Special Issue on COVID-19 Aerosol Drivers, Impacts and Mitigation (IV)

Rasa Zalakeviciute  1,2, Renne Vasquez2, Daniel Bayas2, Adrian Buenano2, Danilo Mejia3, Rafael Zegarra3, Valeria Diaz4, Brian Lamb5

1 Grupo de Biodiversidad Medio Ambiente y Salud (BIOMAS), Universidad de Las Americas, Quito – EC 170125, Ecuador
2 Universidad de Las Americas, Quito – EC 170125, Ecuador.
3 Carrera de ingeniería ambiental, Facultad de Ciencias Químicas, Universidad de Cuenca, Cuenca 010203, Ecuador
4 Air Quality Monitoring Network, Secretariat of the Environment, Municipality of the Quito Metropolitan District, Calle Rio Coca, Quito – EC 170125, Ecuador
5 Laboratory for Atmospheric Research, Washington State University, Pullman, WA 99163, USA


Received: May 23, 2020
Revised: June 29, 2020
Accepted: July 5, 2020

 Copyright The Author's institutions. This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are cited. 

Download Citation: ||https://doi.org/10.4209/aaqr.2020.05.0254  

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Cite this article:

Zalakeviciute, R., Vasquez, R., Bayas, D., Buenano, A., Mejia, D., Zegarra, R., Diaz, A. and Lamb, B. (2020). Drastic Improvements in Air Quality in Ecuador during the COVID-19 Outbreak. Aerosol Air Qual. Res. 20: 1783–1792. https://doi.org/10.4209/aaqr.2020.05.0254


  • Impact of reduced human activities on urban air quality in Ecuador is investigated.
  • Air quality in Quito, Ecuador improved by 29–68% due to COVID-19 quarantine measures.
  • Geographic dependent pollution reductions vary due to differing preventative measures.


In the beginning of 2020, the global human population encountered the pandemic of novel coronavirus disease 2019 (COVID-19). Despite social and economic concerns, this epidemiologic emergency has brought unexpected positive consequences for environmental quality as human activities were reduced. In this paper, the impact of restricted human activities on urban air quality in Ecuador is investigated. This country implemented a particularly strict set of quarantine measures at the very dawn of the exponential growth of infections on March 17, 2020. As a result, significant reductions in the concentrations of NO2 (–68%), SO2 (–48%), CO (–38%) and PM2.5 (–29%) were measured in the capital city of Quito during the first month of quarantine. This large drop in air pollution concentrations occurred at all the monitoring sites in Quito, serving as a valuable proof of the anthropogenic impact on urban air quality. The spatial evolution of atmospheric pollution using observed surface and satellite data, showed different results for the two major cities: Quito and Guayaquil. While the population in Quito adhered to the quarantine measures immediately, in the port city of Guayaquil, quarantine measures were slow to be adopted and, thus, the effect on air quality in Guayaquil occurred more slowly. This lag could have a considerable cost to the mortality rate in the port city, not only due to the spread of the disease but also due to the poor air quality. Overall, the air quality data demonstrate how quickly air quality can improve when emissions are reduced.

Keywords: COVID-19; Urban air pollution; Quarantine measures.


In the first three months of 2020, the human population of the world encountered a colossal challenge—a global pandemic of coronavirus disease 2019 (COVID-19). This infectious disease is caused by the novel severe acute respiratory syndrome coronavirus 2 (SARS-CoV-2). The first news of the exponential infection rate of SARS-CoV-2, spreading to thousands of people in a period of weeks and rapidly causing countless deaths, started arriving from China in January 2020. Then, quickly, by the end of March 2020, the same exponential growth of infection was replicated in almost every country of the world (Worldometer, 2020). Some countries rigorously adopted social distancing measures by putting in quarantine entire cities at the first few identified cases. Meanwhile, others chose to wait until the numbers reached well into thousands to apply mitigation actions, if at all. For the significance of this study, one of the countries implementing the stricter scenario is Ecuador (pop. 16.6 million people). The capital Quito suspended all non-essential activities when eight infected individuals were reported on March 17, 2020. However, in Guayaquil, the biggest port city in Ecuador, the local population failed to adopt the quarantine measures quickly. Reported infections quickly grew from 111 to about 1082 individuals nationally in one week, but most of these were in Guayaquil (Servicio Nacional de Gestion de Riesgos y Emergencias, 2020). This rapid escalation placed Ecuador at the top of the list of Latin American countries with the highest infection and death rates (Cabrera and Kurmanaev, 2020; Worldometer, 2020).

