1. Introduction
Over the past four decades, the Arctic underwent the most climate variability and changes as a response to strong climate-related positive feedback (Serreze and Barry 2011). The Arctic has warmed nearly 4 times faster than the rest of the Earth since 1979 (Rantanen et al. 2022). Patterns of negative anomalies in snow mass balances and snow cover spatial extent have been observed, significantly affecting how the cryosphere responds to climate change (Cullather et al. 2016; Liston and Hiemstra 2011; Derksen and Brown 2012; Larue et al. 2017). Furthermore, recent model simulations predict an increase in both the mean and the variability of arctic precipitations over the next decades (Bintanja et al. 2020) that would become more frequent (Song and Liu 2017). Satellite-based studies have shown that rain-on-snow (ROS) occurrences are increasing as a response to this accelerated warming (Rennert et al. 2009; Langlois et al. 2017; Dolant et al. 2018a). However, their cumulative impacts on snow and the environment remain unknown.
ROS events and increasingly warming temperatures lead to the presence of liquid water in the snow cover that alters energy transfer mechanisms (Rennert et al. 2009; Weismüller et al. 2011; Riseborough et al. 2008), causing uncertainties in climate projections. Water in the snowpack creates ice crusts and melt–freeze layers that can have negative impacts on foraging conditions for the Arctic’s ungulates such as caribou (Rangifer tarandus) and muskoxen (Ovibos moschatus) (Putkonen et al. 2009; Langlois et al. 2017; Sokolov et al. 2016). Long-term remote sensing–based approaches allow quantifying spatial and temporal changes in the melt–freeze cycle that results from ROS (e.g., Marmy et al. 2013)
The spatial and temporal occurrence variability of ROS events remains widely unknown, despite their impacts on the surface energy balance and snow condition, because of a sustained lack of data. The lack of weather stations in the Arctic makes in situ monitoring difficult, especially regarding ROS events spatial patterns and trends. Liston and Hiemstra (2011) used snow modeling alongside atmospheric forcing data to analyze temporal trends and the results suggested an increase in ROS days of +0.03 days decade−1 between 1979 and 2009. Passive microwaves have also been used as a method to monitor ROS (Dolant et al. 2016; Grenfell and Putkonen 2008) given the high sensitivity of microwave brightness temperatures (Tb) to wet snow (Comiso et al. 2003). The water changes the snow properties and its microwave dielectric contrast before (i.e., dry) and after (i.e., wet) an ROS event. In normal and dry conditions, the values of Tb at 19 GHz are higher than Tb at 37 GHz given the enhanced scattering loss at high frequencies and shorter wavelength but the opposite is observed in wet conditions. Unfortunately, the coarse spatial resolution of passive microwaves (10–25 km) leads to biases in errors of omissions and commissions in existing algorithms (Dolant et al. 2018a). A new passive microwave dataset [NASA’s Making Earth System Data Records for Use in Research Environments (MEaSUREs)] has been published with a gridded resolution of 3.125 km × 3.125 km for Tb values at 37 GHz and 6.25 km × 6.25 km at 19 GHz (Brodzik et al. 2016). The 3.125 km × 3.125 km grid is used in this study to get a better precision for ROS event detection.
The main objective of this paper is to produce an ROS occurrence database over the Canadian Arctic Archipelago (CAA) from 1979 to the present using an updated detection algorithm (Dolant et al. 2016, 2018a). The objectives consist of 1) producing ROS occurrence anomaly maps to share with the wide scientific community and 2) evaluating the spatial and temporal variability in event occurrence across the CAA.
2. Data and method
a. Study site
The algorithm is run over all the islands of the CAA (Fig. 1). Baffin Island was excluded because no caribou live there. We divided the area into seven island groups as follows:
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Victoria Island (Victoria);
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Banks Island (Banks);
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Island group: Prince of Wales, Somerset, Russell, and Boothia Peninsula (Boothia)
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Island group: Axel Heiberg, Ellesmere, Ellef Ringnes, Corwall, Graham, Meighen, Coburg, and Amund (Axel and Ellesmere);
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Island group: Melville, Prince Patrick, Eglinton, Emerald, and Byam Martin (Melville);
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Island group: Mackenzie, Brock, and Borden (Mackenzie);
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Island group: Bathurst, Cornwallis, Little Cornwallis, Lougheed, Devon, and Baillie-Hamilton (BIC).
