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Asian Journal of Atmospheric Environment - Vol. 16 , No. 4
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Asian Journal of Atmospheric Environment - Vol. 14, No. 1
Abbreviation: Asian J. Atmos. Environ
ISSN: 1976-6912 (Print) 2287-1160 (Online)
Print publication date 31 Mar 2020
Received 09 Aug 2019 Revised 15 Nov 2019 Accepted 19 Feb 2020
DOI: https://doi.org/10.5572/ajae.2020.14.1.073

The Long-term Characteristics of PM10 and PM2.5 in Bangkok, Thailand
Supanan Chirasophon* ; Pakpong Pochanart
Graduate School of Environment Development Administration, National Institue of Development Administration (NIDA), Bangkok 10240, Thailand

Correspondence to : * Tel: +66-869-751-454 E-mail: ammsupanan.chi@gmail.com


Copyright © 2020 by Asian Journal of Atmospheric Environment
This is an open-access article distributed under the terms of the Creative Commons Attribution Non-Commercial License (http://creativecommons.org/licenses/by-nc/4.0/), which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.
Abstract

The long-term characteristics of non-roadside (residential) PM10 and PM2.5 in Bangkok, Thailand was analyzed by using hourly concentrations of PM10 and PM2.5 which had been collected from 10 monitoring stations by the Pollution Control Department (PCD) of Thailand from 2006 to 2016. The results showed that most of the stations showed either the decreasing trend or no trend characters. The PM2.5 and PM10 during weekdays and dry season were higher than during weekends and wet season, respectively. The diurnal variations of both PM2.5 and PM10 exhibited multi-peaks characteristic, mostly 2 peaks during a day for PM2.5 and 2 to 3 peaks depending on the locations for PM10. The PM2.5 to PM10 ratio of our residential monitoring stations was 0.61 in average which was in the same range as the PM2.5/PM10 ratio from the roadside monitoring stations. This shows that the common sources of PM2.5 and PM10 at both types of monitoring station were similar, probably mainly from the traffic and transportations. However, it was found that PM2.5/PM10 ratio during wet season was lower than during dry season indicating the role of emission sources and removal process in each season.

Keywords: PM2.5 to PM10 ratio, Long-term characteristics of PM2.5 and PM10, Bangkok, PM10, PM2.5
1. INTRODUCTION

Air pollution is one of the important urban environmental issues which globally killed an estimated 4.2 million people per year (WHO, 2018). PM2.5 and PM10 are major pollutants which link the premature death, the global trend of annual PM2.5 and PM10 levels during 2008-2013 increased by 8% (WHO, 2016). According to 2018 World Air Quality Report (AirVisual, 2018) the most cities which ranked top in an estimated annual average of PM2.5 concentration were in Asia and the Middle East. Among the capital cities, Delhi (India), Dhaka (Bangladesh), and Kabul (Afghanistan) occurred the maximum yearly average concentrations at 113.5, 97.1, and 61.8 μg/m3, while Bangkok (Thailand) ranked at 24th with 25.2 μg/m3 yearly concentration.

Bangkok, the capital of Thailand, has been rapidly developed and its urbanization accelerated more environmental issues in the city. Bangkok has been experienced the air pollutions for years. The main sources of those pollutants are transportations in the city (Pochanart, 2016). Recently, the situations of Bangkok’s air quality, especially PM2.5 and PM10 during the dry season, have been increasingly concerned by the public. In 2017, the PM2.5 average concentrations in Bangkok Metropolitan Region (BMR) exceeded the Thailand’s standard, 50 μg/m3 in 24 hours, about 40 to 50 days during January to March (PCD, 2018a). In 2018-2019, Bangkok’s air quality index (AQI) had been at an unhealthy level for months because of PM2.5 concentration crisis (Reuters, 2019). The vision in Bangkok was unclear and masks for protecting PM2.5 was in short supply. The local government announced warning to a sensitive group, especially the elderly and children (Lefevre, 2018), and released several solutions such as spraying water into the air by drones and driving trucks but it did not clearly show that the problems were solved by those solutions (Supoj, 2019; TheNation, 2019).