Despite the calamities caused to human health by the coronavirus outbreak, this crisis has brought unexpected positive consequences for air quality and the environment. Relentless population growth and urbanization in the past decades have produced continuously worsening air quality conditions in many cities in developing countries (UN, 2015; Limb, 2016; WHO, 2016). Criteria atmospheric pollutants (carbon monoxide (CO), nitrogen oxides (NO and NO2), sulfur dioxide (SO2), ozone (O3) and particulate matter (PM)), predominantly fine particulate matter (with aerodynamic diameter ≤ 2.5 µm, PM2.5), are known for causing negative effects on respiratory and cardiovascular health (Pope and Dockery, 2012; Lelieveld et al., 2015; U.S EPA, 2018). These negative health impacts exacerbate the symptoms of COVID-19 (Gardiner, 2020; Wu et al., 2020).Worldwide implementations of precautionary quarantine, namely closures of factories, shopping centers, restrictions on travel and transportation, have resulted in a considerable reduction of emissions of air pollutants as well as greenhouse gases (Cho, 2020; Wang et al., 2020). In contrast to other research, a recent study in Tehran reported an increase in PM2.5 and PM10 concentrations due to a rise in private car use during the quarantine (Faridi et al., 2020). In different regions of China, studies have shown that strict COVID-19 control policies significantly reduced concentrations of criteria pollutants except for ozone (Chen et al., 2020; Xu et al., 2020). The most significant decrease in CO (20–36%) and NO2 (30–52.8%) concentrations were correlated with a reduction of emissions due to economic and transport restrictions (Filonchyk et al., 2020; Xu et al., 2020). The National Aeronautics and Space Administration (NASA) and the European Space Agency released satellite images that show a significant (10–30%) reduction in nitrogen dioxide (NO2) concentrations, between the months of January and February in eastern and central China, and between February and March in northern Italy (ESA, 2020; NASA, 2020). Chinese data also showed the lowest average concentrations of PM2.5 particulate matter since 2014 (Cho, 2020; Wang et al., 2020), confirmed by (Xu et al., 2020). However, as expected, the pollution levels have returned to previous levels when economic activities are resumed (Filonchyk et al., 2020).

The economic slowdown due to the COVID-19 outbreak has also caused at least a 25% decline in carbon dioxide (CO2) emissions in late January in China, representing a 6% reduction in global emissions (Cho, 2020). As a result, during the last three weeks of February, China emitted 150 million metric tons less of CO2 than last year on the same dates. A recent study showed that global CO2 emissions in March 2020 were 7% lower than the same time last year, mostly due to the decrease in industrial use of fossil fuels, especially coal (Safarian et al., 2020).

At this point, during the first months of social distancing and mitigation actions, there is still a lack of published scientific studies concerning changes in air quality in the cities of Latin America. Prata et al. (2020) reported results for Brazil which only focused on the impact of meteorological parameters on COVID-19 pandemic. Prata et al. (2020) found a negative linear relationship between temperatures and daily cumulative confirmed cases of COVID-19. This relationship was also reported for Malaysia (Suhaimi et al., 2020), but not in studies in Norway and Singapore (Menebo, 2020; Pani et al., 2020). Therefore, the objective of this paper is to evaluate the impact of the reduced human activities on urban air pollution in the Ecuadorian capital, Quito. The case of Quito is additionally more interesting, as a range of strict social measures were implemented early on; and as a result, there is already one month of quarantine data on atmospheric conditions from this high elevation Andean city.


