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Impact of Covid-19 partial lockdown on PM2.5, SO2, NO2, O3, and trace elements in PM2.5 in Hanoi, Vietnam


Covid-19 lockdowns have improved the ambient air quality across the world via reduced air pollutant levels. This article aims to investigate the effect of the partial lockdown on the main ambient air pollutants and their elemental concentrations bound to PM2.5 in Hanoi. In addition to the PM2.5 samples collected at three urban sites in Hanoi, the daily PM2.5, NO2, O3, and SO2 levels were collected from the automatic ambient air quality monitoring station at Nguyen Van Cu street to analyze the pollution level before (March 10th–March 31st) and during the partial lockdown (April 1st–April 22nd) with “current” data obtained in 2020 and “historical” data obtained in 2014, 2016, and 2017. The results showed that NO2, PM2.5, O3, and SO2 concentrations obtained from the automatic ambient air quality monitoring station were reduced by 75.8, 55.9, 21.4, and 60.7%, respectively, compared with historical data. Besides, the concentration of PM2.5 at sampling sites declined by 41.8% during the partial lockdown. Furthermore, there was a drastic negative relationship between the boundary layer height (BLH) and the daily mean PM2.5 in Hanoi. The concentrations of Cd, Se, As, Sr, Ba, Cu, Mn, Pb, K, Zn, Ca, Al, and Mg during the partial lockdown were lower than those before the partial lockdown. The results of enrichment factor (EF) values and principal component analysis (PCA) concluded that trace elements in PM2.5 before the partial lockdown were more affected by industrial activities than those during the partial lockdown.


Coronavirus was first reported in the city of Wuhan, China, in December 2019 (Huang et al. 2020; Huijun et al. 2020) and was declared a pandemic by March 11, 2020 (WHO 2020). In Vietnam, the first two coronavirus cases were confirmed on January 23, 2020. Since then, the Vietnamese government has taken a series of measures to prevent coronavirus outbreaks such as closing schools and universities, travel restrictions, quarantining residential areas, and restrictions on public gatherings. By December 12, 2020, there have been 1385 confirmed cases and 35 deaths in Vietnam (Ministry of Health of Vietnam 2020).

On April 1, 2020, a partial national lockdown was ordered by the Vietnamese government (Vietnam 2020), closing shopping malls, restaurants, fitness centers, kindergartens, elementary, middle, high schools, and universities. Travel restrictions were also implemented, and public transportation was stopped. Supermarkets and drugstores started working with a safety distance of 2 m during communication.

Recent studies have reported air quality improvements related to partial/full lockdowns and the consequent decrease of anthropogenic sources, including road traffic and industrial activities in Asia (Kerimray et al. 2020), China (Li et al. 2020; Wang et al. 2020a), and several European (Chauhan and Singh 2020) and American countries (Berman and Ebisu 2020; Nakada and Urban 2020). For example, Chauhan and Singh (2020) revealed a decline in PM2.5 concentration due to lockdown in major cities (New York, Los Angeles, Zaragoza, Rome, Dubai, Delhi, Mumbai, Beijing, and Shanghai) around the world. Kanniah et al. (2020) used the Himawari-8 satellite to quantify the changes in aerosol and air pollutants in southern Asian countries and observed 27–30% reduction of NO2 during the lockdown compared with the same period in 2018 and 2019. The authors also showed 26–31%, 23–32%, 63–64%, 9–20%, and 25–31% reduction of PM10, PM2.5, NO2, SO2, and CO, respectively, during the lockdown in an urban area in Malaysia compared with the same period in 2018 and 2019. Otmani et al. (2020) also analyzed the data in Salé city (North-Western Morocco) using field measurement (PM10) and in situ measurements (SO2 and NO2) to assess the impact of Covid-19 lockdowns on air quality. The authors observed 75, 49, and 96% reduction of PM10, SO2, and NO2, respectively, during the lockdown compared with the day before the lockdown. Nakada and Urban (2020) analyzed data from air quality stations to assess air quality during the partial lockdown in São Paulo, Brazil. The authors observed approximately 77, 54, and 65% reduction of NO, NO2, and CO, respectively, during the partial lockdown compared with the 5-year monthly mean. However, these studies which have focused on assessing common ambient pollutants (PM10, PM2.5, SO2, and NO2) in the environment metals associated with PM2.5 have not been reported. It is well known that toxic heavy metals bound to PM2.5 cause harm to human bodies via inhalation, ingestion, and dermal contact. These metals originate from anthropogenic sources, including road traffic and industrial activities (Bi et al. 2020; Ledoux et al. 2017). Thus, this study aims to assess the variation of PM2.5-, SO2-, NO2-, and PM2.5-bound elements in Hanoi city before and during the partial lockdown implemented due to the Covid-19 pandemic.

Materials and methods

Study area and sampling sites

Hanoi is a populous city with a total population of 7.4 million people (General Statistic Office of Vietnam 2019), about 623,668 automobiles and 6,013,582 motorbikes (TDSI 2017). It is the second largest city in Vietnam and covers an area of about 3328 km2. However, the city has faced serious air pollution (Cohen et al. 2013; Ly et al. 2018). The PM2.5 sampling was conducted in inner urban Hanoi city at three sites, namely S1, S2, and S3 (Fig. 1). The coordinates of the S1, S2, and S3 sampling sites were 21o04’14.7” N, 105o48’189” E; 20o59’50” N, 105o49’22” E; and 21o04’14.7” N, 105o48’189” E, respectively. All the sampling sites were situated on the rooftop of houses. The height above the ground of sampling points was in the range of 16–20 m. Furthermore, the S1 and S2 sites were within close range of 2nd ring roads, namely, Vo Chi Cong and Truong Chinh, respectively, while the S3 site was 100 m away from the 3rd ring road named Pham Van Dong. Also, the distance from the North Thang Long industrial park to both the S1 and S3 sites was approximately 6 km, whereas the S2 site was about 8 km far away from the Sai Dong industrial park. The North Thang Long industrial park is located at the North of the S3 site and the Northwest of the S1 site. The Sai Dong industrial park is located at the Northeast of the S2 site.

