During the COVID-19 lockdown, large industries in the Russian Arctic region were closed for two months, leading to a significant reduction in anthropogenic aerosol emissions. This decline in aerosols resulted in a decrease in the human-made aerosol cooling effect. The strict lockdown measures implemented after 18 March 2020 caused a drastic downward fall in considered aerosols. Consequently, there was an impact on air temperature, with temperature differences exceeding 3 K in November and February, while clear-sky top net solar flux values were greater than 13 W m−2. Throughout the lockdown period, the Russian Arctic's annual area average sea ice concentration was 7.72% in 2019 and 7.64% in 2020. The decrease in radiation-scattering pollutants contributed to an increase in global warming. Some pollutants, like sulfur, carbon dioxide, and methane, produced a cooling effect by mitigating greenhouse gases, which could affect the speed of sea ice melt. However, due to the short duration of the pandemic, it remains challenging to determine whether the aerosol changes accelerated or decelerated the sea ice melting process.

  • COVID lockdown resulted in a drastic drop in the amount of anthropogenic aerosol emitted over the Russian Arctic.

  • Arctic haze was experienced during April 2020.

  • The decline in aerosol emissions, black carbon, and sulfur dioxide led to reductions in total aerosol cooling.

  • Net solar radiation flux showed values greater than 13 W m−2 during lockdown.

  • No significant effect of anthropogenic activities on the sea ice condition was observed.

The two polar regions, the Arctic and Antarctic, significantly influence the climate across the entire globe. These areas appear to have an impact on the sea level (Dasarathy et al. 2021), wildlife coupled with numerous food chains, traditional human livelihoods, tundra vegetation, and natural ecosystems with excess productivity (Aas et al. 2019). The sea levels are altered when the snow over the land melts and also by the process of desalination. Accurate sea level estimation is important for designing effective intake systems, optimizing energy efficiency, and ensuring the protection of desalination plants from coastal flooding (Panagopoulos 2022). It also helps in managing salinity levels and preserving the quality of freshwater sources. Additionally, sea-level estimation guides long-term planning and investment decisions for desalination infrastructure in coastal areas (Panagopoulos & Giannika 2022). While comparing the two poles, it is often found that the Arctic Circle is more vulnerable to global warming compared with the Antarctic (Jang et al. 2022). One of the primary reasons for this could be the presence of human settlement in the Arctic (Allen 2020). The presence of human activity in the region causes the emission of hazardous aerosols (Sakib 2023), and these aerosols either absorb or reflect the incoming solar radiation into the atmosphere (Carslaw 2022). This process can lead to global warming when there is more absorption than reflection of this radiation (Vihma 2014). Global warming has caused greater shrinking (Duan et al. 2022) and thinning (Kwok et al. 2011) of Arctic sea ice during the recent decade (Kay et al. 2011). Since the modern satellite era began in 1979, researchers have observed a decline of 9.1% of sea ice per decade (Shibata et al. 2013), which was just 7.8% per decade during the pre-1979 period (Stroeve et al. 2012). However, the decline is higher (12.6% per decade) in recent years (2009–2019) (Wunderling et al. 2020). Hence, it is understood that the region demands more attention and scientific study.

Further, in 2020 as well, the decline in sea ice is found to prevail. During the beginning of this year, the outbreak of COVID-19 occurred, which caused major lockdowns across the globe. The lockdown impacted all sectors of society, ranging from economics to the environment, either directly or indirectly (Muhammad et al. 2020; NASA Global Climate Change 2022). Over the Arctic, pollution levels have decreased, which has greatly improved the air quality while reducing the amount of soot and other particles settling on the sea ice. However, over the Arctic, a rise in temperature was witnessed during the period, which accelerated the melt and decelerated the evolution of sea ice. During the recent decade, the region is already found to have experienced higher rates of warming temperature compared with the global average, a phenomenon also referred to as Arctic amplification (Screen & Simmonds 2010). The Arctic region is observed to have few sources of anthropogenic emissions, and additionally, there exists a long-range transport of aerosols from mid-latitudes to the poles that makes the presence of these emissions more intense (Screen et al. 2012; Cohen et al. 2014). The transported aerosol is often referred to as ‘Arctic haze’. A decline in aerosols lowers the cloud drop, resulting in a greater presence of low and dimmer clouds (Ekman & Schmale 2022), further leading to an increase in precipitation (Bintanja & Selten 2014), and thereby changing the lifetime of clouds (Albrecht 1989). Furthermore, reducing anthropogenic emissions would reverse the planet-cooling effect (Yadav et al. 2020), affecting the cloud properties as these particles have the ability to scatter back the incoming solar radiation (Im et al. 2021). Further, it is understood that during the 1980s and 1990s, changes in the extent of cloud cover caused cooling during summers and reduced warming in winters, through the radiative effect (Liu et al. 2012). Uncertainty about cloud properties has always prevailed over the North Pole (Kato et al. 2018). Accuracy about the behavior of polar clouds always helps in understanding the radiation happening at the top of the atmosphere, which further governs the polar climate system (Li et al. 2022).

According to Yang et al. (2020) and Diamond & Wood (2020), preliminary findings from the early lockdowns in China and Russia suggest that the decrease in aerosols during this time may have led to minor changes in cloud microphysics. The major decline of these aerosols was due to the most polluted industries (Aerosol Pollution 2022), which caused a short-term effect on temperature. Furthermore, as noted by Gettelman et al. (2020), some types of air pollution can have a cooling effect on the planet by reflecting sunlight back into space or by reducing the amount of incoming solar radiation that reaches the Earth's surface (Kok et al. 2023). Therefore, reducing pollution could have the opposite effect and lead to the warming of the planet (Gagné et al. 2015). Likewise, the impact of aerosol emissions on global temperatures is particularly significant in areas with high levels of pollution, resulting in warming of up to 0.37 °C across significant areas of the United States and Russia. Therefore, there exists a gap which needs to be addressed over the region.