To investigate common characteristics of PM2.5 and PM10 and their causes in Bangkok, the study mainly focused on (1) the relation between the pollutants and time and (2) the ratio of both pollutants. To achieve the study’s goal, the long-term trends, the temporal variation, and the ratio between PM2.5 and PM10 were analyzed. The daily, weekly, and monthly variations of each pollutant could be related to urban activities, differently by location sources and time of the emission, while the monthly variation may additionally represent the influence of the weather condition to the characteristic of the pollutants. Moreover, the ratio between PM2.5 and PM10 could also show the relation of the pollution sources and seasonal factors.

2. METHODOLOGY

The concentrations of PM10 and PM2.5 which were analyzed in this study had been collected from 2006 to 2016, covered all dry season and wet season. According to Thai Meteorological Department (TMD, 2010), Climate of Thailand has been divided into 3 seasons; summer (February-May), rainy season (May-October), and winter (October-February). For this study, the dry season included summers and winters, while the wet season is only rainy seasons.

The raw data, hourly concentrations, had been collected by the Pollution Control Department (PCD) of Thailand, who has collected the air pollution data for decades. PCD has 2 categories of ambient monitoring station in Bangkok, roadside and non-roadside. There were 10 non-roadside monitoring stations which collected residential pollution concentrations and there were only 3 stations which the PM2.5 had been collected. The PM10 concentrations which were used in this study had been collected since 2006, while the PM2.5 concentration had been collected since 2016 at Bangna station (05T), 2015 at Phayathai station (59T), and 2014 at Wangthonglang station (61T). To compare the ratio, the roadside stations which have been collected both PM2.5 and PM10 were considered. There are only 2 out of all 6 roadside station which have been monitoring PM2.5. Those were Intharaphithak road station (52T) and Dindang road station (54T). The locations of the stations are shown in Fig. 1 and Table 1. The other 4 roadside stations which had not collected PM2.5 are not shown in the figure and table.


Fig. 1. 
Map of the locations of the monitoring stations in Bangkok area.

Table 1. 
The locations of the monitoring stations in Bangkok area.
St. ID Station Location Monitored PM
Latitude Longitude PM10 PM2.5
Non-roadside station
02T Thonburi district 13.7330 100.4882 ● ○
03T Ratburana district 13.6144 100.4059 ● ○
05T Bangna district 13.6661 100.6057 ● ●
07T Chatuchak district 13.8200 100.5759 ● ○
10T Bangkapi district 13.7795 100.6457 ● ○
11T Dindang district 13.7755 100.5692 ● ○
12T Yannawa district 13.7080 100.5473 ● ○
15T Chomthong district 13.6842 100.4460 ● ○
59T Phayathai district 13.7831 100.5405 ● ●
61T Wangthonglang district 13.7698 100.6146 ● ●
Roadside station
52T Intharaphithak road 13.7276 100.4866 ● ●
54T Dindang road 13.7626 100.5504 ● ●
●: PM concentration had collected; ○: PM concentration had not collected

According to PCD (PCD, 2016), the ambient air pollution has been monitored by using USEPA Federal Reference Method (FRM), gravimetric method for PM10 and In-stack Particulate filtration for PM2.5, or USEPA Federal Equivalent Methods (FEM) such as Beta Ray Attenuation, Tapered Element Oscillating Microbalance (TEOM), or Dichotomous Air Sampler for both PM10 and PM2.5. The stations are set at 1.5-6.0 meters above from ground level and 50 meters from main road for non-roadside or residential stations.

The data from all non-roadside stations were used for analyzing the long-term characteristics, while the relation between PM2.5 and PM10 were developed by using the data from 3 stations, which the PM2.5 had been collected. The hourly PM10 data which were used in this study covered 71.17% of all data monitoring for 11 years. The PM2.5 for 05T, 59T, and 61T covered 52.04%, 83.30%, and 73.25%, respectively. For organizing, and analyzing data and results in this study, commercial spreadsheet software was mainly used.