Fig. 1

Location of sampling sites (S1, S2, S3) and the automatic ambient air monitoring station (NVC)

PM2.5 sampling

The PM2.5 sampling was conducted consecutively at three sites from February 17, 2020, to March 23, 2020 (5 weeks before the partial lockdown), and from April 1, 2020, to April 22, 2020 (3 weeks during the partial lockdown). PM2.5 was collected using a high-volume air sampler (Shibata HV 500R, Japan) for 36 h at an average flow rate of 15 m3/h on quartz fiber filters (Advance, QR-100, size110mm, Japan), which was baked at 550 oC for 6 h before use. A total of 17 PM2.5 samples (8 before the partial lockdown and 9 during the partial lockdown) were collected at three sampling sites. The collected PM2.5 samples were wrapped in aluminum foil, transported to the laboratory, and stored in a desiccator with silica gel particles until analysis. To determine PM2.5 mass concentration, the filters were preconditioned before and after sampling (48 h in desiccators with a temperature of 25 ± 2 oC and relative humidity 50 ± 5%) and weighed using a microbalance (Adam AEA-160DG, sensitivity ± 0.01 mg). After weighing, the filter samples were stored under refrigeration at −30oC until chemical analysis.

Air pollution and meteorological data

Besides the PM2.5 mass concentrations obtained from fieldwork at three sampling sites in Hanoi, this study utilized further air pollution data including PM2.5, sulfur dioxide (SO2), nitrogen dioxide (NO2), and ozone (O3) concentrations. Daily pollutant concentrations from March to April 2020 at Nguyen Van Cu monitoring point were downloaded from the Northern Center for Environmental Monitoring (NCEM) ( (Fig.1). The mean concentration of PM2.5, NO2, O3, and SO2 from the automatic ambient air quality monitoring station before the partial lockdown (March 10–March 31) and during the partial lockdown (April 1–April 22) was calculated to analyze the variation of pollutant concentrations.

Besides, we utilized the hourly meteorological data including precipitation, temperature, boundary layer height, dew point temperature, and surface solar radiation. These are fifth-generation atmospheric reanalysis products of the European Centre for Medium-Range Weather Forecasts (ECMWF). The relative humidity was computed using the dew-point temperature and temperature data based on the method described in (Alduchov and Eskridge 1996). The mean precipitation, temperature, and relative humidity before and during partial lockdown were computed from the corresponding hourly data to analyze the impact of meteorology on the pollution level.

The variations in the contributions of stationary and mobile sources were analyzed using mass concentration ratios of [NO2]/[SO2] (Lian et al. 2020). [NO2]/[SO2] from the stationary and mobile sources had the range from 0.2 to 0.8 and from 24 to 119, respectively (Fiedler et al. 2009). Therefore, we computed mass concentration ratios of [NO2]/[SO2] during and before the partial lockdown in 2020 and in past years to investigate the contribution of mobile sources and stationary sources.

To estimate the possible emission sources of elements in PM2.5, the enrichment factor (EF) analysis and principal component analysis (PCA) were conducted. The enrichment factor (EF) analysis was used to determine the natural or anthropogenic sources of elements in PM2.5 (Kim et al. 2019; Zhang et al. 2018). The EF of each element was calculated according to the equation below:

$$ {\mathrm{EF}}_{\mathrm{X}}={\left(\raisebox{1ex}{$\mathrm{X}$}\!\left/ \!\raisebox{-1ex}{$\mathrm{R}$}\right.\right)}_{\mathrm{PM}2.5}/{\left(\raisebox{1ex}{$\mathrm{X}$}\!\left/ \!\raisebox{-1ex}{$\mathrm{R}$}\right.\right)}_{\mathrm{crust}} $$

where (X/R) PM2.5 and (X/R) crust are the concentration of the X element and reference element R in PM2.5 and crust, respectively. The concentration of elements in crust refers to their concentrations in Earth’s Crust proposed by Taylor (Taylor 1964). Ti, Si, Al, and Fe were generally used as reference elements of crustal materials (Cesari et al. 2012; Kim et al. 2002; Song et al. 2016). In this study, the element Ti was selected as the crustal reference element. If EFx value is close to 1, the element is mainly originated from natural sources. If EFx value is larger than 10, the element is mainly derived from anthropogenic sources. The value of EFx between 1 and 10 is indicated the elements emitted from both the natural and anthropogenic sources; however, the influences of anthropogenic sources on the element are small.

Analytical methods

The quarter filter of the sample filter was treated for analysis of heavy metals by the digestion method according to EPA method IO-3.1(U.S.EPA 1999). The sample filter was first to cut into pieces, then digested in 10 ml of mixed acid solution (HNO3: HCl in a ratio of 1:3), and kept on a hot plate at a high temperature until the transparent solution was boiled. After complete digestion, the digested sample was heated at a low temperature until nearly dry to remove excess acid. Then, the solution was diluted to a 25-ml volumetric flask with distilled water. Samples were analyzed using an inductively coupled plasma mass spectrometer (ICP-MS, ELAN 9000, Perkin Elmer) for Al, As, Ba, Ca, Cd, Co, Cr, Cu, Fe, K, Mg, Mn, Mo, Na, Ni, Pb, Ti, Zn, and V. In the analysis, a blank sample, a duplicated sample, and a spiked sample were measured for the quality control. The relative standard deviation of each element is within 10%, and the analytical errors were < 10%. The detection limit of all the trace elements was 0.01 ng/m3 except for Cd (0.002 ng/m3).

Statistical analysis

In this study, principal component analysis (PCA) was performed to determine potential sources of elements in PM2.5 using SPSS 22.0 software (IBM, USA). The concentration of elements in PM2.5 was normalized by dividing them by the total concentration of each sample. The rotation method was varimax, and eigenvalues higher than one were used for the principal components (PCs) extraction criterion.