The study of variability in sea ice due to induced emissions gives a unique opportunity for climate change research as it allows scientists to examine the impact of reduced human activities on the Arctic environment. By analyzing the fluctuations in sea ice during this period, researchers can gain valuable insights into the relationship between emissions and Arctic sea ice decline, aiding in the refinement of climate models and predictions. Additionally, understanding these variabilities helps evaluate feedback mechanisms, such as the albedo effect, where melting sea ice leads to increased heat absorption, further accelerating ice loss and contributing to climate change (Stroeve & Notz 2018). This knowledge can guide policy decisions and mitigation strategies by highlighting the benefits of long-term emission reduction and sustainable practices. Furthermore, the socioeconomic implications of sea ice changes in the Arctic are significant, affecting indigenous communities and biodiversity (Serreze & Barry 2011). Overall, studying the sea ice variability during the 2020 lockdown provides crucial insights into the intricate interactions between human activities, emissions, climate change, and Arctic ecosystems, informing global efforts to mitigate climate change and safeguard vulnerable regions. Therefore, the goal of this paper is to carry out a preliminary spatiotemporal analysis of the sea ice condition during the COVID-19 pandemic in the Russian Arctic region. The effect of emissive aerosol particles on sea ice conditions in the region is closely studied for the years 2019 and 2020. The Russian Arctic is considered to be the region of interest as there exists human intervention with the presence of sea ice.

The year 2019 is considered so as to understand the situation of the sea before the lockdown. Temperatures rise during the pandemic, even though man-made emissions are expected to be low. The region is carefully selected in order to comprehend the land-related effects that cause a reduction in the reflection of incoming solar radiation back into space, ultimately altering the temperature of the air above it. This study highlights the influence of various kinds of emissions from numerous sources, like power plants, motor vehicles, industrial facilities, etc. Additionally, outgoing radiation is also observed as these aerosols are seen to be in direct contact with them. The impact of these on clouds and the potential of it to reflect radiation back into the atmosphere are understood. However, there are other greenhouse gases, such as carbon dioxide, that have a reverse effect: they trap warm air near the land surface and cause a temperature hike.

Datasets

This paper consists of three variants of datasets: atmospheric variables, atmospheric aerosols, and cryospheric variables.

Atmospheric variables

To study the meteorological shift over the Russian Arctic region (Figure 1), atmospheric variables comprising the air temperature above 2 m and clear-sky top net solar shortwave radiation at the top of the atmosphere (TOA) are considered. Both the datasets are derived from the ERA-5 ECMWF reanalysis (users can find the dataset at https://doi.org/10.24381/cds.adbb2d47) with a spatial resolution of 0.25° × 0.25° at a time interval of one month. The term ‘air temperature above 2 m’ is the temperature of the air at a height of 2 m over land, water, or inland waters. This parameter is measured in kelvin (K). Another parameter, the clear-sky top net solar shortwave radiation at the top of the atmosphere (TOA), also referred to as shortwave radiation, is received from the sun at the top of the atmosphere. It refers to how much radiation is transmitted over a horizontal plane. Depending on the data gathered, a specific time period is used to accumulate this parameter. Joules per square metre (J m−2) is the general unit. To convert it to watts per square metre (W m−2), overall statistics (value) is divided by the accumulation period.
Figure 1

Region of interest: (a) the Arctic region and (b) the Russian Arctic region with coordinates 10°E–170°E and 40°N–84°N, which is a subset of the Arctic region.

Figure 1

Region of interest: (a) the Arctic region and (b) the Russian Arctic region with coordinates 10°E–170°E and 40°N–84°N, which is a subset of the Arctic region.

Close modal

Atmospheric aerosols

For the current study, aerosols like ammonia (NH3), black carbon (BC), carbon dioxide (CO2), carbon monoxide (CO), sulfur dioxide (SO2), organic carbon (OC), nitrous oxide (N2O), and non-methane volatile organic compounds (NMVOCs) are considered and are extracted from Community Earth System Model version 2 (CESM2) (Danabasoglu et al. 2020). The model is coupled ocean–sea-ice–atmosphere–land configuration at 1° horizontal resolution. Later, two sets of simulations: one with historical aerosol emissions from 1979 to 2020, and one with reduced aerosol emissions during the 2020 lockdown based on satellite observations, are performed. Daily data are available on the websites https://doi.org/10.5281/zenodo.3957826 and https://doi.org/10.5281/zenodo.3952959. Daily averages are a running seven-day mean that eliminates any weekday effects.

Cryospheric variables

As the considered region of study is closer to the North Pole (Arctic), the impact of atmospheric conditions on cryospheric parameters is crucial. For understanding the influence of the aforementioned atmospheric parameters on sea ice conditions, sea ice concentration (hereafter referred to as SIC) and sea ice thickness (hereafter referred to as SIT) are considered. SIC values are from the CEDA Archive: AMSR-E and AMSR-2 at spatial resolution of 0.25° × 0.25° (https://catalogue.ceda.ac.uk/uuid/1dcb79727b313a281233afc3c3e10519) (Hadley Centre for Climate Prediction & Research 2007). SIT datasets are derived from CryoSat-2 and Envisat with a spatial resolution of 0.25° × 0.25°. SIT error is estimated to be between 0.04 and 0.06 m (Table 1).

Table 1

Validation of sea ice parameters with their R, biases, and RMSE

VariableRetrieved fromValidation with*RBiasRMSE
Sea ice concentration (SIC) (%) CEDA Archive: AMSR-E and AMSR-2 DMSP-F8 SSM/I (NSIDC) 0.99 3 ± 0.51 3–5 
Sea ice thickness (SIT) (m) CryoSat-2 and Envisat ICESat (Kwok 2018NA 0.14 ± 0.51 0.04–0.06 
VariableRetrieved fromValidation with*RBiasRMSE
Sea ice concentration (SIC) (%) CEDA Archive: AMSR-E and AMSR-2 DMSP-F8 SSM/I (NSIDC) 0.99 3 ± 0.51 3–5 
Sea ice thickness (SIT) (m) CryoSat-2 and Envisat ICESat (Kwok 2018NA 0.14 ± 0.51 0.04–0.06 

*DMSP – Defense Meteorological Satellite Program-F8, -F11, and -F13, SSM/Is – Special Sensor Microwave/Imagers (SSM/Is), and the DMSP-F17 Special Sensor Microwave Imager/Sounder (SSMIS), ICESat – Ice, Cloud, and land Elevation Satellite.