3. RESULTS AND DISCUSSION
3. 1 The Characteristics of PM10 and PM2.5

The monthly average concentrations for 11 years were plotted for determining long-term trends of PM10 at each station, whereas the PM2.5 trends were not discovered because of its relative short-term and lacking data. Examples of PM10 trend from 10 stations were shown in Fig. 2. The study found that long-term trends of PM10 was slightly decreasing in about half of the monitoring stations (02T, 11T, 15T, 59T, and 61T) and increasing in only one station, Ratburana station (03T). The stations with no-trend (not positive or negative) were determined when the correlation coefficient (R-value) were less than 0.1 or there were less than 50% of data at each station which were the cut-off point of the trends. There were four stations (05T, 07T, 10T, and 12T) that did not show positive or negative trends. However, if we look at the PM10 trend in the maximum months of the year, normally in dry season, and the minimum months year, normally in wet season, it appears that the decreasing trends are found in the wet season, while most stations in the dry season show positive trends. This is the main reason for recent pollution episode in Bangkok during dry season.


Fig. 2. 
The long-term trends of PM10 at each station (left), and the maximum and minimum monthly average PM10 of each year (right).

The decreasing trends probably showed that Bangkok strategies to solve long-term urban PM10 issue such as enhancing the fuel and vehicle standard and monitoring mobile sources in Bangkok were efficiently implemented, with the exception of the dry season PM10 and PM2.5 episodes.

The hourly concentrations of PM10 and PM2.5 were averaged by various time scales - hour, days of the week, and month - as shown in Fig. 3. The study showed that season and sources have a role in determining the pollution concentrations. As shown in the seasonal variations of PM10 and PM2.5, the average concentrations were decreasing in the wet season and increasing in the dry season. For PM10, the maximum monthly average concentrations which were normally in January and December ranged between 50.38-88.28 μg/m3, while the minimum monthly average concentrations which were normally in August, September, and May ranged from 21.72 to 39.04 μg/m3. The maximum concentrations of each station were 193%-265% higher than the minimum. For PM2.5, the maximum monthly average concentration for PM2.5 ranged from 36.38 to 45.42 μg/m3, while the minimum ranged from 13.60 to 27.10 μg/m3. The maximum concentrations of each station were 266%-334% higher than the minimum. The seasonal variations of PM2.5 were normally high in January and December and low during the mid-year. The high dry season and low wet season concentrations of PM10 and PM2.5 are common characteristics found similarly for other air pollutants such as ozone and carbon monoxide in Thailand as well (Pochanart et al., 2003; Pochanart et al., 2001).


Fig. 3. 
The characteristics of PM10 and PM2.5 (a) the seasonal variations of PM10, (b) the seasonal variations of PM2.5, (c) the days of week variations of PM10, (d) the days of week variations of PM2.5, (e) the diurnal variations of PM10, and (f) the diurnal variations of PM2.5.

The meteorological factors in the season influenced the character of the PM10 and PM2.5. The removal process by rain in the wet seasons probably has a role in reducing the pollutants, moreover, the weather condition in the dry seasons is always more stagnant and may be the cause of PM10 accumulating during the season. Biomass burning is another important source that characterize the differences between wet and dry season. More biomass burning during dry season produces higher PM2.5 and PM10 concentration. Although the levels of PM2.5 and PM10 in wet and dry season are different, the characteristic of PM2.5 and PM10 in other time scale, weekend/weekdays and diurnal variation, are still similar.

The PM10 and PM2.5 concentrations were normally higher during weekdays. For PM10, the weekdays’ average concentrations among the stations were about 3.01%-7.91% greater than the weekends’. The daily average concentrations were always highest on Wednesday and Thursday, and lowest on Sunday. Like PM10, the weekdays’ concentrations of PM2.5 were about 2.97%-10.62% higher than the weekends’ and the maximum values of PM2.5 were on Wednesday. But the lowest concentrations were normally on Saturday, except Bangna station (05T) which does not show the consistency in the minimum. The results could mean that there were fewer pollution sources on weekends or the sources during weekdays probably generated more pollutants. During weekdays, there were not only more traffic in rush hour, but also other sources from activities such as combustion in factory and construction work which generally do during the weekdays. In addition, when we look at the PM10 concentrations during long holidays which generally have less traffic in Bangkok compared to non-holidays, the PM10 concentrations during the long holidays, New Year holiday (31st December-2nd January) and Songkran Festival (13th-15th April, Thai New Year) are normally lower than the concentrations during the non-holidays in the same month, January and April.