Area covered by the seven island groups studied in this report.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
This list only cites the biggest islands in each group as there are about 90 major islands. The total area covers approximately 1 400 000 km2.
b. Passive microwave satellite data
1) MEaSUREs
Passive microwave data were extracted from the Calibrated Enhanced-Resolution Passive Microwave Daily EASE-Grid 2.0 Brightness Temperature ESDR, Version 1 (MEaSUREs) dataset (Brodzik et al. 2016). The dataset consists of gridded passive microwave brightness temperature (Tb) data from the following instruments:
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Scanning Multichannel Microwave Radiometer (SMMR) on Nimbus-7;
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Special Sensor Microwave Imager (SSM/I) on DMSP 5D-2/F8, F10, F11, F13, F14, DMSP 5D-3/F15;
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Special Sensor Microwave Imager/Sounder (SSMIS) on DMSP 5D-3/F16, F17, F18, F19;
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Advanced Microwave Scanning Radiometer–Earth Observing System (AMSR-E) on Aqua.
Table 1 presents a selection of sensors and periods. Brodzik et al. (2016) used an overlap technique to enhance the resolution up to 3.125 km × 3.125 km. Two frequencies were used to detect ROS (see section 2c): 19 and 37 GHz with both horizontal and vertical polarizations. As such, the MEaSUREs database provides grids with a resolution of 6.25 km × 6.25 km for the 19-GHz Tb dataset and grids with a resolution of 3.125 km × 3.125 km for the 37-GHz Tb dataset. We divided by 4 the pixels from the 19-GHz dataset to fit the 37-GHz grids and created a temporal dataset from 1 July 1987 to 30 June 2018. We excluded data prior to September 1987 because record gaps made unavailable a high number of data points, making it too scarce to meet the objectives highlighted above. The values from the twice daily temporal resolution were averaged to give one daily Tb observation at 3.125 km for each frequency and polarization (i.e., 4 Tb values daily) starting using the data from the SSM/I F08 sensor (Table 1). Data with a 37-GHz frequency with vertical polarization from 1 August 2016 to the end of the period were retrieved from the F16 SSMIS sensor instead of the F17, which the dataset provider flagged as too low quality (Brodzik et al. 2016). In this study, each pixel is tested with the algorithm each day, therefore, the numbers in the results do not represent the number of events since one event can affect multiple pixels for multiple days. The GRP [Eq. (4)] response to water on the surface of the snowpack can linger for multiple days after an event or have a different cause, inflating the numbers again.
List of sensors selected to form the database used for ROS detection.
2) The North American Regional Reanalysis and atmospheric corrections
Linear functions of pwat used to derive the atmospheric brightness temperature contribution and transmissivity.
c. ROS detection algorithm
Dolant et al. (2016, 2018a) developed the original passive microwave detection algorithm for ROS. During an ROS event, liquid water accumulates at the snow surface, which is typically very dense in the Arctic, where the snowpack consists mainly of a wind slab on top of a hoar layer (Royer et al. 2021). The water changes the snow properties and its microwave dielectric contrast before (i.e., dry) and after (i.e., wet) a, ROS event. In normal and dry conditions, the values of Tb at 19 GHz are higher than Tb at 37 GHz given the enhance scattering loss at high frequencies and shorter wavelength. A snow surface wet from rainwater is warmer than the underlying snowpack and leads to microwave emission increasing, proportionally to the frequency. The increase is higher for horizontal polarization given the horizontal nature of the hard snow surface.
d. Meteorological stations and precipitations measurements
e. ROS count method
We applied the GRP algorithm to the daily corrected (atmospheric corrections) Tb measurements. If an ROS event was detected on a pixel, the value 1 was attributed; otherwise, the value was 0. We applied the algorithm on all inland pixels of an island group, except the pixels next to the water. Then, using two approaches detailed in the next paragraph, we accumulated the occurrences per winter by adding the daily values from each pixel to create daily occurrence maps, yearly accumulation maps, and yearly anomalies maps. We obtained anomalies by calculating the winter average ROS occurrence for each pixel over the period, then by calculating the difference between that average and the number of occurrences for a particular winter.