Methodology

In this paper, the Russian Arctic region with coordinates 10°E–170°E and 40°N–84°N is considered. The reason for considering this area is to understand the influence of lockdown on the sea ice condition near places where there is human intervention (as the region is closer to land). Atmospheric variables, air temperature above 2 m and solar shortwave radiation at the top of the atmosphere (TOA), are extracted month-wise for the years 2019 and 2020. Many researchers in the past have used different criteria to divide seasons (Wang et al. 2019). In this paper, December–February, March–May, June–August, and September–November are classified as winter, spring, summer, and autumn, respectively. The year 2019 gives the condition of the atmosphere during the pre-pandemic period, and the year 2020 represents the period during the pandemic (or, in other words, when the lockdown was implemented over the considered region). Initially, year-to-year variability in air temperature over the Russian Arctic is investigated. Trends for the years 2016–2021 have been computed so as to understand the general behavior of the parameter over the region. The paper thoroughly displays all of the examined characteristics of the air temperature at 2 m in the form of color maps. Differences in the seasonal spatial average are also measured to validate the difference between the two timeframes, 2019 and 2020, and the equation is given below:
(1)
Similarly, the seasonal spatial and temporal averages of solar shortwave radiation are also calculated, with a pie chart displaying the differences between the two years. Here, the difference is calculated as a percentage in order to understand the significance of the change in value and the percentage deviation is calculated using the formula:
(2)
where is the observed value and is the expected value.
For the aerosol emission data extracted from the aforementioned websites, the monthly variability of Arctic haze for the span of 2000–2020 is observed. Daily difference is calculated for the span of 1 January 2020 to 31 August 2020 (based on the availability of the data), along with the composition of aerosol during the date of mass intrusion (Russell 1988). The daily difference is calculated using the formula:
(3)
where is the amount of aerosol that is found on the current day and is the amount of aerosol present during the previous day.

The available data have already been simulated for COVID-19 perturbations. The data consisted of temperature nudging because it was collected on the ground. However, Forster et al. (2020) have tried removing and controlling the role of temperature on these parameters. For the current study as well, the daily averages for the considered domain are calculated, and for the daily difference between them, the present-day emission value is subtracted from the past day. This way, the decline or rise in value with respect to each day could be understood. Additionally, the Sea-Ice–Aerosol–Cloud Feedback (SIACF) Index in S. M. Nazmuz Sakib's Hypothesis can be applied to the aerosol emission changes. The SIACF Index serves as a quantitative measure to assess the influence of aerosol emission variations on sea ice conditions (Sakib 2023).

The Arctic cryospheric variables SIT and SIC are extracted for the monthly timeframe from the aforementioned sources for the years 2019 and 2020. The region is then constrained and cropped to the chosen region of interest. As per standard practice, SIT and SIC are replaced with zero (‘0’) in the grid wherever the values are missing or ‘NaN’ (undefined), as the absence of sea ice corresponds to zero thickness and concentration. Later in the case of SIT, the months March and April are considered, and for SIC, the months March, April, May, and June are considered. Monthly averages are considered for both parameters. Later, the differences are analyzed to understand the extent of change in sea ice conditions during the years 2019 and 2020. The spatial differences between SIT and SIC are illustrated in the paper.

Spatiotemporal variability in air temperature over the Russian Arctic region

The monthly variation in temperature over the Russian Arctic region is clearly based on seasonal classification. Winters (December, January, and February) have the lowest temperature, followed by spring (March, April, and May), and the highest is during summer (June, July, and August). Again, by autumn (September, October, and November), the temperature change is lower when compared with that during the previous stage, summer. Although the temperature gradually rises in the spring, it can still be extremely frigid. The hottest season is summer, which features higher temperatures and longer daylight hours. Autumn comes after summer, and while the temperature drops, the transition may be less pronounced than in other areas. The Russian Arctic has a wide variety of temperatures, with winter being the coldest and summer being the hottest.

From Figure 2, it is evident that during the year 2020 (during the COVID-19 pandemic lockdown), the air temperature over the Russian Arctic region is significantly higher by ∼2 K. Strict lockdowns were imposed in Russia between March and June 2020. The months January, February, May, June, September, October, November, and December 2020 have air temperatures greater than those compared with past years (in this case, 2016–2019). According to researchers, 2020 has been recorded to have the highest mean air temperature during the past five years, post-2015, despite the year experiencing a cooling La Nina event (Yagodin 2021). During the course of the study, different regions were randomly analyzed to see the alteration in temperature. As one would generally contemplate, during the pandemic, the majority of countries were experiencing lockdowns that restricted the emission of harmful greenhouse gases from automobiles, factories, etc., thereby inhibiting or slowing down the rise in global temperature. However, based on the observations, this was not the case. The temperature change between 2020 and 2019 clearly shows a significant rise over the considered region. Recent articles prove that warming has increased by 0.37 °C over the United States and Russia alone (mentioned in the Introduction section). Further, to quantitatively validate the increase in temperature during the pandemic, this timeframe is compared with the pre-pandemic situation of 2019 and is represented in Table 2. The highest temperature difference between the two periods is observed in the months of February (ΔT = 3.23 K) and November (ΔT = 3.55 K), with ΔT > 3 K, followed by January (ΔT = 2.16 K) (from Table 2). Such a rise in temperature clearly indicates the significance of understanding the reason behind such a trend. The lockdown imposed halted the entire world, and most importantly, it hampered the functioning of huge factories that emitted harmful substances. However, there would have been various causative factors for such a rise in air temperature. It may be due to: (1) excess incoming solar radiation (excess heating of the atmosphere): when excess solar radiation enters the Earth's atmosphere, it heats up the Earth's surface, which in turn warms the air above it. This causes the air to expand and rise, creating areas of low pressure. As the warm air rises, it cools and releases its moisture, resulting in cloud formation and precipitation. (2) Differential heating of the water and land: energy to raise its temperature by a certain amount compared with the land. As a result, water takes longer to heat up and cool down than land. This causes differences in the heating and cooling rates of adjacent land and water surfaces. (3) Declining air quality (burning of organic materials). As air quality declines, the concentration of these greenhouse gases can increase, which can lead to a warming of the planet's surface temperatures. (4) Other meteorological factors (such as ocean currents and prevailing winds).
Table 2