For diurnal variations of PM10 and PM2.5, the common characteristic was that there were morning peaks. The peaks always occurred during rush hours which have heavy traffic. However, the diurnal variation of PM10 and PM2.5 were slightly different. The study revealed that PM2.5 had 2 peaks in the morning (hour 8-9) and the evening (hour 21-22). The morning peaks of PM2.5 were normally as high as the evening one. On the other hand, PM10 in 6 stations (02T, 03T, 05T, 07T, 10T, and 59T) normally showed 2 peaks and showed 3 peaks patterns in other 4 stations (11T, 12T, 15T, and 61T), but the morning peaks were generally higher than the other peaks. For example, PM10 shows one peak (hour 9) at 02T (Thonburi station), 2 peaks (hour 8 and 21) at 07T (Chatuchak station), and 3 peaks (hour 7, 13, and 19) at 12T (Yannawa station). The different number of peak hours means that the locality, such as traffic intensity, urban activities, and local meteorological condition in each area, probably had a role in determining the characteristic of the particulate matters’ concentration at each station.

For PM10 among the stations, the result found that Thonburi station (02T) had the highest average concentration, 56.18 μg/m3, while Chomthong station (15T) had the lowest, 33.32 μg/m3. The difference was 68.63%. It was found that the 3-highest PM10 concentration stations (02T, 07T, and 12T) are located in the center of Bangkok, while the 3 lowest PM10 stations (61T, 03T, and 15T) are located at the outskirt of Bangkok. For PM2.5, there were only 3 monitoring stations and the concentrations at each station did not show large differences.

The differences of the pollutant levels and patterns of each station probably mean that the characteristics of PM10 and PM2.5 were influenced by local factors, such as the local sources, weather or locations. The morning and evening peaks were probably affected by traffic, while other peaks may be caused by other minor sources (PCD, 2018b). Meanwhile, the baseline movement of PM2.5 may reflect the pollution transport from somewhere else. At the same station, the main sources of the PM10 and PM2.5 may be common, but the minor sources are different. Normally, both PM2.5 and PM10 were high when the traffic was dense, in the morning and evening.

3. 2 The Relation between PM2.5 and PM10
3. 2. 1 The Roadside and Non-roadside Ratios

The PM2.5 and PM10 concentration showed a strong correlation when we used linear regression, the correlation equation is [PM2.5]=m[PM10], when m is a slope of relation between PM2.5 and PM10. The PM2.5 and PM10 concentrations at the same hour were plotted using a scatter plot as shown in Fig. 4 (Noted that the irrational or invalid results, i.e. the hour that PM2.5 were higher than PM10 or there were only either PM10 or PM2.5 concentrations, were removed which may cause slight bias of the information).


Fig. 4. 
The relation between PM2.5 and PM10 for non-roadside and roadside stations.

Table 2 showed that the slopes of relation between PM2.5 and PM10 at non-roadside stations and roadside stations which ranged from 0.53 to 0.73. When compared the non-roadside stations with the roadside stations, we did not find distinct difference between the ratios. The results probably meant that sources of PM2.5 and PM10 from the roadside and non-roadside stations were common. The R2 of each station ranged from 0.46 to 0.87, regardless of station type. This may indicate that the number of common sources and emission characteristics at each station could be difference. The station with higher R2 may have lower numbers of common source but with more intensity of emission and shorter distance to the source. While the lower R2 probably represents the influence of the various common sources, some with less intensity or longer distance from monitoring station. Local meteorological factors also determine the correlation.