Study Site

Ecuador is one of the less urbanized countries in South America, the second most urbanized continent of our planet (UN, 2019). The capital city Quito is located on a narrow plateau wrapping around the Pichincha volcano (elev. 4,800 meters above sea level (m.a.s.l.)) in the Andes cordillera. The city is the highest constitutional capital of the world with an average elevation of 2,815 m.a.s.l. (EMASEO, 2011). The rapidly growing metro area now occupies 4,218 km2 with more than 2.2 million people (INEC, 2011). Due to the use of poor quality fuels, the city struggles with long-term air pollution problems (Zalakeviciute et al., 2017). The city has a mild spring-like climate with two distinct seasons: wet (September–May) and dry (June–August) (Zalakeviciute et al., 2018a).

Within the city mayor’s office, the Secretariat of Environment has managed an air quality network since 2004 to monitor the concentrations of atmospheric criteria pollutants and meteorological parameters. Nine monitoring stations are distributed across the city in representative areas varying in elevation, population density, intensities of traffic and industrial activities. In this investigation, data from seven study sites were analyzed: Guamani (elev. 3,066 m.a.s.l., coord. 78°33'5''W, 0°19'51''S), Los Chillos (elev. 2,453 m.a.s.l, coord. 78°27'36''W, 0°18'00''S), Camal (elev. 2,840 m.a.s.l, coord. 78°30'36''W, 0°15'00''S), Belisario (elev. 2,835 m.a.s.l, coord. 78°29'24''W, 0°10'48''S), Centro (elev. 2,820 m.a.s.l, coord. 78°30'36''W, 0°13'12''S), Cotocollao (elev. 2,739 m.a.s.l, coord. 78°29'50''W, 0°6'28''S) and Carapungo (elev. 2,660 m.a.s.l, coord. 78°26'50''W, 0°5'54''S) (see Fig. 1).

Fig. 1. Map of the study sites distributed in the Ecuadorian capital, Quito.Fig. 1. 
Map of the study sites distributed in the Ecuadorian capital, Quito.

Quito Air Quality Monitoring

At each site, air quality monitoring equipment were positioned on the roofs of buildings, in agreement with the requirements set by the Environmental Protection Agency of the United States (U.S. EPA). To measure the concentrations of CO, ThermoFisher Scientific 48i instruments, based on infrared absorption (EPA No. RFCA-0981-054), were used. For SO2, ThermoFisher Scientific 43i high level SO2 analyzers were used. This method is based on ultraviolet florescence (EPA No. EQSA-0486-060). For O3, ThermoFisher Scientific 49i ozone analyzers based on ultraviolet absorption (EPA No. EQOA-0880-047) were used. For NO2, ThermoFisher Scientific 42i NOx analyzers were used. This method is based on chemiluminescence method (EPA No. RFNA-1289-074). Finally, to measure the concentrations of fine particulate matter - PM2.5, Thermo Scientific FH62C14-DHS continuous ambient particulate monitors 5014i were used. This method is based on a beta ray attenuation method (EPA No. EQPM-0609-183).

To acquire meteorological data, complete weather stations with automatic sensors were used. To measure wind speed and direction MetOne instruments were used. Thies Clima equipment were used to measure relative humidity, temperature and precipitation. Finally, solar radiation parameters were measured with Kipp & Zonen radiometer and pressure with Vaisala equipment.

Sentinel 5P

The tropospheric concentration (mol m–2) columns of gases used in this research project are products of the TROPOMI instrument on board the Sentinel - precursor (S5P). This satellite carries instruments for the measurement of various pollutants such as NO2, CO, SO2, CH4 and O3(Veefkind et al., 2012; Zheng et al., 2019). For our analysis, the L3 level images, provided by the Google Engine (GGE) platform, were used.


The COVID-19 case count for Ecuador was acquired from the Worldometer (https://www.worldometers.info/coronavirus/) webpage.