The GRP algorithm was applied following two “temporal” approaches: 1) “fixed period” and 2) “snow condition.” The fixed period applies the GRP algorithm over a fixed duration. We defined winter from 1 November to 31 May, providing a conservative estimate of the snow cover duration. This approach allows a constant “observation period,” which is useful when monitoring temporal changes in ROS occurrences over the years. In contrast, the snow condition approach uses a snow detection algorithm to detect the presence of a snow cover, then applies the GRP algorithm. The snow presence is detected when Tb at 19 GHz is higher than the Tb at 37 GHz in the vertical polarization, which is a well-used criteria in several snow water equivalent or snow depth microwave algorithms (Shi et al. 2016; Foster et al. 1984; Armstrong and Brodzik 2002). This approach makes temporal trends hard to analyze given the observational period changes over time but provides a better assessment of spatial patterns during winter by including the entire season as opposed to a fixed period.
3. Results
a. GRP threshold assessment
Overview of the algorithm validation results using data from meteorological stations. (a) Number of commissions in relation to the GRP threshold. (b) Number of omissions in relation to the GRP [Eq. (4)] threshold. (c) Error in percent [Eq. (5)] in relation to the GRP threshold.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
b. ROS anomalies
To compute ROS occurrence anomalies, we used a threshold value of −10 on the GRP and computed yearly anomalies following the fixed period and the snow condition approaches for each island group. We expected ROS occurrences to be higher in this second set of maps because the winter monitoring period spans over all months with snow cover.
1) Fixed period
The fixed period method ensures the number of days examined each year for ROS events remains constant. Figure 3 provides a broad idea of the region that received more ROS on average. It illustrates the number of ROS occurrences per year averaged for the 32 years from 1987 to 2018 included. The algorithm is not valid over glaciers, and a land mask has been used to exclude them. The higher occurrences on Ellesmere Island are likely false positives caused by the proximity of the glacier. Other regions with higher occurrences are the coastlines of the southern islands.
Annual average ROS occurrences from 1987 to 2019 with a fixed winter season from 1 Nov to 31 May as a scale of gray maxed at 4 ROS.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Figures 4 and 5 are examples chosen arbitrarily of anomalies of ROS occurrences detected across the CAA for, respectively, the 2010/11 and 2015/16 seasons. We calculated the anomaly with respect to the means of ROS detected per year and per pixel over the 1987–2018 period. Often, the ROS observations were along the coasts despite excluding pixels touching the water. Meanwhile, the ROS events detected were much closer to the average toward the middle of the islands.
Rain-on-snow occurrence anomalies map for winter 2010/11 using the fixed period method.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Rain-on-snow occurrence anomalies map for winter 2015/16 using the fixed period method.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Figure 6 shows the annual ROS anomalies averaged per island group. Values are color-coded from low (blue) to high (orange). Different regions show different evolutions. For instance, Mackenzie Island group’s ROS occurrence has not changed much over the years despite a large and intense ROS season during the winter of 2002/03. In contrast, BIC demonstrates high variability in ROS occurrence when compared to other island groups. We observed a general peak in ROS occurrence across the CAA for winter 2014/15, but then fewer occurrences happened in recent years. Despite high interannual variability in ROS anomalies, Table 3 suggests a current increase in positive anomalies compared to past conditions for Banks, Boothia, Mackenzie, and Melville.
Spatial average of ROS occurrence anomalies with the fixed period method. Blue represents a negative anomaly and orange represents a positive anomaly compared to the 1987–2018 average for each island group.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Percentage of years with positive average anomalies using the fixed period method.