Results and discussion

The concentration of PM2.5, SO2, O3, and NO2 obtained from the automatic ambient air quality monitoring station

In this study, we considered ambient air quality data during the partial lockdown (April 1st–April 22nd) and prior to the partial lockdown period (March 10th–March 31st). Air quality data in 2020 represented “current” data. Due to a lack of monitoring data in 2015, 2018, and 2019, air quality measurements in 2017, 2016, and 2014 were considered as the “historical” data. Table 1 presented the concentration of PM2.5, NO2, O3, and SO2 and meteorological data in Hanoi before and during the partial lockdown. As reported in Table 1, most of the meteorological parameters before and during the partial lockdown witnessed small variations. The change of mean temperature, precipitation, and relative humidity from before the partial lockdown in the current year and past years (shown in parentheses) were –3.7% (– 11.8%), 8.7% (–4.2%), and 1.2% (–0.1%), respectively. Therefore, the impact of temperature, precipitation, and relative humidity on the changes of pollution level during the partial lockdown would be minor.

Table 1 Mean concentration of PM2.5, SO2, NO2, O3, and average meteorological parameters recorded in Hanoi before the partial lockdown (March 10–31) and during the partial lockdown (April 1–22)

The decrease of air pollutants mainly resulting from the closing of non-essential public places, small industry, and reduced traffic during the Covid-19 lockdown period was also reported in previous studies (Berman and Ebisu 2020; Chauhan and Singh 2020; Nakada and Urban 2020; Otmani et al. 2020). The NO2 concentration dropped from 21.6 μg/m3 to 5.2 μg/m3, showing a significant reduction (–75.8%) during the current partial lockdown period compared with historical data. There was also a significant NO2 decline (–55.1%) with an absolute reduction of –6.4 μg/m3 before and during the partial lockdown in 2020. A decrease of NO2 concentrations was consistent with the value of –52.7% in Delhi, India (Mahato et al. 2020), and higher than the value of –46.6% in São Paulo, Brazil (Nakada and Urban 2020). The sharp variation of NO2 concentration is possibly associated with the abrupt decrease in vehicular traffic during the partial lockdown resulting from “work-from-home” and international and national travel limitations. Hien et al. (2014) demonstrated that exhaust emissions of motorbikes are a major source of NO2 in Hanoi. Additionally, SO2 declined 60.7% during the partial lockdown compared with the same dates in historical years. The SO2 reduction in this study is higher than other researchers found in the Yangtze River Delta Region (15–26%) (Li et al. 2020) and Malaysia (9– 20%) (Kanniah et al. 2020). However, a slight increase of SO2 (13.5%) was observed during the partial lockdown compared with the pre-partial-lockdown period in 2020. The small increase of SO2 concentration during the lockdown in Almaty, Kazakhstan, was reported by Kerimray et al. (2020), which could be statistically insignificant. The reduction of vehicular traffic and the closure of non-essential shops and businesses during the partial lockdown could cause a decrease of [NO2]/[SO2]. Both mobile sources (motorcycles (with two-stroke petrol engines), diesel trucks, buses, cars, and boats) and stationary sources (industry, power generation, and burning of biomass) are responsible for air pollution in big cities in Vietnam. Biomass burning sources include cooking and heating activities in homes and the street, burning of rubbish, and burning of rice straw and fresh vegetation in surrounding rural areas. Additionally, construction activities are both mobile and stationary sources that have made significant contributions to air pollution in Hanoi. Figure 2 illustrates a significant decrease of [NO2]/[SO2] during the partial lockdown period compared with that of historical years and before the lockdown period in 2020. The mean values of [NO2]/[SO2] before the partial lockdown were two times higher than that of the partial lockdown period. There was a significant drop in traffic during the partial lockdown, which caused the reduction of mobile emission sources. Although the industrial sector was affected by the Covid-19 pandemic, the industry factories and power plants in Vietnam still operate during the partial lockdown, which may lead to an insignificant change in the contribution of stationary sources. Thus, a drastic reduction of [NO2]/[SO2] during the partial lockdown was observed in Hanoi due to a significant reduction of mobile sources (vehicular traffic). Lian et al. (2020) also reported a significant reduction of [NO2]/[SO2] during the Covid-19 lockdown period in Wuhan, China. The partial lockdown in Hanoi experienced a reduction of –55.9% in PM2.5 concentration with the absolute decline of –55.0 μg/m3 compared with the same period in the past years. The reduced concentration of PM2.5 during the quarantine compared with historical years was higher than findings of other recent publications. PM2.5 reduction rate during the partial lockdown compared with historical years was 27.12% in megacity Delhi, India (Mahato et al. 2020), 39.0% in Gujarat state of India (Selvam et al. 2020), 29.8% in São Paulo state (Nakada and Urban 2020), and 32% in NewYork, USA (Chauhan and Singh 2020). A lower reduction of PM2.5 (–18.0%) during the partial lockdown compared with the pre-partial-lockdown in 2020 was recorded, which was less than a reduction of 23–32% in PM2.5 concentration in Malaysia (Kanniah et al. 2020). The decline of PM2.5 was less than the reduction of NO2, which may be because PM2.5 was emitted from multiple non-transportation sources such as industrial factories and biomass burning (Berman and Ebisu 2020).

Fig. 2

Mass concentration ratio of [NO2]/[SO2] before and during the partial lockdown in 2020 and in historical years

The average concentration of O3 decreased by –21.4% from 21.6 μg/m3 (average of historical years) to 17.1 μg/m3 (2020). However, an increase of 40.7% in O3 from 12.2 μg/m3 (before the partial lockdown) to 17.1 μg/m3 (during the partial lockdown) occurred in 2020. This result could be attributed to a high association between solar activity levels and the concentration of O3 (Nakada and Urban 2020). An increase of 20% in surface solar radiation during the partial lockdown period compared with the same days in historical years would lead to an increase in O3 concentration. On the other hand, a decline of O3 concentration in 2020 compared with historical data could be explained that surface solar radiation during the partial quarantine was 20% higher than the value measured before the partial lockdown period in 2020. The amplified O3 pollution was observed in cities worldwide. Sicard et al. (2020) reported the daily O3 mean concentrations increased at urban stations by 24% in Nice, 14% in Rome, 27% in Turin, 2.4% in Valencia, and 36% in Wuhan during the lockdown in 2020. Besides the high solar radiation activities, the increase of O3 can be attributed to the effect of chemical reactions caused by the strong decrease of nitrogen oxide emissions and PM2.5 (Chen et al. 2020; Menut et al. 2020; Sicard et al. 2020).

