Last updated 31 May 2022

The polar bear in the Barents Sea lives on disappearing sea ice. Climate warming is the main threat to polar bears. The polar bear habitat is changing rapidly, and the Polar Basin could be ice-free in summer within a few years. To gain access to preferred denning areas and their favorite prey, ringed seals, polar bears depend on good sea ice conditions at the right time and place. The population probably increased considerably during the years after hunting was banned in 1973, and new knowledge indicates that the population has not been reduced the last 10-15 years, in spite of a large reduction in available sea ice in the same period.

Polar bear
Photo: Janne Schreuder / Norwegian Polar Institute

What is being monitored?


Polar bear dens and sea ice cover

The figure shows the number of days when the sea ice cover around the island of Kongsøya from 1 October – 31 December (left axis) exceeded 60% and the number of dens the same winter (right axis). Dens are counted the following spring by surveys on the ground (over several weeks) or from a helicopter (1–2 days). The coverage in the study area has varied between years. The number of days when the sea ice cover exceeds 60% has a strong influence on the number of females that den on Kongsøya; few days with sufficient ice cover leads to few females entering dens.
(Cite these data: Norwegian Polar Institute (2022). Autumn sea ice cover and polar bear dens at Kongsøya. Environmental monitoring of Svalbard and Jan Mayen (MOSJ). URL: https://mosj.no/en/fauna/marine/polar-bear.html)


The figure shows the number of days when the sea ice cover around the island of Hopen from 1 October – 31 December (left axis) exceeded 60% and the number of dens the same winter (right axis). Dens are counted from helicopter the following spring. The number of survey days has varied between years. The number of days when the sea ice cover exceeds 60% has a strong influence on the number of females that den on Hopen; few days with sufficient ice cover leads to few females entering dens. Since 1979, when sea ice monitoring started, there has been a marked decrease in the number of days with sea ice cover around Hopen, and since the den counts started in the 1990s, there has been a similar decrease in the number of dens on the island.
(Cite these data: Norwegian Polar Institute (2022). Autumn sea ice cover and polar bear dens at Hopen. Environmental monitoring of Svalbard and Jan Mayen (MOSJ). URL: https://mosj.no/en/fauna/marine/polar-bear.html)


The figure shows the number of days between 1 October and 31 December that had a sea ice cover exceeding 60 % (within four 25×25 km pixels) in and around 5 denning areas in Svalbard (Hopen, Kongsøya, Storfjorden, Kvitøya and Nordaustlandet). The annual median value is represented by a line within each box, while box segments and lines over and under the median show the other data points for each year. There has been a decrease in the number of days with the given sea ice cover for all 5 areas over time. Fewer than 30 days with a 60% sea ice cover or more means that pregnant females will struggle to get to the denning area in time to breed, especially to the more distant islands such as Hopen, Kongsøya and Kvitøya.
(Cite these data: Norwegian Polar Institute (2022). Sea ice surrounding important denning areas for polar bears in Svalbard. Environmental monitoring of Svalbard and Jan Mayen (MOSJ). URL: https://mosj.no/en/fauna/marine/polar-bear.html)

Details on these data

Last updated28 February 2022
Update intervalYearly
Next updateFebruary 2023
Commissioning organizationMinistry of Climate and Environment
Executive organizationNorwegian Polar Institute
Contact personsJon Aars
Magnus Andersen

Method

Ice data are based on remote sensing data from the NASA earth observation system (passive microwave SSM/I/Special Sensor Microwave Imager). Observations from the ground or helicopter are made of dens which, with a high degree of certainty, are judged to be maternity dens, often confirmed by observations and tracks of cubs, and in some cases inspected (Aars 2013).

Quality

No such formal requirements. The proportion of dens in an area which is observed will depend upon when the bears leave the den, how long they remain there, how visible the den entrances are (which varies with the weather, particularly snow and wind), and the timing and geographical coverage of the observation studies. It is conceivable that the time when dens are vacated varies from year to year. A better understanding of the factors determining when dens are vacated and how visible they are may help to reduce the uncertainty. Some studies of this nature are taking place.

Other metadata

All data are stored at the Norwegian Polar Institute.

Reference level and action level

No set reference level or action limit.


What is being monitored?