Table 2. 
The relation between PM2.5 and PM10.
Stations PM2.5 : PM10 R2
Non-roadside stations 0.53-0.73
(0.61 average)		 0.65-0.87
05T - Bangna district 0.73 0.87
59T - Phayathai district 0.53 0.65
61T - Wangthonglang district 0.63 0.81
Roadside station 0.53-0.65
(0.54 average)		 0.46-0.83
52T - Intharaphithak road 0.65 0.83
54T - Dindang road 0.53 0.46

According to Fig. 4, the distributions of PM10 at each station are similar with concentrations normally ranged from 0 μg/m3 to ~<300 μg/m3, but the PM2.5 distribution pattern among the station are more disperse with the maximum concentration ranged from ~<150 μg/m3 to ~<200 μg/m3 at different sites. The difference in PM2.5 concentration range could influence the R2 value and the ratio. It is noticed that the more dispersed PM2.5 in the relation to that of PM10 could lead to the lower R2. The stations with lower R2 typically show more dispersed concentration of PM2.5 as compared to the stations with higher R2 despite the similar PM10 concentration ranges among sites.

3. 2. 2 The Seasonal Ratios

The seasonal variations of PM2.5 to PM10 ratios for non-roadside stations (Fig. 5) showed that the ratios in the wet season were normally lower than the dry season.


Fig. 5. 
The seasonal variation of PM2.5 to PM10 ratios.

The seasonal ratios were calculated by data from 3 continuous-months during the dry season and the wet season of each station. The results also showed that the dry season ratios were higher than the wet season ratio. As shown in Fig. 6, the PM2.5 to PM10 ratio in the dry season was 0.64 with R2=0.76, while it was 0.58 with R2=0.56 in the wet season. According to Kim Oanh et al. (2006), the city averaged ratios between PM2.5 to PM10 at Bangkok during 2001-2004 were 0.64 for the dry season and 0.47 for the wet season. The dry season ratio was as same as the previous study, while the wet season ratio was higher for this study. Noted that the Bangkok city averaged ratios by Kim Oanh et al. (2006) were from upwind, traffic, urban, and residential sites.


Fig. 6. 
The PM2.5 to PM10 ratios in dry and wet season at non-roadside stations (05T, 59T, and 61T).

The result means that the emission characteristics of PM2.5 and PM10 were different during wet and dry season. According to a study on urban air pollution improvement in Asia (Kim Oanh, 2017), the major sources of PM2.5 were diesel vehicles and biomass burning. During the wet season, the diesel vehicles sources were about 1.8%-4.3% higher than the biomass burning. On the other hand, the biomass burning in the dry season was about 10.6%-14.7% higher than the vehicles sources. The fresh burning during dry season which release high PM2.5 proportion could contribute to the higher PM2.5 and PM10 mixing ratio during the dry months. Moreover, the removal process can also affect to the PM2.5 and PM10 concentration. During the wet season, there are both wet and dry depositions, while there is only dry deposition in the dry season. More removal processes during wet season could result in lower concentrations of PM2.5 and PM10 in the wet season.

3. 2. 3 The Comparison between Bangkok’s and Other Cities’ Ratios

To compare with the PM2.5 to PM10 ratios in other cities, the city averaged ratios were in the same ranged as this study, both developed and developing countries. As shown in Table 3, the mean ratios normally ranged between 0.6 to 0.8, except Chennai site. Compared to the ratio in Bangkok with 0.61 averaged for the non-roadside area, the ratio is in the same range as most cities. That implies that the major sources of urban PM2.5 and PM10 in Bangkok and other cities are probably similar. According to Watson and Chow (2000), the ratios from combustion and burning are normally over 0.80, while the ratios from physical processes, such as road dust and construction site, are lower than 0.30. The result probably indicates that most urban areas normally have common sources of the PM2.5 and PM10 which are mainly generated by combustion or burning. On the other hand, the major sources of PM2.5 and PM10 in Chennai may be the pollutant from the physical processes.