PM2.5 concentrations obtained from fieldwork

The PM2.5 concentration and average elemental concentration in PM2.5 at three sites in Hanoi prior to and during the partial lockdown period were shown in Table 2. The average PM2.5 concentration ranged from 73.65 to 90.67 μg/m3 before the partial lockdown period, which was higher than the ambient air quality standard in Vietnam for 24-h (50 μg/m3) and the annual standard (25 μg/m3) (QCVN 05:2013/BTNMT). Besides, the mean PM2.5 mass observed in this study was about 1.9 to 3.6 times higher than the guideline value suggested by WHO 24-h (25 μg/m3). Our study showed that the average PM2.5 concentration during the partial lockdown (47.85 μg/m3) was lower than the ambient air quality standards in Vietnam for 24-h, a decreased of –41.8 % compared with that before the partial lockdown. The average PM2.5 during the partial lockdown in this study was much higher than that in New York, USA (9.48 μg/m3), in Zaragoza, Spain (29.38 μg/m3) (Chauhan and Singh 2020), and in Sao Paulo, Brazil (12.4–12.5 μg/m3) (Nakada and Urban 2020). However, this study reported lower daily mean PM2.5 than in Megacity Delhi, India (60 μg/m3) (Mahato et al. 2020). A reduction of –41.8 % in PM2.5 in our study was much higher than that in Delhi, India (– 53.11%) (Mahato et al. 2020), in São Paulo state, Brazil (– 29.8%) (Nakada and Urban 2020), in Malaysia (23–32%) (Kanniah et al. 2020) and was similar to findings reported by Zoran et al. (2020).

Table 2 Average concentrations (average ± standard deviation) of metals in PM2.5 before the partial lockdown and during the partial lockdown in Hanoi (unit: ng/m3; except for the units of PM2.5 with *μg/m3)

Relationship between PM2.5 pollution and the boundary layer height (BLH)

Several studies have shown that the high boundary layer height (BLH) being associated with the low pollution level of particulate matter and vice versa (Chen and Xie 2014; Chu et al. 2019). Therefore, this study investigated the relationship between the BLH and PM2.5 concentrations obtained from both fieldwork and the automatic ambient air quality monitoring station in Hanoi. The hourly BLH data was first obtained from the fifth generation of the European Centre for Medium-Range Weather Forecasts (ECMWF) atmospheric reanalysis. After that, it was aggregated to the daily mean values and the mean values according to the sampling time to analyze its correlation with PM2.5 data from the automatic ambient air quality monitoring station and sampling sites, respectively. As shown in Fig. 3, the significantly negative correlation between the BLH and the PM2.5 obtained from the automatic air monitoring station (R = –0.37) and the PM2.5 obtained from fieldwork (R = –0.47) indicated that the shallow BLH would exacerbate the PM2.5 pollution. The significant negative correlation between the BLH and the daily PM2.5 concentration was also reported in Miao et al. (2017) with the range of R-value from –0.32 to –0.37. The negative correlation between the BLH and the PM2.5 concentrations could be explained by the fact that the vertical volume for dispersion and dilution of pollutants was regulated by the BLH, which modulates the PM2.5 concentration (Miao et al. 2019). In addition, the reduction of the PM2.5 pollution level would lead to an increase in the BLH due to the increment of surface solar radiation (Wang et al. 2020b). Therefore, to some extent, the increment of the BLH and surface solar radiation as shown in Table 1 would be partially attributed to the reduction of PM2.5 in Hanoi.

Fig. 3

Scatter plot between BLH and PM2.5 level in Hanoi (a) PM2.5 from field work and (b) PM2.5 from the automatic air quality monitoring station

Concentration of elements bound to PM2.5

Twenty elements in PM2.5 (Al, Na, Mg, V, K, Ba, Mn, Co, Ca, Fe, Cr, Cu, Ni, Mo, As, Pb, Zn, Cd, Ti, and Sr) were measured in this study. As shown in Table 2, the concentration of the most abundant elements (Fe, Al, Ca, K, Na, Mg, and Zn) was significantly higher than those of others at all sites before and during the partial lockdown. These elements were representative of crustal elements. The concentrations of Cd, As, Ba, Cu, Mn, Pb, K, Zn, Ca, Al, Mg, and Sr before the partial lockdown were higher than those during the partial lockdown, while the concentrations of V prior to and during the partial lockdown were similar. Our results showed that concentrations of Cd, Cu, Pb, Zn, and K were substantially decreased by 42.5, 45.2, 52.6, 51.7, and 44.7%, respectively, during the partial lockdown. Cu, Pb, Zn, are Fe are emitted from non-exhaust traffic sources such as tire and brake wear (Alves et al. 2018). Moreover, Jeong et al. (2019) showed that non-exhaust emissions contained a high contribution of trace elements (74% of Ba, 56% of Cu, and 42% of Fe). Denier van der Gon et al. (2007) showed that brake wear emissions accounted for up to 75% of Cu emissions into the air. Therefore, the decreases in the concentration of these metals could be the result of restriction on the traffic activities during the partial lockdown.

Lower reduction of trace metals concentration (Se (33.4%), As (27.2%), Sr (26.8%), Ba (32.1%), Ti (24.2%), Mn (23.4%), Mg (19.7%), Al (26.5%), Fe (12.2%), and Ca (30.1%)) were observed during the partial lockdown compared with before the partial lockdown. Al, K, Fe, Mn, Ni, and Cr were emitted from re-suspension of road dust (Chang et al. 2009; Lee and Hieu 2011; Lim et al. 2010; Manoli et al. 2002). Emission of Ni, Cd, Mn, As, Pb, Zn, and Cu could be emitted from metallurgical industry, boiler factories, thermal power plants, and coal combustion into the atmosphere (Chang et al. 2009; Cheng et al. 2017; Manoli et al. 2002; Tian et al. 2012). In addition, combustion of oil/ petrochemical plants (As, Cd, Cu, Cr, Zn, V, Ni, ) (Dai et al. 2015; Nielsen et al. 2013; Pacyna and Pacyna 2001; Querol et al. 2007), non-ferrous metal production (As, Cd, Cr, Cu, In, Mn, Zn) (Pacyna and Pacyna 2001), and gasoline combustion (Pb, Sr, Cu, Mn) (Pacyna and Pacyna 2001; Sanderson et al. 2014) also contributed to industrial emissions of trace metals. It is therefore assumed that reduction of anthropogenic emissions (industrial emissions, construction operations, mainly traffic) contributed to the reduction of metal concentrations. Li et al. (2020) and Kanniah et al. (2020) indicated that the reduction of air pollution was mainly related to the restriction on traffic and industrial activities. However, an increase in concentrations of Co (82.6%), Mo (47.8%), Ni (89.7%), and Cr (37.9%) found during the partial lockdown compared with the prior to the partial lockdown could be attributed to the activities of factories in an industrial park being close to CN site under the impact of atmospheric condition. Furthermore, Wang et al. (2020a) indicated that the restriction on anthropogenic activities would not help avoid severe air pollution due to the impact of weather conditions. Thus, the increments of these metal concentrations during the partial lockdown need further investigation.

