statistical description of meteorological factors; mean and standard deviation (SD) values in 2019 and 2020 over Greater Bangkok.
Before Lockdown 2019Before Lockdown 2020MeanSDMeanSDTI3.661.793.790.40Fire (counts/day)389.77338.04492.06303.68SP (mbar)1011.862.251012.111.90BLH (m)511.71428.72295.21160.70TP (mm)0.030.180.000.01WS (m/s)13.7511.5216.8111.30RH (%)72.7216.4482.8410.14T2M (°C)28.222.9226.931.07Lockdown 2019Lockdown 2020TI3.931.933.100.38Fire (counts/day)80.6881.87164.55326.44SP (mbar)1007.662.331009.691.73BLH (m)615.80371.17393.45130.12TP (mm)0.110.360.040.21WS (m/s)14.7711.3318.6411.30RH (%)72.3013.7583.483.70T2M (°C)30.812.5028.991.02After Lockdown 2019After Lockdown 2020TI4.291.943.820.63Fire (counts/day)8.728.657.847.60SP (mbar)1006.721.541007.132.73BLH (m)584.75350.74301.21125.16TP (mm)0.220.580.100.21WS (m/s)12.7410.708.665.67RH (%)76.8111.2585.305.29T2M (°C)29.952.1627.940.89Figure 4
Temporal variations of the traffic index (a), Fire spot count (b), surface pressure (c), air temperature at 2 meters (d), relative humidity (e), wind speed (f), boundary layer height (g), and total precipitation (h). Grey color highlights the Lockdown period from March 26, 2020, to May 31, 2020. Influence factors driving the improvements in air quality.
(a)(b)(c)(d)(e)(f)(g)(h)It is evident that the lockdown corresponding to COVID-19 has had an effect on average pollutant concentrations because of human activity restrictions since the lockdown measure began on March 26, 2020, in Greater Bangkok. Moreover, higher WS in 2020 could have helped to dilute the pollutant concentrations in the air [32]. In contrast, Kerimray et al. [11] reported no significant change in average PM2.5 concentrations during the COVID-19 lockdown when compared with previous years in Almaty, Kazakhstan. This is possibly because that they had a shorter period of lockdown (March 19, 2020–April 14, 2020) than in Bangkok; thus, the impact of COVID-19 cannot be compared well to Almaty. In addition, it was during the seasonal transition from summer to rainy seasons in Almaty, and PM2.5 concentrations may have been highly influenced by meteorological factors. In the After Lockdown period, there were decreases in both the source and meteorological variables, except for RH, which increased compared with the previous year. In addition, many studies report that O3 concentrations had increasing trends [33–35], while in this study we found decreasing O3 concentrations over Greater Bangkok. NO2 is an oxidation product from nitrogen oxides (NOx) and O3, which is emitted from combustion sources such as vehicle exhaust, industry, power plants, and residential heating [17]. Thus, this decrease in O3 could be due to greater increases in NO2 concentrations. It is noted that ship traffic along the main river in Bangkok, the Chao Phraya River, is an important logistic hub in Greater Bangkok and a significant emission source of NO2 concentrations. The ship traffic was reduced due to the lockdown too, so this also contributed to the reduction of O3 concentrations.Furthermore, different degrees of reduction in the pollutant concentrations point out that the decreasing pollution levels in three different periods cannot be explained by limited emissions only but depend on meteorological conditions too. To obtain the influence factors driving air quality improvements between expected emission sources, meteorological variables, and these six pollutants during the COVID-19 outbreak, this study used PCA to investigate in more detail, as shown in the following sections.