Temperature difference between pre-pandemic (2019) and pandemic (2020) years (SD: standard deviation)

MonthsT2020T2021ΔT(2020–2019) (K)
Jan 258.69 255.20 2.16 
Feb 261.15 256.86 3.23 
Mar 264.62 261.83 0.17 
Apr 271.77 270.65 0.62 
May 278.73 278.29 1.13 
Jun 284.33 284.36 0.11 
Jul 286.59 286.78 0.62 
Aug 285.60 285.64 0.27 
Sep 281.99 280.28 1.30 
Oct 274.61 272.99 0.81 
Nov 267.44 264.32 3.55 
Dec 258.58 257.63 −0.52 
SD 10.63 11.84 1.26 
MonthsT2020T2021ΔT(2020–2019) (K)
Jan 258.69 255.20 2.16 
Feb 261.15 256.86 3.23 
Mar 264.62 261.83 0.17 
Apr 271.77 270.65 0.62 
May 278.73 278.29 1.13 
Jun 284.33 284.36 0.11 
Jul 286.59 286.78 0.62 
Aug 285.60 285.64 0.27 
Sep 281.99 280.28 1.30 
Oct 274.61 272.99 0.81 
Nov 267.44 264.32 3.55 
Dec 258.58 257.63 −0.52 
SD 10.63 11.84 1.26 
Figure 2

Temporal variability in temperature for 2016–2021.

Figure 2

Temporal variability in temperature for 2016–2021.

Close modal
Figure 3 shows the spatial variation of air temperature for the months of March and April for pre-pandemic (2019) and pandemic years (2020). From the earlier section, it is known that the major difference in temperature is observed in the months of January and February; however to understand the persistent change in the variation of the parameter, the next two months, March and April, are selected. During March 2019, the region to the north, near the Arctic, is seen to have lower air temperatures than the continental region, which is expected due to the latitudinal variation. When comparing the month of March, it is clear from Figure 3(a) and 3(b) that the Laptev Sea has gained a significant amount of temperature in 2020 compared to 2019. Similarly, in the region toward the north, in the Arctic, the areas around Svalbard and Franz Josef Land have again gained temperature during the pandemic and pre-pandemic, right from the beginning (March). Further, while observing the month of April, the entire region to the right of the Laptev Sea has gained more heat during 2020 than that observed during 2019. Additionally, the region beneath the Barents Sea (land region) has also reached higher temperatures in 2020 than the previous year. From the spatial plots (Figure 3), it is evident that the increase in air temperature is visible not only in the temporal domain but also in the spatial (xy) plane.
Figure 3

Spatial distribution of temperature (K) for (a) March 2019, (b) March 2020 and (c) April 2019, (d) April 2020.

Figure 3

Spatial distribution of temperature (K) for (a) March 2019, (b) March 2020 and (c) April 2019, (d) April 2020.

Close modal

Spatiotemporal variability in top net solar radiation–clear-sky net shortwave flux at TOA

In addition to air temperature, clear-sky net shortwave flux is studied because it is an important component of the Earth's radiation budget, and it plays a key role in determining the amount of energy that is available to drive the Earth's climate system. Figure 4 shows the spatial variability in net solar radiation over the considered domains for the months of June and July for the years 2019 (pre-pandemic) and 2020 (post-pandemic). Similar to the air temperature spatial plot in Figure 3, the solar radiation flux also shows distinct variability over two years, which is represented in Figure 4. The months of June and July are used in this study to examine the long-term effects of lockdown over a prolonged period of time. During June (Figure 4(a) and 4(b)), the land region (Russia) remains almost the same for the years 2019 and 2020. Some seas, however, such as the Kara and Laptev, exhibit extreme variability. In June, the sea ice conditions over Kara and Laptev are particularly vulnerable due to variations in atmospheric and oceanic environments, which can have a substantial impact on the overall extent and thickness of the ice cover. The changes in water bodies due to wind patterns or ocean currents can cause the ice to break up or move, leading to a reduction in overall ice extent. Similarly, changes in temperature or atmospheric pressure can affect the melting or freezing of the ice, which can also contribute to changes in overall ice condition. Additionally, the flux in the Kara Sea is expected to be significantly higher in 2020 than in 2019. Kara, which had traces of flux ranging from 7 to 8.5 W m−2, has completely intensified to a flux greater than 12 W m−2. The intensity of the flux during July (Figure 4(c) and 4(d)) is found to be lower compared with that in June for both 2019 and 2020. From Figure 4(d), it is clearly evident that the entire region around Svalbard, Franz Josef Land, and the Laptev Sea has gained more flux in 2020 compared with the pre-pandemic year 2019. In general, the radiation is seen to be more concentrated on the continental side (the Russian side) than the water side (Arctic side). When considering the difference between the two years in June, it is observed that in the latter year there was more radiation absorbed from the atmosphere compared with the previous year. The Barents Sea, which lacked higher measures in June 2019, is seen to have radiation exceeding 13 W m−2. Similarly, the higher limits of solar radiation are expected to extend further north in July 2020 than in July 2019. Such fluctuation in the net solar radiation is not only because of the radiation exerted by the sun. The months of June and July are specifically chosen to investigate the ongoing change in the nature of the parameter after the world has been locked down. It was after March when the majority of the countries implemented mandatory lockdowns that restricted the use of automobiles. Large manufacturing companies were also put on high alert because the supply chain had not been in full swing for a limited time.
Figure 4

Spatial distribution of clear-sky top net solar radiation–shortwave flux at TOA (W m−2) for months (a) June 2019, (b) June 2020 and (c) July 2019, (d) July 2020.