Recruitment

Average litter size (cubs of the year); data from the annual capture-recapture program 1993-2023. There is a statistically significant weak trend of decreasing litter size over time (red line).
(Cite these data: Norwegian Polar Institute (2022). Polar bear cubs per litter. Environmental monitoring of Svalbard and Jan Mayen (MOSJ). URL: https://mosj.no/en/fauna/marine/polar-bear.html)


Proportion of females with cubs of the year, based on data from the annual capture-recapture program 1993-2022. The red trend line shows that there is no statistically significant linear trend in the data.
(Cite these data: Norwegian Polar Institute (2022). Production of polar bear cubs. Environmental monitoring of Svalbard and Jan Mayen (MOSJ). URL: https://mosj.no/en/fauna/marine/polar-bear.html)


Proportion of females with cubs of the year (COYs) and yearlings, based on data from the annual capture-recapture programme in 1993–2022. The blue dotted line describes a non-significant linear trend in the proportion of females with COYs over time. There is no significant trend over time in the proportion of females with yearlings (red dotted line). The observed interannual variation in the proportion of females with yearlings cannot be explained by time trend.
(Cite these data: Norwegian Polar Institute (2022). Number of females with cubs of different age. Environmental monitoring of Svalbard and Jan Mayen (MOSJ). URL: https://mosj.no/en/fauna/marine/polar-bear.html)

Details on these data

Last updated31 May 2022
Update intervalYearly
Next updateJune 2023
Commissioning organizationMinistry of Climate and Environment
Executive organizationNorwegian Polar Institute
Contact personsJon Aars
Magnus Andersen

Method

The number of cubs of all immobilized female polar bears is registered. The life history stage of the adult bear is noted (single adult, with cubs of the year, with one-year-old cubs, with two-year-old cubs, with adult partner).

Quality

Tagging and recapturing of polar bears is opportunistic; ice and weather conditions result in different areas being covered to differing extents in different years. The proportion of females with cubs will vary both geographically and seasonally. The reproduction parameter will therefore not necessarily reflect the population very well and a significant year-to-year variation can be expected in how well it does so.

Litter sizes will decrease somewhat during the spring, also during the period prior to April. Some of the inter-annual variation in litter size may be due to the fact that females with cubs are caught at different times between year, caused by effort and catchability.

Other metadata

All data are stored at the Norwegian Polar Institute.

Reference level and action level

No set reference level or action limit.


What is being monitored?


Body condition

Body condition index of adult male polar bears caught in spring (March-May) in the period 1993-2022. The lines in the middle of each box show the median value, and the box segments and lines above and below the median each cover ca 25 % of the data points. There is no significant trend over time. There was no fieldwork in 2020 due to the corona pandemic.
(Cite these data: Norwegian Polar Institute (2022). Condition in adult polar bear males. Environmental monitoring of Svalbard and Jan Mayen (MOSJ). URL: https://mosj.no/en/fauna/marine/polar-bear.html)

Details on these data

Last updated31 May 2022
Update intervalYearly
Next updateJune 2023
Commissioning organizationMinistry of Climate and Environment
Executive organizationNorwegian Polar Institute
Contact personsJon Aars
Magnus Andersen

Method

Males are darted from a helicopter. The straight-line body length (SL, from the end of the tail to the tip of the nose using a stretched tape measure held just above the bear), the zoological length (ZL, along the body from the end of the tail to the tip of the nose) and the axillary girth (G) are measured.

Quality

Natural uncertainty with measuring errors; right from the start, new people in the field have always learnt from previous fieldworkers how measurements are taken.

Other metadata

All data are stored at the Norwegian Polar Institute.

Reference level and action level

No set reference level or action limit.

Status and trend

A period of intensive hunting in and around Svalbard began about 1870, and on average some 300 bears were harvested annually in the following 100 years. The population was consequently at a low level when it was protected in 1973.

In 2004, it was estimated to number between 1900 and 3600, which means that it is not threatened by the effects smaller populations may be impacted by, such as loss of genetic diversity or random demographic processes. Furthermore, genetic studies show that exchange between neighboring subpopulations to the west and east is large. Another aerial survey over Norwegian territories in the Barents Sea and in Svalbard was conducted in 2015, and the results indicate that the number of local bears had not changed much when compared to the results from the previous survey in 2004. The number of bears that live north in the pack ice in the fall most likely has been stable or even increased in the period between the surveys.