Identification of elemental emission sources

Except for Co, a low EF (EF < 10) was observed for crustal metal (Ti, Al, Na, Mg, V, K, and Sr) during the partial lock and before the partial lockdown (Fig. 4). Conversely, high EF values (EF > 10) of Ca, Fe, Cr, Cu, Ni, Mo, As, Pb, Cd, and Se were observed both during the partial lock and before the partial lockdown (Fig. 4), which suggested that these elements originated from human activities. In particular, the EFs of As, Pb, Zn, and Cd were higher than 1000, which implied that the influence of the anthropogenic sources on these elements was dominant. The EFs for Ba and Mn were around 10 during the partial lockdown and a little bit higher than 10 before the partial lockdown, which indicated that their emissions were affected by both natural and anthropogenic sources.

Fig. 4

Element concentrations in PM2.5 before and during the partial lockdown in Hanoi

The results of the PCA (i.e., the loading plots of the 20 metals and the score plots of the individual periods) were presented in Fig. 5. Two PCs having eigenvalues greater than one were extracted; in general, they account for 65.7% of the total data variance (first PC: 43.7% and second PC: 22.0%). The score and loading plots were used to estimate relations between the periods and trace elements.

Fig. 5

Results of PCA represented by the score and loading plots of samples before the partial lockdown (open squares) and during the partial lockdown (close circles). Open triangle represented trace elements in PM2.5 samples

In general, the samples during the partial lockdown and before the partial lockdown were not strongly separated from each other in the score plot (Fig. 5a). However, some of the samples before the partial lockdown on the horizontal line of the score plot was separated from the samples during the partial lockdown on the right side and left side of the score plot. The separation of these three groups (group 1, group 2, and group 3) can be explained by the loading plot (Fig. 5). Group 1 (Zn) was located at a lower side of the loading plot, group 2 (Na, Sr, Mg, and Ca) were located at the right side of the loading plot, and group 3 (Mn, Pb, Cd, As, Cu, Ba, and K) were located at the horizontal line of the loading plot. This spatial distribution of these elements in the loading plot can be correlated with the distribution of the sample prior to and during the partial lockdown in the score plot.

Some of the samples during the partial lockdown in the score plot, which were determined by Zn and group 3 (Na, Sr, Mg, and Ca), were at the left side and right side of the loading plot, respectively. Some researchers reported that the high loadings of Mg and Ca were the typical elements of the crustal source (soil) (Gu et al. 2014; Kim et al. 2019; Morawska and Zhang 2002). Machado et al. (2008) and Zhai et al. (2014) found that Zn is mainly associated with non-exhaust traffic sources such as the brake and tire wear and other transport processes. This result implied that these metals during the partial lockdown originated from crustal sources/natural sources and were matched with their low EF values (Fig. 4) and non-exhaust traffic sources.

In addition, most of the samples (five out of eight samples) before the partial lockdown in the score plot can be explained by the distribution of elements in the loading plot, characterized by Mn, Pb, Cd, As, Cu, Ba, and K. These elements were representative of elements produced by industrial processes (Kim et al. 2019; Querol et al. 2007; Soleimani et al. 2018). Additionally, Cu and Ba were emitted from non-exhaust traffic sources such as brake wear (Jeong et al. 2019; Pant and Harrison 2013). Besides, other samples before the partial lockdown on the left side of the score plots were determined by the distribution of Zn in the loading plot. Hence, this result suggested that these elements before the partial lockdown were emitted from industrial activities and non-exhaust traffic, which was consistent with their high EF values (Fig. 4). This finding indicated that samples before the partial lockdown were more affected by industrial activities than those during the partial lockdown.


This study investigated the impact of the partial lockdown caused by Covid-19 on main air pollutants and the elements bound to PM2.5 in Hanoi. During the partial lockdown, NO2, PM2.5, O3, and SO2 decreased by 75.8, 55.9, 21.4, and 60.7%, respectively, compared with historical data. In addition, PM2.5 at sampling sites was reduced by –41.8%, which was consistent with the ground-based measurements. A noticeable increase of O3 (40.7%) concentration compared with the period before partial quarantine could be attributed to both high solar activities and the effect of chemical reactions caused by the strong decrease of NO2 emission and PM2.5. A slight increase in SO2 level (+ 13.5%) compared to pre-partial lockdown is possibly statistically insignificant. In addition, a significant negative correlation between the BLH and PM2.5 concentration was observed in Hanoi. However, the trivial variations of mean temperature, precipitation, and relative humidity prior to and during partial lockdown indicate a minor impact on the changes of pollutants level. Lower concentrations of Cd, As, Ba, Cu, Mn, Pb, K, Zn, Ca, Al, and Mg were observed during the partial lockdown. The values of EFx and results obtained from PCA indicated that Zn, Na, Sr, Mg, and Ca during the partial lockdown originated from crustal sources/nature sources and non-exhaust traffic sources, while Mn, Pb, Cd, As, Cu, Ba, and K before the partial lockdown period were emitted from industrial sources and non-exhaust traffic sources. This study demonstrated that decreases of air pollutants and elements bound to PM2.5 in this study area would mainly be attributed to a significant decrease in emissions from vehicle exhaust and the close of the small industry during the Covid-19 lockdown period.