Figure 4

Spatial distribution of clear-sky top net solar radiation–shortwave flux at TOA (W m−2) for months (a) June 2019, (b) June 2020 and (c) July 2019, (d) July 2020.

Close modal

The extent and the amount of aerosols emitted over the region is analyzed daily in the upcoming section. The validation of the extent of the difference in the net solar radiation between the two timelines is provided in Figure 4 based on the temporal frame. During February 2019, the average solar radiation is 2.09 W m−2 and that during February 2020 is 2.14 W m−2, making the difference ΔS = 0.04 W m−2. The lowest solar radiation is observed during this month, ultimately causing the month to experience winter. Further, in March 2019 and 2020, the value of net solar radiation is seen to be twice that of February. The hike in incoming solar radiation also marked the onset of spring. The amount of solar radiation received during the years 2019 and 2020 is represented in Table 3 along with the differences. Table 3 shows that by the beginning of summer, in June, ΔS = 0.15 W m−2. Later in July, we see lower net solar radiation than the previous month, ΔS = 0.06 W m−2.

Table 3

Clear-sky top net solar radiation–shortwave flux (W m−2) at TOA difference between pre-pandemic (2019) and pandemic (2020) years (SD: standard deviation)

MonthsS2019S2020ΔS(2020–2019)
Feb 2.09 2.14 0.05 
Mar 4.03 4.12 0.09 
Apr 6.87 7.00 0.13 
May 9.92 10.21 0.29 
Jun 12.35 12.50 0.15 
Jul 12.17 12.23 0.07 
SD 4.29 4.32 0.09 
MonthsS2019S2020ΔS(2020–2019)
Feb 2.09 2.14 0.05 
Mar 4.03 4.12 0.09 
Apr 6.87 7.00 0.13 
May 9.92 10.21 0.29 
Jun 12.35 12.50 0.15 
Jul 12.17 12.23 0.07 
SD 4.29 4.32 0.09 

Overall, as shown in Figure 5(a) and 5(b), there is a significant increase in the radiation trapped at the top of the atmosphere when compared with the pre-pandemic period. Apart from the temporal profile, which shows the difference in the solar flux from February to July for the years 2019 and 2020, the pie chart beside it shows the percentage difference of the 2019 solar flux from the 2020 solar flux. During February, the difference in solar flux during the pandemic from pre-pandemic is seen to be the least, with a value of 6.36%. By March, it has risen slightly to 12.09%. Further on in April, the difference becomes 16.29%. The highest recorded difference in solar flux is observed in the month of May, with a value of 37.15%. Later, it is seen decreasing to 19.63% in June, followed by 8.48% in the month of July.
Figure 5

(a) Temporal variability of clear-sky net shortwave flux at TOA (W m−2) along with percentage (%) deviation and (b) percentage difference for months February–July during the years 2019 and 2020.

Figure 5

(a) Temporal variability of clear-sky net shortwave flux at TOA (W m−2) along with percentage (%) deviation and (b) percentage difference for months February–July during the years 2019 and 2020.

Close modal

From the observations, it is evident that temperature and absorption of solar radiation inside the Earth's atmosphere have gone up significantly during the lockdown. One of the main reasons for such a trend is the presence of greenhouse gases. Greenhouse gases and water vapor trap heat and prevent it from escaping into space, leading to a rise in temperature inside the atmosphere. With the closure of industries, there was a decrease in the use of energy derived from fossil fuels, leading to a reduction in greenhouse gas emissions during the COVID-19 lockdown. Therefore, the nature and presence of aerosols need to be examined in the upcoming sections.

Temporal variability in aerosol emissions during pandemic lockdown over the Russian Arctic

Aerosols with larger particle sizes are seen in the lower atmosphere, obstructing visibility by scattering sunlight. At higher altitudes, however, indirect scattering occurs due to the difference in size of cloud particles. According to the preceding sections, the air temperature at 2 m and the amount of solar radiation trapped in the atmosphere significantly increased during the pandemic period of 2020. Therefore, to understand the causative factor of this trend, the aerosols are analyzed in this section. Apart from the aerosols present over a region, some aerosols are transported through wind and are found settling over the Arctic region, also called the ‘Arctic haze’. These events can release large amounts of smoke, dust, and ash into the atmosphere, which can be transported to the Arctic and contribute to the haze. This haze primarily consists of sulfur dioxide, nitrogen oxides, and BC resulting from human activities such as industrial processes, transportation, and energy production. The lifecycle of the haze along with the mass through the atmospheric column over the Russian Arctic region is illustrated in Figure 6(a). The aerosols (surface and mass-wise) are at their maximum during March, when the sea ice is at its maximum. The column substance (mass) restricts the amount of sunlight reaching the ice, thereby affecting the composition of the ice. However, the pollutants which are deposited on the ice surface have the ability to alter the reflectivity of the ice, making it more susceptible to melting. From Figure 6(a), it is evident that the Arctic haze is an annually recurring phenomenon, which is the most common during the winter months when there are less sunlight and low temperatures. During the year 2020 (the pandemic year), the Arctic haze was experienced over our region of interest during mid-April 2020 (15–17 April 2020) (Dada et al. 2022), and the fractional contributions of the different mass components during this period are depicted in Figure 6(b). The presence of cyclic Arctic haze over the region, coupled with already existing aerosols, alters the air temperature over the region. From Figure 6(c), it is visible that the mass of the aerosol over the Russian Arctic region is found to be higher than that over the Arctic Circle (Schmale et al. 2022).
Figure 6

(a) The Russian Arctic haze lifecycle – anthropogenic long-range-transported aerosol during 2000–2020; (b) the warm air-mass intrusion event. Pie chart showing the % contribution of each aerosol to the total PM1 (particle size with diameter smaller than 1 µm) during 15–17 April 2020; (c) whisker plot showing the differences in the mass of the aerosols over the Russian Arctic region and Central Arctic region for the span of 20 years (2000–2020).