The atmospheric pollution and meteorological data were compiled into four-week, hourly and diurnal averages during the periods prior and during the COVID-19 quarantine. For illustrative purposes, hourly NO2, SO2, PM2.5 and CO concentrations were processed as 24-hour averages starting January 2020. February 2020 data were considered as “normal” conditions, with a usual human activity, and were compared with the pollution levels during the first four weeks of the quarantine March 17–April 12, 2020. All data processing and graphics were performed using Microsoft Excel (MS Office) and Igor Pro (Wavemetrics) softwares. Maps of the city pollution were created using Inverse distance weighting in QGIS open source software.

The S5P satellite data resolution of tropospheric concentration (mol m–2) columns is 1 km2 per pixel. Knowing that S5P captures total column products of trace gases, daily images of total column of NO2 and tropospheric SO2 from the Royal Netherlands Meteorological Research Institute (KNMI) were used for March 9–31, 2020 (Xue et al., 2020). For this study, daily images were separated into three groups: 9–15 March 2020 one week before quarantine and two first weeks of quarantine March 16–22 and 23–30, 2020. Raster analysis tools were used to obtain the weekly averages. For this study the Google Engine (GGE) platform was used which allows to download L3 level products, GGE uses HARP commands which provides images.


COVID-19 Quarantine Timeline in Quito, Ecuador

A series of quarantine measures were progressively implemented in Ecuador within the first two weeks of a quick escalation of COVID-19 cases (see Fig. 2(a)). On the 16th of March 2020, strict mandatory mitigation measures, focused on a social distancing, were communicated by the national government to the public of Ecuador. At this point there were already 111 confirmed cases, mostly concentrated in the port city of Guayaquil, with no reported cases of deaths in the country (Worldometer, 2020). The next day those measures were successfully applied by the local government in Quito. All city transportation was cancelled, with the exception of the taxi and food/medication delivery services. The use of private vehicles was limited to only essential tasks, such as food and medication purchases. The operation of all businesses, except banks, food stores and pharmacies, was prohibited. All restaurants, theatres, and other public activities were banned by the law. As these measures were implemented, there were some intentions to disobey them, including some protesting activities. These were especially frequent in the port city of Guayaquil. Thus, on Saturday, 21 March 2020, the curfew rule was applied nationally from 19:00 to 5:00, in anticipation of possible weekend festivities. If disobeyed, this rule implied a jail-time punishment. As numbers surpassed 1000 of infected cases on 23 March 2020, additional measures were implemented to further control the use of private vehicles. Vehicle usage was limited, based on the last number of the license plate, allowing circulation only every second day for essential tasks, like food and medication purchases. Furthermore, a stricter curfew was adopted on March 25, 2020 from 14:00 to 5:00, as the number of deaths started rising quickly due to the saturation of limited-capacity hospitals in the country. These measures might seem excessive, when compared to the strategies implemented by other countries, however, at that point, most of the extreme quarantine conditions were reported from the developed and rich in resources countries, and even those were struggling with high daily mortality (e.g., 600–700 cases in Spain and Italy) (Worldometer, 2020). Finally, starting April 5, 2020, private transportation was even further restricted to circulation allowed once per week (based on license plate) for essential shopping, and completely forbidden on the weekends (Fig. 2). There were still essential services allowed, like garbage, gas and food delivery services, even during the curfew hours. But people faced monetary fines, confiscation of their vehicle throughout the quarantine and even jail-time, if caught breaking the law. The circulation between the cities and provinces were strictly forbidden as well since the beginning of the quarantine.

Fig. 2. 24-hour average concentrations for January 1–April 12, 2020 for: a) NO2, b) SO2, c) PM2.5 and d) CO. Blue shaded area indicates the period of COVID-19 quarantine. National quarantine measures (green dotted lines) are displayed in the panel (a). COVID-19 number of infections in Ecuador (black line) are displayed on the right axis of (b). Hourly wind speed data are added on the right axis of (c). Cumulative 24-hour precipitation is displayed on the right axis of (d).
Fig. 2.
 24-hour average concentrations for January 1–April 12, 2020 for: a) NO2, b) SO2, c) PM2.5 and d) CO. Blue shaded area indicates the period of COVID-19 quarantine. National quarantine measures (green dotted lines) are displayed in the panel (a). COVID-19 number of infections in Ecuador (black line) are displayed on the right axis of (b). Hourly wind speed data are added on the right axis of (c). Cumulative 24-hour precipitation is displayed on the right axis of (d). 