Data availability

All data generated or analyzed during this study are included in this published article.


  1. Alduchov OA, Eskridge RE (1996) Improved Magnus form approximation of saturation vapor pressure. J Appl Meteorol 35:601–609.<0601:IMFAOS>2.0.CO;2

    Article  Google Scholar 

  2. Alves CA, Evtyugina M, Vicente AMP, Vicente ED, Nunes TV, Silva PMA, Duarte MAC, Pio CA, Amato F, Querol X (2018) Chemical profiling of PM10 from urban road dust. Sci Total Environ 634:41–51.

    CAS  Article  Google Scholar 

  3. Berman JD, Ebisu K (2020) Changes in U.S. air pollution during the COVID-19 pandemic. Sci Total Environ 739:139864.

    CAS  Article  Google Scholar 

  4. Bi C, Chen Y, Zhao Z, Li Q, Zhou Q, Ye Z, Ge X (2020) Characteristics, sources and health risks of toxic species (PCDD/Fs, PAHs and heavy metals) in PM2.5 during fall and winter in an industrial area. Chemosphere 238:124620.

    CAS  Article  Google Scholar 

  5. Cesari D, Contini D, Genga A, Siciliano M, Elefante C, Baglivi F, Daniele L (2012) Analysis of raw soils and their re-suspended PM10 fractions: Characterisation of source profiles and enrichment factors. Appl Geochem 27:1238–1246.

    CAS  Article  Google Scholar 

  6. Chang S-H, Wang K-S, Chang H-F, Ni W-W, Wu B-J, Wong R-H, Lee H-S (2009) Comparison of source identification of metals in road-dust and soil. Soil Sediment Contam Int J 18:669–683.

    CAS  Article  Google Scholar 

  7. Chauhan A, Singh RP (2020) Decline in PM2.5 concentrations over major cities around the world associated with COVID-19. Environ Res 187:109634.

    CAS  Article  Google Scholar 

  8. Chen Y, Xie S (2014) Characteristics and formation mechanism of a heavy air pollution episode caused by biomass burning in Chengdu, Southwest China. Sci Total Environ 473–474:507–517.

    CAS  Article  Google Scholar 

  9. Chen H, Huo J, Fu Q, Duan Y, Xiao H, Chen J (2020) Impact of quarantine measures on chemical compositions of PM2.5 during the COVID-19 epidemic in Shanghai, China. Sci Total Environ 743:140758.

    CAS  Article  Google Scholar 

  10. Cheng X, Huang Y, Long Z, Ni S, Shi Z, Zhang C (2017) Characteristics, sources and health risk assessment of trace metals in PM10 in Panzhihua, China. Bull Environ Contam Toxicol 98:76–83.

    CAS  Article  Google Scholar 

  11. Chu Y, Li J, Li C, Tan W, Su T, Li J (2019) Seasonal and diurnal variability of planetary boundary layer height in Beijing: Intercomparison between MPL and WRF results. Atmos Res 227:1–13

    Article  Google Scholar 

  12. Cohen DD, Garton D, Stelcer E, Wang T, Poon S, Kim J, Oh SN, Shin H-J, Ko MY, Santos F, Esquerra L, Bac VT, Hien PD, Uematsu M (2013) Characterisation of PM2.5 and PM10 fine particle pollution in several Asian regions. 16th Int Clean Air Conf 128:18–22.

  13. Dai Q-L, Bi X-H, Wu J-H, Zhang Y-F, Wang J, Xu H, Yao L, Jiao L, Feng Y-C (2015) Characterization and source identification of heavy metals in ambient PM10 and PM2.5 in an integrated iron and steel industry zone compared with a background site. Aerosol Air Qual Res 15:875–887.

    CAS  Article  Google Scholar 

  14. Denier van der Gon HAC, Hulskotte JHJ, Visschedijk AJH, Schaap M (2007) A revised estimate of copper emissions from road transport in UNECE-Europe and its impact on predicted copper concentrations. Atmos Environ 41:8697–8710.

    CAS  Article  Google Scholar 

  15. Fiedler V, Nau R, Ludmann S, Arnold F, Schlager H, Stohl A (2009) East Asian SO&lt;sub&gt;2&lt;/sub&gt; pollution plume over Europe – Part 1: Airborne trace gas measurements and source identification by particle dispersion model simulations. Atmos Chem Phys 9:4717–4728.

    CAS  Article  Google Scholar 

  16. General Statistic Office of Vietnam (2019) Statistical Yearbook of Vietnam 2019. Statistical Publishing House, Hanoi, pp 97

  17. Gu J, Du S, Han D, Hou L, Yi J, Xu J, Liu G, Han B, Yang G, Bai ZP (2014) Major chemical compositions, possible sources, and mass closure analysis of PM2.5in Jinan, China. Air Qual Atmos Health 7:251–262.

    CAS  Article  Google Scholar 

  18. Hien PD, Hangartner M, Fabian S, Tan PM (2014) Concentrations of NO2, SO2, and benzene across Hanoi measured by passive diffusion samplers. Atmos Environ 88:66–73.

    CAS  Article  Google Scholar 

  19. Huang C, Wang Y, Li X, Ren L, Zhao J, Hu Y, Zhang L, Fan G, Xu J, Gu X, Cheng Z, Yu T, Xia J, Wei Y, Wu W, Xie X, Yin W, Li H, Liu M, Xiao Y, Gao H, Guo L, Xie J, Wang G, Jiang R, Gao Z, Jin Q, Wang J, Cao B (2020) Clinical features of patients infected with 2019 novel coronavirus in Wuhan, China. Lancet 395:497–506.

    CAS  Article  Google Scholar 

  20. Huijun C, Juanjuan G, Chen W, Luo F, Xuechen Y, Zhang W, Li J, Zhao D, Xu D, Gong Q, Liao J, Yang H, Hou W, Zhang Y (2020) Clinical characteristics and intrauterine vertical transmission potential of COVID-19 infection in nine pregnant women: a retrospective review of medical records. Lancet 395:809–815.