Figure 6

(a) The Russian Arctic haze lifecycle – anthropogenic long-range-transported aerosol during 2000–2020; (b) the warm air-mass intrusion event. Pie chart showing the % contribution of each aerosol to the total PM1 (particle size with diameter smaller than 1 µm) during 15–17 April 2020; (c) whisker plot showing the differences in the mass of the aerosols over the Russian Arctic region and Central Arctic region for the span of 20 years (2000–2020).

Close modal

The range of Arctic aerosol mass lies between 0.09 and 0.76 μg m−3, and over the Russian Arctic, it lies between 0.34 and 1.01 μg m−3. This is primarily due to the presence of human activities such as industrial processes, transportation, and energy production in the region. The Russian Arctic is home to several industrial centers and oil and gas fields, which can release significant amounts of aerosol and other pollutants into the atmosphere. In addition to human activities, the geography and weather patterns of the region may also contribute to higher aerosol concentrations over the Russian Arctic. The region is surrounded by mountains (from the topographic plot in Figure 1), which can trap pollutants in the air, and it experiences frequent weather inversions that can prevent the dispersion of pollutants.

Further, the daily pattern of all the primary aerosols present over the region is analyzed. Total column sulfur dioxide (SO2) is found (Figure 7(a)) oscillating between high and low values during the initial phase (16–21 February 2020), where it remains positive. The daily difference soon becomes negative, reaches a value of −0.16 kt/day during 21–28 February. It is positive from 29 February to 6 March. Further, during 7–13 March, it again becomes negative. Later, during 14–18 March, it is again positive. After 19 March 2020, the daily difference is negative thereafter, with the highest negative difference observed on 3 April 2020, with a daily difference value of −1.51 kt/day. With the lifting of the lockdown, the daily difference is gradually seen to be increasing. The Intergovernmental Panel on Climate Change (IPCC) has already recognized SO2 as an active participant in controlling and initiating global warming. This is because the aerosol can react with water droplets in the air, resulting in acid rain (sulfuric acid). However, when the very same aerosols reach the stratosphere and remain there for several weeks, they produce sulfate aerosols. These aerosols act as artificial cooling agents. Additionally, the region under study is known to be the second largest country producing ammonia after China. Russia is recorded to have manufactured ∼19.9 million metric tonnes of NH3 in the year 2021. Ammonia (NH3) is mainly found in land and water; however, it is also proven that it is retained in the atmosphere for almost a week. The major source of this compound is the soil, through bacterial processes or decomposition. Researchers in the past have already noted the positive correlation between temperature and NH3 emissions (Hafner et al. 2019). It is not only that a decrease in NH3 causes a decrease in temperature; it is also found the other way around. Temperature increases have also been shown to increase the amount of NH3. An increase in temperature of 2 or 4 °C is found to increase NH3 by 10% and 20%, respectively. Figure 7(b) shows the daily profile of NH3 over the Russian Arctic region. This plot depicts the daily difference in NH3 having a positive and negative fluctuation during the 16 and 17 of February, indicating that there have been highs and lows in NH3 values during the initial spans (16 February through 21 February show a positive trend, 22–28 February show a negative trend, 29 February through 6 March show a positive trend, 7–13 March show a negative trend, followed by 14 March showing a negative trend). A steady decline in the aerosol is observed post-17 March. The highest negative difference is seen between 3 and 5 April 2020, with a value of −0.04 kt/day. However, after April, it is seen to gradually pick up its pace. This decline in NH3 during the spring (MAM) clearly indicated the hike in incoming radiation during the pandemic period compared with 2019, which has been discussed in the above section.
Figure 7

Daily Russian Arctic mean time series of differences due to COVID-19 lockdowns: (a) total column sulfur dioxide (SO2) and (b) total column ammonia (NH3).

Figure 7

Daily Russian Arctic mean time series of differences due to COVID-19 lockdowns: (a) total column sulfur dioxide (SO2) and (b) total column ammonia (NH3).

Close modal
It is not only these two gases which dropped during the time of lockdown. Many other industrial emitted gases were significantly reduced during this time. The aerosols along with their daily rates are represented in Figure 8. Organic carbon (OC) initially remains positive until 19 March 2020 (Figure 8(a)). It has been declining since 20 March. Here, two daily minimum differences were observed, on 4 April and 6 May 2020, with a value of −0.02 kt/day for each of the considered days, after which, just like all other aerosols, OC is also seen to be rising. OC in the atmosphere mainly includes hydrocarbons, oxygenated compounds, halogenated compounds, and multifunctional compounds. OC is found to be deposited in the atmosphere or transported to long distances through stream flow. In the present case, it is primarily transported, as the naturally produced one was not hampered during the considered period. Instead, man-induced changes were halted. Further, the trend line of BC (Figure 8(b)) is also found to be the same as that of NH3, except for the fact that before 19 March, the difference in this aerosol remains positive. However, slight negative differences are observed between 22 and 28 February. Following 19 March, the greatest negative difference of −0.02 kt/day is observed during 3–5 April 2020, which is almost relatable to NH3. The size of BC particles varies from 10 to 104 nm.
Figure 8

Daily Russian Arctic mean time series of differences due to COVID-19 lockdowns: (a) total column organic carbon (OC), (b) total column black carbon (BC), (c) total column nitrous oxide, (d) total column carbon dioxide (CO2), (e) total column carbon monoxide (CO), and (f) non-methane volatile organic compounds (NMVOCs).

Figure 8

Daily Russian Arctic mean time series of differences due to COVID-19 lockdowns: (a) total column organic carbon (OC), (b) total column black carbon (BC), (c) total column nitrous oxide, (d) total column carbon dioxide (CO2), (e) total column carbon monoxide (CO), and (f) non-methane volatile organic compounds (NMVOCs).

Close modal

Nitrous oxide (N2O) also behaves in a similar fashion as SO2 (Figure 8(c)). N2O alternates between negative and positive values between 3 February and 8 March 2020. During the initial phase (3–15 February 2020), it remains positive. Later, from 16 to 21 February, it turns positive. From 22 to 28 February, the daily differences become negative. From 29 February to 8 March, it again becomes positive. Furthermore, it turns negative once more during 9–13 March. Later, from 14 to 17 March, it is once again positive. The daily differences continue to be negative after 18 March 2020. The lowest daily difference is observed on 4 April 2020, with a value of −0.11 kt/day. When this aerosol is exposed to sunlight and oxygen in the stratosphere, it gets converted to nitrogen oxide. Later, this has the potential to deplete the ozone layer nearly 300 times more than CO2. However, it has a shorter life span than CO2. Therefore, it is believed that even slight fluctuations in N2O can greatly contribute to global warming.