Concentrations of Criteria Pollutants in Quito

To demonstrate the contrast in urban air pollution due to the COVID-19 mitigation measures in Quito, 24-hour all-sites average NO2, SO2, PM2.5 and CO concentrations are presented in Fig. 3 for January 1–April 12, 2020. It can be easily distinguished that the concentrations of the four criteria pollutants began to decrease on March 13, 2020, Friday before the official implementation of the quarantine measures (starting Tuesday, March 17, 2020, see Fig. 2(a), blue shaded area). This suggests that even before the official quarantine, people started self-isolating, as the number of COVID-19 cases started rising with the first reported death on March 13, 2020 (Fig. 2(b)). A slight increase in concentrations of criteria pollutants can be noted on Monday, March 16, 2020, before the first regulation is applied. However, an overall decreasing trend can be clearly seen (see Fig. 2). Interestingly, while the gaseous pollution levels decreased, PM2.5 concentrations displayed more variability (Fig. 2(c)). This might be due to the fact that even though the anthropogenic emissions were reduced, variable wind speeds could produce varying levels of windblown dust especially during the second week of quarantine (23–29 March 2020) (Fig. 2(c)). Wind direction patterns within the city are quite complex due to the complex terrain. However, we did not observe significant changes in wind direction patterns (not shown) during the quarantine compared to before the quarantine. While the concentrations of the gaseous pollutants reflected a large reduction of anthropogenic activities, the particle pollution levels result from a combination of emissions from anthropogenic activities and dust resuspension. This was also supported by visual observations of hazy skies during the second week of the quarantine, coinciding with windier conditions. The windblown dust appears to be a predominant factor in PM2.5concentration peaks during these unusual conditions. Finally, as the weather was drier and sunnier, there is an increased possibility of fires, which were also observed in the area. During the last week of the observation period, there were extremely rainy conditions (April 11, 2020) which reduced the particulate resuspension (Fig. 2(d)).

Fig. 3. Four-week average NO2, SO2, PM2.5 and CO concentrations for February 2020 (Feb, 2020) and March 17–April 12, 2020 (period of COVID-19 quarantine measures) in Quito. Comparative bar plot analysis between sites for: a) NO2, b) SO2, c) PM2.5, and d) CO concentrations. Error bars indicate standard deviation. Spatial analysis is included between the two sets of four weeks: e) and i) for NO2, f) and j) for SO2, g) and k) for PM2.5, and h) and l) for CO concentrations evolution due to the quarantine measures.Fig. 3.
 Four-week average NO2, SO2, PM2.5 and CO concentrations for February 2020 (Feb, 2020) and March 17–April 12, 2020 (period of COVID-19 quarantine measures) in Quito. Comparative bar plot analysis between sites for: a) NO2, b) SO2, c) PM2.5, and d) CO concentrations. Error bars indicate standard deviation. Spatial analysis is included between the two sets of four weeks: e) and i) for NO2, f) and j) for SO2, g) and k) for PM2.5, and h) and l) for CO concentrations evolution due to the quarantine measures.

The comparative analysis between average concentrations of NO2, SO2, CO and PM2.5 for the month before the COVID-19 outbreak (February 2020) and during the first four weeks of COVID-19 quarantine (17 March–12 April 2020) across all seven sites are presented in Fig. 3. The results show a strong reduction in average concentrations of four studied criteria pollutants: NO2 (68%), SO2 (48%), CO (38%) and PM2.5 (29%). This large drop in air pollution concentrations was observed at all of the monitoring sites (Figs. 3(a)3(d)). This is a clear demonstration of the effect of reduced anthropogenic activities on urban air quality. PM2.5 and CO concentrations were reduced, while NO2 and SO2 concentrations decreased to levels close to zero, especially in the more residential parts of the city (e.g., Cotocollao). However, there is still some evidence of anthropogenic activity in the business districts of Belisario, which includes banks, pharmacies, major shopping centers, and of Los Chillos, which is a suburban residential district with a thermoelectric power plant, see Fig. 1). The change in NO2 levels is higher than those reported in other global cities, ranging from 16% to 53% (Chen et al., 2020; Filonchyk et al., 2020; Xu et al., 2020), similarly, the reduction in levels for CO (12–36%), PM2.5 (14–50%) and SO2 (12–52.5%) in Quito are also in the higher range compared to other global cities, which is probably due to the strictness of the measures in Ecuador.