Table 3. 
The PM2.5 to PM10 ratios in other countries.
City/country PM2.5 to PM10 ratios Remarks
UK (Munir, 2016) 0.65 ranged 0.4-0.8
Scotland (Sykes, 2016) 0.66 ranged 0.56-0.80
Canada (Brook, Dann & Burnett, 1997) 0.51 Urban sites
Hongkong (EPD, 2012) 0.71 Annual ratio
0.75 Daily ratio
Wuhan, China (Xu et al., 2017) 0.62±0.22 Urban sites
Beijing, China (Kim Oanh et al., 2006) 0.60 Dry season
0.58 Wet season
Chennai, India (Kim Oanh et al., 2006) 0.30 Dry season
0.32 Wet season
Bandung, Indonesia (Kim Oanh et al., 2006) 0.63 Dry season
0.61 Wet season
Manila, Philippines (Kim Oanh et al., 2006) 0.61 Dry season
0.68 Wet season
Hanoi, Vietnam (Kim Oanh et al., 2006) 0.74 Dry season
0.62 Wet season

CONCLUSION

The long-term trends of PM10 are negative in most residential areas in Bangkok, while the trends in some areas did not show any positive or negative. During the dry season, the trends are generally increasing, while the trends are decreasing during the wet season. The PM2.5 and PM10 characteristics are influenced by meteorological factors and sources. The meteorological factors such as deposition and air transportation have a role in determining the characteristic. As shown in seasonal characteristic, the pollutions in the wet season are generally lower than in the dry season because of more deposition process, less stagnant weather, and lower emission from biomass burning. The PM2.5 and PM10 sources also determine their characteristics. The days of week characteristics and the difference between long holidays and non-holidays concentrations show that the pollution concentrations during weekends and holidays which have fewer mobile sources in urban area are normally less than during weekdays and non-holidays which has more urban activities. For the diurnal characteristics, there are common peaks, normally in the morning and evening, which occurs during heavy traffic hour. However, the other peaks probably show the influence of local sources which were differently observed at the sites.

The relation between PM2.5 and PM10 is shown as the PM2.5 to PM10 ratio. The study shows that the ratio of residential areas in Bangkok is 0.61. The seasonal variation of the ratios shows that the ratios are normally higher during the dry season, average 0.64 for the dry season and 0.58 for the wet season. The different major pollution sources in 2 seasons and deposition processes could affect to the ratios. More fresh burning in dry seasons may have a role in increasing PM2.5 part, while wet deposition which mainly occurs only in wet season may have a role in removing the pollutants from the atmosphere. Compared to other cities, in developed and developing countries, Bangkok’s ratio is in the same range as most cities. The result could mean that the source of PM2.5 and PM10 of most cities are common, mostly from combustion and burning process.

Acknowledgments

We would like to thank the Pollution Control Department (PCD) of Thailand who kindly provided the raw long-term data which is mostly used in the study.