2) Snow condition period
The snow condition method produced similar results to the fixed period method. Figure 7 highlights the average number of events each year. By using the snow condition method, we expanded the monitored period, thus inevitably increasing the total of occurrences detected. This did not seem to result in any major changes in the spatial or temporal patterns of anomalies. Figure 7 highlights areas where the major changes in ROS occurred across the CAA. With a longer observation period, more ROS events were detected, especially on the northernmost islands, since more events are more likely to occur at the beginning and the end of the snow season where there is a mix of rain and snow. With the fixed period method, we likely missed this moment for the northern islands. Once again, we observed more average occurrences along coastlines, but also across every island. Figures 8 and 9 show examples of anomaly for the years 2010 and 2015, respectively. Once again, stronger anomalies were observed along the coastlines and revealed the location where the meteorological systems produced more ROS for each year.
Annual average ROS occurrences from 1987 to 2019 with the snow condition method as a scale of gray maxed at 4 ROS.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Rain-on-snow occurrence anomalies map for winter 2010/11 using the snow condition method.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Rain-on-snow occurrence anomalies map for winter 2015/16 using the snow condition method.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Figure 10 highlights the temporal evolution of the averaged island yearly anomalies, using the snow condition approach. The behavior in trend occurrence across the islands is different than with the fixed period method (Table 4). Only 1 out of 7 island complexes have more ROS occurrence observed in the latter period compared to 4 out of 7 for the fixed period method. This suggests that the shortening of the snow season might lead to less ROS events observed with time.
Spatial average of ROS occurrence anomalies with the snow detection method. Blue refers to a negative anomaly and orange refers to a positive anomaly compared to the 1987–2018 average for each island group.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Percentage of years with positive average anomalies using the snow condition method.
The ROS events detected for every island varied widely. While in absolute more ROS events were detected in the latter part of the study period, we detected no significant trend. All the data are available on the https://grimp.ca/ server as a GeoTIFF raster map. The database contains rasters showing the period total yearly occurrences and yearly anomalies for both the snow condition and fixed period methods as shown in Table 5.
Number of rasters produced covering the entire study area.
4. Discussion
We selected the algorithm threshold based on data from various meteorological stations in the CAA, besides the recommendations of previous works. The validation at the meteorological stations confirms the algorithm is working, which was already demonstrated in Dolant et al. (2018a) and Langlois et al. (2017). The method does yield an number of omissions and commissions. Events other than ROS can cause liquid on the surface of the snowpack and trigger the algorithm (e.g., melt), or some ROS events might be too light to be detected (e.g., light drizzle). The threshold can be adjusted based on the study objectives. The biases of the data are unknown and remain a source of uncertainty in this study. The rasters were produced at a resolution of 3.125 km × 3.125 km since we do not expect any significant change in the Tb at 19 GHz given the homogeneous nature of tundra and polar desert snow (Royer et al. 2021), and we then optimize the information for the Tb at 37 GHz, which causes the reversal (Dolant et al. 2016) given its increased sensitivity to wetness. Using the raster products, we could assess spatial and temporal changes in ROS occurrence across the CAA. Our results show a high variability in occurrence anomalies between different island groups. On large islands, positive anomalies are observed along the coastline, with few events in the mainland. Topography likely does not impact GRP measurements but creates orographic effects that affect ROS occurrences. For the fixed period method, most island groups experienced an increase in “positive years,” where anomalies were especially strong toward the end of the study period, especially for the 2015/16 season, which was the warmest over the studied period (Cullather et al. 2016). When considering snow on the ground, we observe less ROS in the later period of the study. As highlighted by Moon et al. (2021) negative anomaly of the snow cover extent is observed in the latter period of our study. This is especially true for the spring season (Derksen and Mudryk 2023) where most ROS can be expected (Dolant et al. 2018a). The lower sea ice coverage during warmer periods might explain the results when open water can increase ROS probability. We conducted a preliminary assessment of sea ice concentration surrounding the island groups with the sea ice coverage information from the work of Couture (2022), who computed ice concentration maps from the Canadian Ice Service Digital Archive (CISDA) for the eastern Arctic and western Arctic. Ice forecasters interpret all available ice information from 1978 onward to create ice charts in the CISDA and to map the different ice types and concentration areas. From this raster dataset, we calculated the average open water area extent in a buffer of 50 km around Victoria Island and Banks Island. For each month, we calculated and compared the total average area of open water in the buffer with the number of ROS events detected for that month. Figure 11 shows examples for the month of October for both islands. We used the snow condition approach for the ROS detection to ensure false positives were excluded where a detection would occur when there was no snow on the ground.