The change in local pollution levels due to the COVID-19 quarantine measures can be also seen in the spatial distribution maps (Figs. 3(e)3(l)). Four–week averages are shown for February and March 17–April 12, 2020 for NO2, SO2, CO and PM2.5 concentrations in the metropolitan area of Quito. The most notable change can be seen for NO2, the combustion marker for diesel and gasoline engines (Ban-Weiss et al., 2008; Park et al., 2019). During normal conditions, this pollutant was at its highest levels (28–30 µg m–3) in the central areas of the city, while it was less prominent (8–21 µg m–3) in the residential parts of the city (Fig. 3(e)). During the quarantine, NO2 varied from 3 to 8 µg m–3, with the minimum concentrations in the residential areas of Quito (Fig. 3(i)). Similarly, high reductions were observed for SO2 in all urban areas due to the quarantine measures (Figs. 3(f) and 3(j)). During February of 2020, the concentrations of SO2 varied from 1.8 to 5.1 µg m–3, with peak concentrations near the thermoelectric power plant, in the southern valley of the city (Fig. 3(f)). In Quito, southeasterly winds prevail, due to the equatorial easterlies moving around an old Ilalo volcano, on the east side of the city and encountering the Pichincha volcano on the west side. Therefore, SO2 concentrations consistently decrease moving northwards away from the power plant. Even during the quarantine, the highest concentrations of SO2 were found near the power plant (2.9 µg m–3) and decreased northwards (0.5 µg m–3) (Fig. 3(j)). The reduction of SO2 during the quarantine was approximately 50%, which may be due to the diminished electricity use and also reduced emissions from public transportation, the principal pollution source in this urban area (Zalakeviciute et al., 2017, 2018b).

As previously discussed (Fig.3(c)), the reduction of PM2.5 concentrations due to the quarantine measures was smaller compared to the gaseous pollutants. This may be explained by the increased solar radiation causing windier conditions during the second and third weeks of the quarantine. Even with a great reduction in transportation, there were elevated PM2.5 concentrations in the second and third weeks of quarantine (Fig. 2(c)). During the last week of quarantine, the PM2.5 concentrations decreased as there were more precipitation events accompanied by stricter private vehicle regulation (Fig. 2(d)). The highest concentrations during February occurred in the outskirts of the city in the industrial districts (24 µg m–3) (Fig. 3(g)), as previously reported (Zalakeviciute et al., 2018a). During the quarantine, those areas were also more polluted (14 µg m–3), although at much lower levels (Fig. 3(k)).

Finally, the concentrations of CO decreased from 0.49–0.85 mg m–3 during February to 0.34–0.44 mg m–3 during the first four weeks of quarantine (Figs. 3(h) and (l)). This lesser change may be due to the relatively high global background levels of CO (Miller, 2015) upon which is superimposed local CO levels. This also helps explain the low spatial variability of this pollutant across the city. In general, CO levels were highest around the central traffic-busy areas of the city.

NO2 and SO2 Satellite Data for Ecuador

Satellite data for Ecuador are presented for NO2 and SO2 one week before the COVID-19 quarantine and during the first two weeks of the quarantine in Fig. 4. Here we aimed to study the spatial evolution of the air pollution in relation to the implementation of the protective measures in the country. For both pollutants, the concentrations were reduced during the quarantine in both the major cities: Guayaquil and Quito. Similar pollution behavior was reported in 10 cities in China where, due to the pandemic, there was a restriction in mobility and industry, with a considerable decrease in NO2 and SO2 concentrations (Wang et al., 2020). Likewise, it is again confirmed that NO2 demonstrated a greater decrease in concentrations due to the cessation of transportation activities. The same was seen in the studies by Zheng et al. (2019) and Wang et al. (2020), where NO2 change was reported due to the reduction of combustion activities, including transportation.