Further, CO2 and CO are also found to maintain a similar trend, which is well evident from Figure 8(d) and 8(e). There is a gradual decline in the month of March, followed by a steady situation post-April. The notable feature about these elements is that the daily difference of CO2 and CO lie within the tenth and unit place, respectively, whereas for NH3 and BC, the magnitude is quite small, occupying the hundredth and thousandth place values (position), respectively. CO2 absorbs energies with wavelengths ranging from 2 × 103 to 15 × 103 nm. This is also the range that overlaps with that of IR (infrared) radiation. The decline in this molecule further hampers the energy radiation budget. CO, like BC, follows a similar trend and remains positive until 18 March. Following 18 March, a gradual downward trend is observed, eventually reaching −8.35 kt/day in April 2020. However, it is alleged that CO does not have a direct effect on atmospheric temperature, like CO2 and methane. The NMVOCs (Figure 8(f)) behave somewhat similarly to OC. NMVOCs remain positive until 18 March 2020 (Figure 8(f)). Later, from 19 March onward, the aerosol shows a negative difference. This declining trend prevails thereafter. The lowest daily difference is observed on 4 April 2020, with a value of −3.14 kt/day.

Variability in SIT and SIC during the pandemic lockdown over the Russian Arctic

As the role of Arctic haze and its associated aerosols in altering the atmospheric conditions over the Russian Arctic region is now thoroughly understood, it is vital to assess the influence of these parameters on the sea ice conditions prevailing over the region. Significant atmospheric fluctuation occurred in 2020, and therefore, the differences in cryospheric parameters due to the difference in these variables are discussed in this section.

Recently, it was discovered that the Barents Sea experiences summers without ice. Figure 9 shows the difference in SIT between 2019 and 2020. From Figure 9(a) and 9(b), it can be seen that for both the months of March and April, the difference values mostly lie on the positive side. In March (Figure 9(a)), the region above the Russian landmass is observed to have a SIT difference ranging from 0 to 0.75 m. However, some regions around Svalbard, near Franz Josef Land and the Kara Sea, are seen to have slight negative differences. This distinction is seen as being highlighted in April (Figure 9(b)). Nevertheless, more positive values are also observed during this month. The tremendous fluctuation in the difference in SIT clearly shows that there exists tremendous variation in the atmosphere, which has caused such huge instability within the span of a year.
Figure 9

Spatial difference of SIT from 2019 to 2020 for months (a) March and (b) April.

Figure 9

Spatial difference of SIT from 2019 to 2020 for months (a) March and (b) April.

Close modal
Figure 10

(a) Temporal variability in SIC, (a) yearly variability using monthly data; and spatial difference of SIC from 2019 to 2020 for months (b) March, (c) April, (d) May, and (e) June.

Figure 10

(a) Temporal variability in SIC, (a) yearly variability using monthly data; and spatial difference of SIC from 2019 to 2020 for months (b) March, (c) April, (d) May, and (e) June.

Close modal

SIC in the Russian Arctic has been declining over the past 20 years due to the effects of climate change. The Russian Arctic SIC has been declining at a rate of approximately 2.7% per decade since the late 1970s (Rodrigues 2008), with some of the most significant declines occurring over the past ten years (2010–2020). Detailed monthly variation of SIC over the region is illustrated in Figure 10(a). The range over the considered region is found to vary between 2% and 14%, indicating that the region experiences low sea ice conditions. Additionally, the annual average of the Russian region shows a declining trend with values of 7.55% and 7.82% during 2016 (the year which is also recorded to have the lowest sea ice condition over the Arctic region) and 2012, respectively. Overall from Figure 10(a), it is difficult to contemplate if any change has been caused to the sea ice environment during the pandemic leading to its acceleration or deceleration. Figure 10(a) shows the annual area average SIC of 7.72% and 7.64% during 2019 and 2020, respectively, with no much significant difference between the two spans.

One of the key aspects of the locations under consideration (the Russian Arctic) is that not only is the area closer to the North Pole (Arctic), but it also serves as a massive sea ice production reservoir. The area surrounding the Barents Sea, Kara Sea, and Laptev Sea is frequently seen to be sparse during the summer and rich in thick sea ice during the winter. The spatial plot in Figure 10 illustrates the variation in SIC for the months of March, April, May, and June between 2019 and 2020. This trend in the drop of SIC during 2020 is well expected given the variations in atmospheric conditions along with the decrease in industrial aerosol emissions. It has been noted that the SIC difference in the area surrounding Svalbard, Franz Josef Land, the Kara Sea, and the Laptev Sea ranges from 0 to 25%. The Barents Sea, on the other hand, is observed to have a negative SIC, with values ranging from −25% to 0%. Positive values are high in the region south of the Barents Sea. Similarly, the region right next to Russia has a positive SIC. Further in the month of April (Figure 10(c)), a positive difference in SIC during 2019 and 2020 is highly visible to the north of the Laptev Sea. The region around and north of the Kara Sea is observed to show slightly negative values of SIC difference. Additionally, the SIC percentage in the area east of Russia fluctuates between positive and negative values, showing that SIC is highly variable. However, the same location was noted to have strong positive SIC values in March (Figure 10(b)). Positive values are leaning more toward the Arctic region in this month than the region around the land (Russia). By May (Figure 10(d)), the sea ice starts to respond to the meteorological shift that occurred way back in March, when the country was put under rigorous lockdown. During May, the majority of the Arctic seas, the Barents Sea, Kara Sea and Laptev Sea, showed positive SIC. The Kara Sea has the highest fluctuation of any sea, surpassing the Laptev and then the Barents. Additionally, there is a significant positive variability in the SIC percentage in the area surrounding Svalbard, Franz Josef Land, and places that are closer to the Russian coasts. However, during June (Figure 10(e)), the highest variability over the seas of the Arctic is observed. It is evident that the Laptev Sea, in particular, exhibits both positive and negative SIC. June is seen as having more positive SIC values in the north than May. A similar trend has been observed east and north of Kara. It is evident from Figure 10 that a rise in temperature has a negative impact on the melting of sea ice. When comparing the years before the pandemic (2019) and the pandemic itself (2020), it is projected that the influence of the pandemic lockdown on sea ice conditions cannot be judged with the current data resolution.