Number of ROS events detected compared to the total area of open water around a buffer of 50 km from the island in October for each year. (a) Victoria Island. (b) Banks Island.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Since the islands are relatively wide, we compared ROS occurrences with open water on a finer scale. We thus divided the island and the ice buffer in four quadrants: southwest, southeast, northeast, and northwest (Fig. 12).
Number of ROS events detected compared to the total area of open water around a buffer of 50 km from Victoria Island in October for each year: (a) northwest, (b) northeast, (c) southwest, and (d) southeast.
Citation: Journal of Hydrometeorology 25, 2; 10.1175/JHM-D-22-0218.1
Although preliminary results suggest that an increase in ROS can be attributed to an increase in open water extent, the linear regressions are not statistically significant, suggesting that we need further work to find a better explanation. Many factors can influence ROS occurrences including wind, temperature, and humidity. Links with local ice conditions might not be trivial.
5. Conclusions
Using the MEaSUREs brightness temperature dataset with an atmospheric correction, we applied an ROS occurrence algorithm over daily CAA data for the period extending from fall 1987 to spring 2018 at a 3.125-km spatial resolution. The number of occurrences, along with yearly anomalies, was investigated using two methods based on how snow presence was considered. Following the main objective, we created a database of raster products on ROS occurrence that can now be used for further research. The dataset contains 128 raster maps including total ROS occurrences and anomalies (32 years each, for both fixed and snow condition approaches) and can be updated along with the updates of the MEaSUREs dataset. The spatial trend analysis indicated an enhanced detection of positive anomalies in the second half of the study period, with most detections expectedly occurring along coastlines, given the proximity of open water. When using a fixed period, the southernmost islands showed a higher number of occurrences, which was not the case when using the snow condition approach. Such results suggest that for the northern parts of the CAA, ROS events tended to occur earlier and later in the season when they were not counted using the fixed method. As for the temporal trend analysis, we observed a strong variability with more ROS occurrences in the later year of the period when using the fixed period winter season but observed less ROS when counting for the presence of snow. It suggests the shortening of the snow season period might lead to less ROS in general. It should be noted that the threshold for ROS detection of GRP = −10 had been validated with data from Arctic snow and should be limited to this region. Different regions should use this method with a revaluated threshold.
This database can be used to investigate the causal relationship with other variables and processes. The hypothesis that ROS occurrences are linked to the amount of free water around a region should be investigated further for all islands because our preliminary assessment of Victoria Island and Banks Island showed that some correlation during the fall might exist when ice coverage varies more, but we found no statistically significant correlation. Future studies could compare the method described here with other methods of ROS detection to better understand the limits of different approaches. This new dataset can also be used as input in ecological models, such as that in the works presented in Gautier (2022) and Martineau (2020) that used snow model outputs and an explanatory variable in ecological models to predict the presence of Peary caribou populations. It would be interesting to combine ROS rasters with their approach aiming at improving our ability to predict the animal presence and expand the approach to other ungulates of the Arctic. Finally, we hope this work can lead to an improved understanding of the processes controlling ROS occurrence and how such events affect other climate variables, improving our understanding of the Arctic’s climate system.
Acknowledgments.
This work was funded by the Natural Sciences and Engineering Research Council of Canada (NSERC), Environment and Climate Change Canada (ECCC), and the Fonds de recherche du Québec–Nature et Technologies (FRQNT). The scientific results and conclusions, as well as any views or opinions expressed herein, are those of the authors and do not necessarily reflect those of NOAA or the U.S. Department of Commerce.
Data availability statement.
The authors were unable to find a valid data repository for the data produced in this study. These data are available from vincent.sasseville@usherbrooke.ca at the University of Sherbrooke.
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