Fig. 4. Satellite images of NO2 (a–b) and SO2 (d–f) levels for Ecuador one week before the COVID-19 quarantine 09–15 March 2020 (a, d) and during the first week 16–22 March 2020 (b, e) and second week 23–30 March 2020 (c, f) of quarantine.Fig. 4.
 Satellite images of NO2 (a–b) and SO2 (d–f) levels for Ecuador one week before the COVID-19 quarantine 09–15 March 2020 (a, d) and during the first week 16–22 March 2020 (b, e) and second week 23–30 March 2020 (c, f) of quarantine.

As discussed before (Section 4.1), the nationally mandatory measures were applied very efficiently in Quito from the first day of quarantine (March 17, 2020). However, it took about a week to completely shut down the activities in the similarly sized port city Guayaquil (Fig. 4). These differences were reflected in the NO2 and SO2 levels which decreased rapidly as epidemic isolation measures were implemented in Quito, but not as rapidly in Guayaquil (Fig. 4). This lag in the application of social distancing measures caused a rapid increase in COVID-19 cases in this port city, while the capital city had a much lower growth of infections. The higher number of cases in the port city may have considerable health implications, not only due to the spread of the disease, but also due to the poorer air quality, which is an aggravator of COVID-19 (Wu et al., 2020). There are some preliminary studies suggesting horrific statistics for Guayaquil, possibly the worst in the world to this date, highlighting the damage that this virus can do in developing world (Cabrera and Kurmanaev, 2020). 


In this work the improvement of urban air quality due to the COVID-19 mitigation measures was investigated for the first time in a Latin American country. As the numbers of the COVID-19 infection cases started accelerating in Ecuador, a series of extremely strict quarantine measures, focused on social distancing and isolation, were progressively implemented in the country starting March 17, 2020. While these measures were immediately implemented in the capital city Quito, there were delays in full implementation in the port city Guayaquil due to public protests and disrespect of the rules.

The time series of the 24-hour data for NO2, SO2, PM2.5 and CO in seven sites in Quito during January 1–April 12, 2020 showed a clear reduction of pollutant concentrations during the four weeks of quarantine. The comparative four-week analysis, before and during quarantine, exhibited one of the most significant globally reported reductions of NO(–68%), SO2 (–48%), CO (–38%) and PM2.5 (–29%) during the first month of quarantine in Quito. This is a clear demonstration of the effect on urban air quality of extremely strict reduction in anthropogenic activities. Although implemented measures were gradually stricter, there was no steady decreasing trend in the measured pollutants. In addition, PM2.5concentrations displayed more variability due to the variable and windy conditions associated with dust resuspension.

The spatial distribution maps identified the zones that are more affected by pollution reduction. Central areas of the city show the highest concentrations of NO2 and CO before and during the quarantine, although the levels are visibly reduced during the pandemic. The concentrations of PM2.5 also show the biggest reduction in the city outskirts in the industrial areas, and similarly, SO2 shows a large overall reduction, including the zone near the thermoelectric power plant.

Finally, comparative analysis of satellite data for Ecuador before and during the quarantine shows the differences in the spatial evolution of air pollution in relation with the implementation of the protective measures in the country. It can be noted that the NO2 and SO2 levels decreased rapidly in Quito and lagged in Guayaquil, due to the less efficient implementation of epidemic isolation measures. The lag in Guayaquil could have a considerable cost to the mortality rate in the port city, not only due to the spread of the disease, but also due to the poorer air quality in the port city.  


Funding for this study is provided by the Universidad de Las Americas, Ecuador as a part of an internal research project AMB.RZ.20.01.


 There are no real or perceived financial conflicts of interests for any author.


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Aerosol Air Qual. Res. 20 :1783 -1792 . https://doi.org/10.4209/aaqr.2020.05.0254  

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