## 3.2. Influence Factors Driving the Improvements in Air Quality

In order to clarify what the main influence is between expected emission sources, meteorological parameters and the six pollutants during the COVID-19 outbreak will be explored in this section. To obtain a better understanding and interpretation of the data, the principal components (PCs) were subjected to a Varimax rotation matrix. Only components with an eigenvalue greater than 1 were determined as principal components (grey color), as shown in Table2. There are five major PCs in each subset period, comprising PC1, PC2, PC3, PC4, and PC5. The percentage of total variance represents how much the proportion of that PC explains the variation in air quality. In each period of the same year, the percentage of the total variance was slightly different. However, it had some significant differences between the Before Lockdown and the Lockdown periods. To obtain the factor loading, a Varimax rotation with Kaiser normalization (Figure 5) was computed, and a loading factor higher than 0.3 contained from the output becomes a principal component (PC). The results of PCA are summarized in Figure 5, presenting significant PC contributions. A loading factor of more than 0.70 is considered strong, a range of 0.50–0.69 is considered moderate, and a range of 0.31–0.49 is considered weak.Table 2
Total variance explaining the principal components of air pollutants and meteorological elements in 2019 and 2020 over Greater Bangkok.
2019BeforeLockdownAfterComponentEigen valueVariance (%)Cumulative (%)Eigen valueVariance (%)Cumulative (%)Eigen valueVariance (%)Cumulative (%)13.8427.4027.403.5025.0025.003.5825.6025.6022.5518.2045.602.3216.6041.602.2115.8041.4031.228.7054.401.349.5051.101.4410.3051.6041.087.7062.101.289.1060.301.349.5061.2051.027.3069.301.148.1068.401.168.3069.4060.835.9075.300.987.0075.400.876.2075.7070.825.8081.100.775.5080.800.846.0081.7080.664.7085.800.644.6085.400.574.1085.7090.614.4090.100.584.2089.600.533.8089.50100.453.2093.400.463.3092.800.453.2092.702020BeforeLockdownAfterComponentEigen valueVariance (%)Cumulative (%)Eigen valueVariance (%)Cumulative (%)Eigen valueVariance (%)Cumulative (%)15.1536.7036.703.5825.5025.503.2523.0023.0021.6711.9048.602.2015.7041.202.4317.2040.2031.228.7057.301.8413.1054.201.6811.9052.1041.097.8065.101.6111.5065.701.6211.5063.6050.966.8071.900.997.0072.801.158.1071.7060.896.4078.300.856.1078.800.876.1077.9070.866.1084.400.745.3084.100.805.7083.6080.604.3088.700.574.1088.200.614.3087.9090.483.5092.200.473.3091.500.523.7091.60100.433.1095.300.412.9094.400.423.0094.50Figure 5
Loading factors of 14 companies in 5 principal components and their estimated comprehensive eigenvalues. The colored bar represents the level of loading value and numeric shows the component loadings between each meteorological factor and a principal component. (a) Before Lockdown 2019. (b) Lockdown 2019. (c) After Lockdown 2019. (d) Before Lockdown 2020. (e) Lockdown 2020. (f) After Lockdown 2020.
(a)(b)(c)(d)(e)(f)During the Before Lockdown period, which denotes the winter season in Thailand, the PC1 and the PC2 could explain the variance by 27.4% and 18.2% for 2019 and by 36.7% and 11.9% for 2020, respectively. The results reveal some similarities between these two years, and there were significant mechanisms associated with air quality. PM10, NO2, and CO are dominant pollutant parameters that associate with the particular atmospheric mechanism of low T2M, BLH, and WS and high SP and RH. Hence, these atmospheric mechanisms reduce the ability of the pollutants to disperse from their sources [36]. These pollutants relating to unknown emissions, such as major and traffic-originated emissions, were minor sources in 2019, while in 2020, the major and minor pollutants were related to biomass burning and unknown emission sources, respectively. These results supporting the comparison of concentrations for PM2.5, PM10, and O3 in Section 3.1 between the two years are not significantly different. As mentioned before, the common sources of air pollution in Greater Bangkok are from biomass burning, traffic, and industrial activities, with varying concentrations due to seasonal factors [15–17]. Due to some limitations, emission-related data for the industrial sector were not available for this study. Thus, the unknown emission source might be from industrial or other sources. Moreover, the PC2 in 2019 shows moderate positive contributions of O3 and T2M, which indicates a strong oxidative air condition producing the formation of secondary particles, which could result in a positive loading factor of PM2.5 and O3. As well, in 2020, the PC2 exhibits moderate positive contributions of T2M but negative contributions of O3. This was mainly affected by photochemical reaction. The reaction system can produce NO2 (positive contribution) due to the reaction of NO with O3 [37]. Additionally, a comparison of the PC1 also explains the increase of NO2 and CO regarding higher positive contribution magnitudes in 2020 than those in 2019. As well, the PC5 had a higher contribution magnitude for SO2 in 2020 than in 2019, resulting in increased SO2 (Section 3.1).During the Lockdown period, which denotes the summer season in Thailand, there were significantly different major pollutant parameters contributing to the PC1 (25.0% and 25.5%) and PC2 (16.6% and 15.7%) for 2019 and 2020, respectively. In 2019, O3 contributed as a major pollutant (PC1) corresponding to photochemical reaction (NO2 + O2 ⟶ NO + O3), as seen in the strong contribution of T2M with the significant emission source of TI. This explains the correlations with temperature and, partly, with O3 concentrations that are commonly higher in summer [15]. PM2.5, PM10, NO2, SO2, and CO are minor pollutants (PC2) which relate to unknown emission sources, with the exception of SO2 and CO, which are associated with biomass burning (the PC4). Vice versa in 2020, the increases in PM2.5, PM10, NO2, and CO concentrations originated from unknown emission sources (PC1), accompanied by strong contributions from decreases in BLH, T2M, and WS. Meanwhile, the moderately negative O3 was related to chemical reaction (NO + O3 ⟶ NO2 + O2), becoming a minor mechanism (PC2) corresponding to the NO added from traffic (TI) and biomass burning (Fire) emissions. These results indicate some important evidence that explains the reduction of air pollutant concentrations in Section 3.1. With COVID-19 lockdown measures, people were largely restricted to their homes, and Greater Bangkok, with its high numbers of vehicles, should have had greater reductions in traffic emissions during the Lockdown period. Decreases in PM2.5, PM10, and CO concentrations in 2020 strongly contributed to the increased Fire (PC1) and the decreased TI (PC2), suggesting that changes in traffic emissions were more responsible for the improvements in air quality during the Lockdown period, especially fine particles, than biomass burning. On the other hand, increases in NO2 concentrations in 2020 (PC2) were significantly related to biomass burning. During the Lockdown period (March 2020), there were massive forest fires in northern Thailand, which reduced the impact of the lockdown on air pollution in that region. A report found an increase in some pollutants during the Lockdown period regarding forest fires in Malaysia [3, 10]. In addition, increased SO2 concentrations were associated with unknown emission sources, which were probably emitted from the industrial sector.During the After Lockdown period, which denotes the rainy season in Thailand, the PC1 and the PC2 could explain the variance by 25.6% and 15.8% for 2019 and 23.0% and 17.2% for 2020, respectively. In 2019, there were similar contributions of air pollutants with the Lockdown period in 2020, as seen with increases in O3 concentrations by the production of photochemical reactions being the major mechanism (PC1). Increased PM2.5, PM10, NO2, SO2, and CO concentrations were minor mechanisms (PC2). In 2020, PM2.5, PM10, NO2, SO2, and CO were major pollutants that originated from unknown sources, with the exception of the PC3, where SO2 concentrations were weakly associated with biomass burning. It can be noted that there were decreases in BLH, WS, and T2M, which are accumulative atmospheric conditions. Interestingly, there were significant decreases in both TI and Fire, while all pollutants except O3 concentrations had increasing trends. However, as the results in Section 3.1 explain, concentrations of PM2.5, PM10, and CO were still decreased to a lower degree during the After Lockdown period. Therefore, the results demonstrate that the improvement of air quality in Greater Bangkok after the easing of lockdown was a combined effect of other emission sources (industrial, household, etc.) and atmospheric mechanisms.All PCs during the lockdown of 2020 comprise important evidence that indicates the influence factors driving the improvement of air quality that were affected by the COVID-19 lockdown in Greater Bangkok. Atmospheric mechanisms play an important role in diluting or accumulating pollutant concentrations, while the emission sources influence the concentrations and type of major pollutants. Therefore, the COVID-19 lockdown measures influenced not only the air pollution levels but also affected the air pollution characteristics.