References
1. AirVisual. (2018) 2018 World Air Quality Report. Retrieved May 11, 2019 from https://www.airvisual.com/world-most-polluted-cities/world-air-quality-report-2018-en.pdf.
2. Brook, J.R., Dann, T.F., Burnett, R.T. (1997) The Relationship Among TSP, PM10, PM2.5, and Inorganic Constituents of Atmospheric Participate Matter at Multiple Canadian Locations. Journal of the Air & Waste Management Association, 47(1), 2-19.
3. EPD. (2012) Guidelines on the Estimation of PM2.5 for Air Quality Assessment in Hong Kong. Retrieved April 20, 2018 from https://www.epd.gov.hk/epd/english/environmentinhk/air/guide_ref/guide_aqa_model_g5.html.
4. Kim Oanh, N.T. (2017) A Study on Urban Air Pollution Improvement in Asia. Retrieved April 20, 2019 from https://www.jica.go.jp/jica-ri/publication/booksandreports/l75nbg00000kjwkk-att/Final_report.pdf.
5. Kim Oanh, N.T., Upadhyay, N., Zhuang, Y.H., Hao, Z.P., Murthy, D.V.S., Lestari, P., Villarin, J.T., Chengchua, K., Co, H.X., Dung, N.T., Lindgren, E.S. (2006) Particulate air pollution in six Asian cities: Spatial and Temporal distributions, and associated sources. Atmospheric Environment, 40(18), 3367-3380.
6. Lefevre, A.S. (2018) Bangkok air pollution warning, children asked to stay indoors. Retrieved May 11, 2019 from https://www.reuters.com/article/us-thailand-weather/bangkok-airpollution-warning-children-asked-to-stay-indoors-idUSKBN1FS0ZF.
7. Munir, S. (2016) Analysing temporal trends in the ratios of PM2.5/PM10 in the UK. Aerosol and Air Quality Research, 17, 34-48.
8. PCD. (2016) Thailand’s air quality and situation reports 2014-2016. Retrieved April 15, 2018 from http://air4thai.pcd.go.th/webV2/download.php?grpIndex=0.
9. PCD. (2018a) Air and noise pollution situations and managements in Thainland 2017. Retrieved June 8, 2019 from http://air4thai.pcd.go.th/webV2/download_book.php?bookid=33 (in Thai).
10. PCD. (2018b) The study of PM2.5 in Bangkok Metropolitan Region Sources and Managements Project. Retrieved June 8, 2019 from http://infofile.pcd.go.th/air/PM2.5.pdf?CFID=1309453&CFTOKEN=84019792 (in Thai).
11. Pochanart, P., Akimoto, H., Kajii, Y., Sukasem, P. (2003) Carbon monoxide, regional-scale transport, and biomass burning in tropical continental Southeast Asia: Observations in rural Thailand. Journal of Geophysical Research Atmospheres, 108, ACH 10-1.
12. Pochanart, P., Kreasuwun, J., Sukasem, P., Geeratithadaniyom, W., Tabucanon, M.S., Hirokawa, J., Kajii, Y., Akimoto, H. (2001) Tropical tropospheric ozone observed in Thailand. Atmospheric Environment, 35(15), 2657-2668.
13. Pochanart, P. (2016) The present state of urban air pollution problems in Thailand’s large cities: cases of Bangkok, Chiang Mai, and Rayoung. Journal of Environmental Management, 12(1), 114-133 (in Thai).
14. Reuters. (2019) Bangkok fires water cannon into the air to fight pollution. Retrieved May 11, 2019 from https://www.bangkokpost.com/thailand/general/1611010/bangkok-fireswater-cannon-into-the-air-to-fight-pollution.
15. Supoj, W. (2019) City deploys water-spraying drones to reduce smog. Retrieved May 11, 2019 from https://www.bangkokpost.com/thailand/general/1621178/city-deploys-waterspraying-drones-to-reduce-smog.
16. Sykes, D. (2016) PM2.5 and PM10 in Scotland. Retrieved April 20, 2018 from http://www.scottishairquality.scot/assets/documents/technical%20reports/pm2.5-pm10ratio_29Mar2016-FINAL_Version_Approved.pdf.
17. Tan, P.H., Chou, C., Liang, J.Y., Chou, C.C.K., Shiu, C.J. (2009) Air pollution “holiday effect” resulting from the Chinese New Year. Atmospheric Environment, 43(13), 2114-2124.
18. TheNation. (2019) Planes, trucks spray water to soak up Bangkok’s smog. Retrieved May 11, 2019 from http://www.nationmultimedia.com/detail/national/30362242.
19. TMD. (2010) Climate of Thailand. Retrieved June 8, 2019 from https://www.tmd.go.th/en/archive/thailand_climate.pdf.
20. Watson, J., Chow, J. (2000) Reconciling Urban Fugitive Dust Emissions Inventory and Ambient Source Contribution Estimates: Summary of Current Knowledge and Needed Research. Desert Research Institue., Nevada, pp. 16-17.
21. WHO. (2016) Ambient air pollution: a global assessment of exposure and burden of disease: World Health Organization. pp. 25-26.
22. WHO. (2018) Air pollution. 8 May 2018. Retrieved June 25, 2019 from https://www.who.int/en/news-room/fact-sheets/detail/ambient-(outdoor)-air-quality-and-health.
23. Xu, G., Jiao, L., Zhang, B., Zhao, S., Yuan, M., Gu, Y., Liu, J., Tang, X. (2017) Spatial and Temporal Variability of the PM2.5/PM10 Ratio in Wuhan, Central China. Aerosol and Air Quality Research 2017(3), 1-116.
 
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This is an open-access article distributed under the terms of the Creative Commons Attribution Non-Commercial License (http://creativecommons.org/licenses/by-nc/4.0/), which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.