    Article  Google Scholar 

  21. Jeong C-H, Wang JM, Hilker N, Debosz J, Sofowote U, Su Y, Noble M, Healy RM, Munoz T, Dabek-Zlotorzynska E, Celo V, White L, Audette C, Herod D, Evans GJ (2019) Temporal and spatial variability of traffic-related PM2.5 sources: Comparison of exhaust and non-exhaust emissions. Atmos Environ 198:55–69.

    CAS  Article  Google Scholar 

  22. Kanniah KD, Kamarul Zaman NAF, Kaskaoutis DG, Latif MT (2020) COVID-19’s impact on the atmospheric environment in the Southeast Asia region. Sci Total Environ 736:139658.

    CAS  Article  Google Scholar 

  23. Kerimray A, Baimatova N, Ibragimova OP, Bukenov B, Kenessov B, Plotitsyn P, Karaca F (2020) Assessing air quality changes in large cities during COVID-19 lockdowns: The impacts of traffic-free urban conditions in Almaty, Kazakhstan. Sci Total Environ 730:139179.

    CAS  Article  Google Scholar 

  24. Kim KH, Lee JH, Jang MS (2002) Metals in airborne particulate matter from the first and second industrial complex area of Taejon city, Korea. Environ Pollut 118:41–51.

    CAS  Article  Google Scholar 

  25. Kim I, Lee K, Lee S, Kim SD (2019) Characteristics and health effects of PM2.5 emissions from various sources in Gwangju, South Korea. Sci Total Environ 696:133890.

    CAS  Article  Google Scholar 

  26. Ledoux F, Kfoury A, Delmaire G, Roussel G, El Zein A, Courcot D (2017) Contributions of local and regional anthropogenic sources of metals in PM2.5 at an urban site in northern France. Chemosphere 181:713–724.

    CAS  Article  Google Scholar 

  27. Lee B-K, Hieu NT (2011) Seasonal variation and sources of heavy metals in atmospheric aerosols in a residential area of Ulsan, Korea. Aerosol Air Qual Res 11:679–688.

    CAS  Article  Google Scholar 

  28. Li L, Li Q, Huang L, Wang Q, Zhu A, Xu J, Liu Z, Li H, Shi L, Li R, Azari M, Wang Y, Zhang X, Liu Z, Zhu Y, Zhang K, Xue S, Ooi MCG, Zhang D, Chan A (2020) Air quality changes during the COVID-19 lockdown over the Yangtze River Delta Region: An insight into the impact of human activity pattern changes on air pollution variation. Sci Total Environ 732:139282.

    CAS  Article  Google Scholar 

  29. Lian X, Huang J, Huang R, Liu C, Wang L, Zhang T (2020) Impact of city lockdown on the air quality of COVID-19-hit of Wuhan city. Sci Total Environ 742:140556.

    CAS  Article  Google Scholar 

  30. Lim J-M, Lee J-H, Moon J-H, Chung Y-S, Kim K-H (2010) Airborne PM10 and metals from multifarious sources in an industrial complex area. Atmos Res 96:53–64.

    CAS  Article  Google Scholar 

  31. Ly BT, Matsumi Y, Nakayama T, Sakamoto Y, Kajii Y, Nghiem TD (2018) Characterizing PM2.5 in Hanoi with new high temporal resolution sensor. Aerosol Air Qual Res 18:2487–2497.

    CAS  Article  Google Scholar 

  32. Machado A, García N, García C, Acosta L, Córdova A, Linares M, Giraldoth D, Velásquez H (2008) Contaminación por metales (Pb, Zn, Ni y Cr) en aire, sedimentos viales y suelo en una zona de alto tráfico vehicular. Rev Int Contam Ambient 24(4). México Nov

  33. Mahato S, Pal S, Ghosh KG (2020) Effect of lockdown amid COVID-19 pandemic on air quality of the megacity Delhi, India. Sci Total Environ 730:139086.

    CAS  Article  Google Scholar 

  34. Manoli E, Voutsa D, Samara C (2002) Chemical characterization and source identification/apportionment of fine and coarse air particles in Thessaloniki, Greece. Atmos Environ 36:949–961.

    CAS  Article  Google Scholar 

  35. Menut L, Bessagnet B, Siour G, Mailler S, Pennel R, Cholakian A (2020) Impact of lockdown measures to combat Covid-19 on air quality over western Europe. Sci Total Environ 741:140426.

    CAS  Article  Google Scholar 

  36. Miao Y, Guo J, Liu S, Liu H, Li Z, Zhang W, Zhai P (2017) Classification of summertime synoptic patterns in Beijing and their associations with boundary layer structure affecting aerosol pollution. Atmos Chem Phys 17:3097–3110.

    CAS  Article  Google Scholar 

  37. Miao Y, Li J, Miao S, Che H, Wang Y, Zhang X, Zhu R, Liu S (2019) Interaction between planetary boundary layer and PM2.5 pollution in megacities in China: a Review. Curr Pollut Rep 5:261–271.

  38. Ministry of Health of Vietnam (2020) Accessed 12 Dec 2020

  39. Morawska L, Zhang J (2002) Combustion sources of particles. 1. Health relevance and source signatures. Chemosphere 49:1045–1058.

    CAS  Article  Google Scholar 

  40. Nakada LYK, Urban RC (2020) COVID-19 pandemic: Impacts on the air quality during the partial lockdown in São Paulo state, Brazil. Sci Total Environ 730:139087.

    CAS  Article  Google Scholar 

  41. Nielsen M, Nielsen O-K, Hoffmann L (2013) Improved inventory for heavy metal emissions from stationary combustion plants. 1990–2009. Aarhus University, DCE – Danish Centre for Environment and Energy, pp 111. Scientific Report from DCE – Danish Centre for Environment and Energy No. 68.

  42. Otmani A, Benchrif A, Tahri M, Bounakhla M, Chakir EM, El Bouch M, Krombi M (2020) Impact of Covid-19 lockdown on PM10, SO2 and NO2 concentrations in Salé City (Morocco). Sci Total Environ 735:139541.

    CAS  Article  Google Scholar 

  43. Pacyna JM, Pacyna EG (2001) An assessment of global and regional emissions of trace metals to the atmosphere from anthropogenic sources worldwide. Environ Rev 9:269–298.