## 4. Conclusions

This study was carried out to expose the effects and influence factors of air quality due to the COVID-19 lockdown in Greater Bangkok, Thailand. Low traffic conditions and reduced human activities due to lockdown measures led to improved air quality in Bangkok. Overall, PM2.5, PM10, O3, and CO concentrations presented a significant decreasing trend during the COVID-19 outbreak year based on three periods: the Before Lockdown, Lockdown, and After Lockdown periods changed by the following amounts: PM2.5 (by −0.7%, −15.8%, and −20.7%); PM10 (by −4.1%, −31.7%, and −6.1%); and O3 (by −0.3%, −7.1%, and −4.7%), respectively. CO increased by 14.7% and then decreased by −8.0% and −23.6%, respectively, compared to the same periods in 2019, while SO2 increased by 54.0%, 41.5%, and 84.6% and NO2 went up by 20.1%, 3.2%, and 26.6% during the Before Lockdown, Lockdown, and After Lockdown periods, respectively. PCA was used to explore the influence factors driving improvements in air quality. The results indicate significant combination effects from atmospheric mechanisms that were strongly linked to emission sources such as traffic and biomass burning. Atmospheric mechanisms played an important role in diluting or accumulating the pollutant concentrations, while the emission sources influenced the concentrations and types of major pollutants. However, it was demonstrated that COVID-19 lockdown measures had a significant positive impact on the improvement of air quality due to decreased traffic emissions. With regard to the lockdown measures, they were not restricted by natural disasters such as forest fires in northern Thailand; the pollution from these sources were able to transport to Greater Bangkok, resulting in decreasing magnitudes of the lower pollutant levels recorded in other countries. Furthermore, the results show that after the lockdown was relieved, all pollutants except O3 tended to increase, even though Greater Bangkok’s populace still kept to decreased mobility and social activity. This implies that the COVID-19 lockdown was able to pause some anthropogenic emissions, i.e., traffic and commercial and industrial activities, but not all of them. Even low traffic emissions could not absolutely cause a reduction in air pollution since several primary emission sources dominate the air quality over Greater Bangkok. In addition, social distancing guidelines recommended that people stay at home, which caused the consumption of higher electricity, resulting in electric power plants increasing their production capacity and emitting more air pollution. Finally, the results demonstrate that the COVID-19 lockdown measures influenced not only the air pollution levels but also affected the air pollution characteristics.



---

*Source: 6697707-2021-02-04.xml*