However, to narrow down the scale to daily observation (just like aerosol change in Figures 7 and 8), day-to-day variability in SIC is observed in Figure 11. The observation starts with the last day of Arctic haze occurrence over the region, i.e., 17 April 2020 (Figure 11(a)). The SIC count for the range 90%–100% SIC is found to reach 160. This trend remains the same for the next day (18 April 2020) as well (Figure 11(b)). By 19 April 2020 (Figure 11(c)), the higher values are observed to have lower counts of ∼130. This trend is visibly seen to be the same until 22 April 2020 (Figure 11(f)). The SIC range of 90%–95% is expected to increase by 23 April 2020 (Figure 11(g)). The count on this date reaches up to 40, having been only ∼30 during the previous dates. By 26 April 2020 (Figure 11(j)), the range of 95%–100% SIC decreases to 80%–85%, and the decrease continues on 27–28 April 2020 (Figures 11(k) and 11(l)), with the count reaching 100. A decline in sea ice melt over the considered region was expected during the course of lockdown due to low levels of air pollution as there was a halt in industrial and transportation activities. This is because pollutants like BC can darken the surface of snow and ice, causing them to absorb more solar radiation and melt more quickly. By reducing emissions of these pollutants, lockdowns may have had a small, temporary cooling effect on the Arctic. Overall, while lockdowns may have had some minor and temporary impacts on sea ice conditions over the Russian Arctic, they are unlikely to have had a significant or long-lasting effect on the overall trend of sea ice decline in the region.
Figure 11

Histogram of SIC over the Russian Arctic region during COVID-19 lockdown: (a) 17 April, (b) 18 April, (c) 19 April, (d) 20 April, (e) 21 April, (f) 22 April, (g) 23 April, (h) 24 April, (i) 25 April, (j) 26 April, (k) 27 April and (l) 28 April for the year 2020 (color differs at the scale of 5% SIC).

Figure 11

Histogram of SIC over the Russian Arctic region during COVID-19 lockdown: (a) 17 April, (b) 18 April, (c) 19 April, (d) 20 April, (e) 21 April, (f) 22 April, (g) 23 April, (h) 24 April, (i) 25 April, (j) 26 April, (k) 27 April and (l) 28 April for the year 2020 (color differs at the scale of 5% SIC).

Close modal

In this paper, we have understood the effects of COVID-19 emissions changes on the sea ice conditions over the Russian Arctic region in 2020. It is found that the decrease in anthropogenic aerosol emission increases the air temperature, indicating that few aerosols play the role of scattering radiation. It was quantitatively understood that there was an increase in temperature during the pandemic, while comparing the year 2020 with 2019. The highest temperature difference between the two periods was observed in the months of February (ΔT = 3.23 K) and November (ΔT = 3.55 K), with a difference ΔT > 3 K. Additionally, the solar flux trapped at the top of the atmosphere was significantly higher in 2020 than in 2019. The majority of the seas (Barents Sea, Kara Sea, and Laptev Sea) in the region have radiation levels greater than 13 W m−2. The highest difference in radiation was observed in the month of May, with the value of ΔS = 0.28 W m−2. By the onset of summer, in June 2019, ΔS = 0.15 W m−2. It is numerically calculated and understood that during May 2020, the flux increased by 37.15% compared with May 2019. Further, the causative factor of such an incline in temperature over the region was understood by analyzing the emissions of aerosols like NH3, BC, CO2, CO, SO2, OC, N2O, and NMVOCs. The Arctic haze aerosols’ lifecycle (surface and mass-wise) reveals that they are at their maximum during March, when the sea ice is at its maximum. The daily trend of aerosols experiences a downward trend after 18–19 March 2020. That was the majority time when the region was put under strict lockdown. The highest negative difference was observed between 3 April and 5 April 2020, with a daily difference value of −0.04, −0.02, −1.51, −0.02, −0.11, and −3.14 kt/day for NH3, BC, SO2, OC, N2O, and NMVOCs, respectively. The impact of these ultimately altered the growth and decay of sea ice over the region which was understood using the SIC parameters. The positive values of SIC were discovered to be leaning more toward the Arctic region than the land region (Russia). From the observations, it is evident that the lockdown was short-lived and the process of sea ice formation occurs over a long period of time. Therefore, associating the two does not yield a positive impact with the current data resolution used. Overall, the COVID-19 pandemic has had both positive and negative indirect impacts on the environment, with the negative effects likely to outweigh the positive ones. While the reduction of aerosol emissions and greenhouse gas concentrations during the pandemic may seem like a quick fix, it is not a sustainable long-term solution for addressing environmental challenges. Moreover, the pandemic has also brought about a range of additional environmental issues that could persist for a long time and may be even more difficult to address if not given adequate attention by countries. The results can be used to further understand S. M. Nazmuz Sakib's Hypothesis, which provides an aerosol sea ice feedback which can be expressed through a comprehensive formula, encompassing the key factors involved. This formula accounts for both positive and negative feedback loops, shaping the interactions within the system.

The findings of this study have important implications for theory, practice, and policy. However, they also come with limitations and complexities. The inherent uncertainties and variability of Russian Arctic sea ice make it challenging to accurately predict its future conditions. Feedback mechanisms triggered by sea ice changes introduce additional uncertainties, as they can amplify the effects of climate change. These findings help in policy implications, particularly for climate change mitigation and adaptation strategies. Here, in this case, it is difficult to strictly establish a relationship between the anthropogenic aerosols and cryospheric parameters as the lockdown imposed was short-lived.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

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