    CAS  Article  Google Scholar 

  44. Pant P, Harrison RM (2013) Estimation of the contribution of road traffic emissions to particulate matter concentrations from field measurements: A review. Atmos Environ 77:78–97.

    CAS  Article  Google Scholar 

  45. Querol X, Viana M, Alastuey A, Amato F, Moreno T, Castillo S, Pey J, de la Rosa J, Sánchez de la Campa A, Artíñano B, Salvador P, García Dos Santos S, Fernández-Patier R, Moreno-Grau S, Negral L, Minguillón MC, Monfort E, Gil JI, Inza A, Ortega LA, Santamaría JM, Zabalza J (2007) Source origin of trace elements in PM from regional background, urban and industrial sites of Spain. Atmos Environ 41:7219–7231.

    CAS  Article  Google Scholar 

  46. Sanderson P, Delgado-Saborit JM, Harrison RM (2014) A review of chemical and physical characterisation of atmospheric metallic nanoparticles. Atmos Environ 94:353–365.

    CAS  Article  Google Scholar 

  47. Selvam S, Muthukumar P, Venkatramanan S, Roy PD, Manikanda Bharath K, Jesuraja K (2020) SARS-CoV-2 pandemic lockdown: Effects on air quality in the industrialized Gujarat state of India. Sci Total Environ 737:140391.

    CAS  Article  Google Scholar 

  48. Sicard P, De Marco A, Agathokleous E, Feng Z, Xu X, Paoletti E, Rodriguez JJD, Calatayud V (2020) Amplified ozone pollution in cities during the COVID-19 lockdown. Sci Total Environ 735.

  49. Soleimani M, Amini N, Sadeghian B, Wang D, Fang L (2018) Heavy metals and their source identification in particulate matter (PM 2.5 ) in Isfahan City, Iran. J Environ Sci (China) 72:166–175.

    Article  Google Scholar 

  50. Song X, Yang S, Shao L, Fan J, Liu Y (2016) PM10 mass concentration, chemical composition, and sources in the typical coal-dominated industrial city of Pingdingshan, China. Sci Total Environ 571:1155–1163.

    CAS  Article  Google Scholar 

  51. Taylor SR (1964) Abundance of elements in the crust: A new table. Geochim Cosmochim Acta 28:1273–1285.

    CAS  Article  Google Scholar 

  52. TDSI (2017) (Transport Development and Stategy Institute) A study to develop a set of applicators for sustainable development of urban road transport-application of calculations for the cities of Hanoi, Ho Chi Minh, Hai Phong, Da Nang, Can Tho. Ministry-level project

  53. Tian HZ, Lu L, Cheng K, Hao JM, Zhao D, Wang Y, Jia WX, Qiu PP (2012) Anthropogenic atmospheric nickel emissions and its distribution characteristics in China. Sci Total Environ 417-418:417–418.

    CAS  Article  Google Scholar 

  54. U.S.EPA (1999) IO Compendium of Methods IO-3.1: Compendium of method for the determination of inorganic compounds in ambient air: selection, preparation and extraction of filter material. EPA/625/R-96/010a. Cincinati, OH

  55. Vietnam (2020) Directive No.16/CT-TTG on Implementation of Urgent Measures for Prevention and Control of Covid-19. Accessed Date 31 March, 2020

  56. Wang P, Chen K, Zhu S, Wang P, Zhang H (2020a) Severe air pollution events not avoided by reduced anthropogenic activities during COVID-19 outbreak. Resour Conserv Recycl 158:104814.

    Article  Google Scholar 

  57. Wang Y, Wenkang G, Shuai W, Tao S, Zhengyu G, Ji D, Wang L, Liu Z, Tang G, Huo Y, Tian S, Li J, Li M, Yang Y, Chu B, Petäjä T, Kerminen V-M, He H, Hao J, Kulmala M, Wang Y, Zhang Y (2020b) Contrasting trends of PM2.5 and surface-ozone concentrations in China from 2013 to 2017. Natl Sci Rev.

  58. WHO (2020) WHO director-General’s opening remarks at the media briefing on COVID19 - 11 March 2020. - Accessed date 21 April, 2020

  59. Zhai Y, Liu X, Chen H, Xu B, Zhu L, Li C, Zeng G (2014) Source identification and potential ecological risk assessment of heavy metals in PM2.5 from Changsha. Sci Total Environ 493:109–115.

    CAS  Article  Google Scholar 

  60. Zhang J, Zhou X, Wang Z, Yang L, Wang J, Wang W (2018) Trace elements in PM2.5 in Shandong Province: Source identification and health risk assessment. Sci Total Environ 621:558–577.

    CAS  Article  Google Scholar 

  61. Zoran MA, Savastru RS, Savastru DM, Tautan MN (2020) Assessing the relationship between surface levels of PM2.5 and PM10 particulate matter impact on COVID-19 in Milan, Italy. Sci Total Environ 738:139825.

    CAS  Article  Google Scholar 

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This research is funded by Graduate University of Science and Technology under grant number GUST.STS.ĐT2019-MT01. We thank two anonymous referees, for their comments/suggestions which have helped us to improve the earlier version of the manuscript. We thank Dr. Parmeshwar Udmale from UKRI GCRF Living Deltas Hub, Asian Institute of Technology, Thailand, and Mr. Connor Morris from Brigham Young University for their great support in improving the quality of this manuscript, especially in English language in scientific writing.

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TPMN and THB designed and wrote the manuscript draft, read, corrected, and approved the final manuscript. KMN contributed to the interpretation of the results. THN provided facilities, technical and evaluated the results and discussion of these results. VTV and HLP contributed to the analysis of the samples. All authors read and approved the final manuscript.

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Correspondence to Thi Phuong Mai Nguyen or Thi Hieu Bui or Thi Hue Nguyen.

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Nguyen, T.P.M., Bui, T.H., Nguyen, M.K. et al. Impact of Covid-19 partial lockdown on PM2.5, SO2, NO2, O3, and trace elements in PM2.5 in Hanoi, Vietnam. Environ Sci Pollut Res (2021).

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  • Air pollution
  • Partial quarantine
  • Metals
  • SARS-CoV-2
  • Hanoi