Lack of earlier estimates of good quality makes it impossible to say anything certain about historical trends, but various types of data indicate that the subpopulation grew rapidly following its protection and into the 1980s. Using demographic data, it has been suggested that the subpopulation also grew up to the turn of the century. Even though the loss of sea ice has been marked around Svalbard in recent years, and is expected to continue in the coming decades, the size of the subpopulation may still be below the carrying capacity. It is therefore possible that the subpopulation currently is still growing, or at least is stable, even though the availability of habitats has become poorer for much of the year.

The occurrence of dens on the islands of Hopen and Kongsøya clearly show that few females reach there in the autumn if the ice comes late, sometime after the first part of November. Whether this means that the proportion of females in the subpopulation that have cubs is declining, or that they den elsewhere, is not clear.

The number of days with sea ice around all the five most important denning areas has experienced a dramatic negative trend since 1979. In some years, the ice has come late in all the areas the same year, and such years can prove challenging for females who have spent the summer in the pack ice to reach one of the relevant areas.

Causal factors

The availability of sea ice has always varied a great deal from year to year and through the seasons. The changes in large parts of the Arctic towards the period with ice-free water becoming longer and longer are explained by a milder climate with especially large changes in the Arctic. With current levels of greenhouse gas emissions, and the forecasts for the coming decade, it is expected that the areas around Svalbard will experience particularly large changes.

Observations so far are unable to document that changes in the climate have had clear effects on the subpopulation. Habitat availability may still be good enough to be able to maintain a population at the current level. Declining trends in reproduction or fitness may not be explainable just by variations in climate impact or corresponding trends in sea ice distribution. Density-dependent responses on reproduction are not an unlikely future scenario and may become prominent with time due to the growth in the subpopulation following its protection in 1973. Such density dependence will also be expected to increase if habitat availability decreases, but not before the population size approaches the carrying capacity.

Very high levels of several fat-soluble substances are found in polar bears in the Barents Sea area, and it is likely that this has effect at the population level, but it is very difficult to quantify how important they are.

The large annual variability in available sea ice makes it possible to study the effects of habitat changes more directly and may eventually enable the effects of density-dependence, habitat changes and other pressure factors to be quantified and separated from one another.

Consequences

The polar bear is an important species in the arctic ecosystem. Changes in their population size and the way bears use their habitat, which can be expected to be particularly large if changes in the availability of sea ice continues, will therefore be likely to have consequences beyond the changes for the species itself.

The polar bear is entirely dependent upon seals that live in the ice, and will have an impact on these species, at least locally. When the sea ice does not freeze in the fjords in Svalbard before late winter, ringed seals may, for lack of snow to make lairs, give birth to their pups directly on the ice. If, in addition, the areas of sea ice are limited, the pups will quickly be taken by bears, foxes and gulls. Over time, it is conceivable that poor seal recruitment leads to less food being available for polar bears.

Perhaps more importantly, less ice makes it difficult for the polar bear to hunt. More bears on land in years with little ice also increases predation on eggs and birds in several areas and may thus also influence ecosystems on land.

It is impossible to say anything now about exactly how changes in the number of bears and available habitats will affect the ecosystems, but a total loss of sea ice will necessarily also lead to a loss of the ecosystems that depend upon it.

Changes in the distribution and availability of sea ice are already leading to great changes in the distribution of polar bear dens. Historically important denning areas, especially on the more peripheral islands, may become unsuitable in the future. Increased use of alternative areas will also lead to greater changes in habitat. This might impose a larger predation pressure on potential prey species in new areas.

About the monitoring

The polar bear is monitored because it is Red Listed and is vulnerable to pressures deriving from climate change and environmental pollutants. It is also a species that has great appeal so that knowledge about how it is being affected will more easily lead to enhanced focus on the effects of climate change, pollutants and other pressures linked with human activity which may harm the ecosystem in the Arctic.

The most important human-induced pressure factor for polar bears is the loss of sea ice due to changes in climate. To be able to detect the effects of this as quickly as possible, the population monitoring of the polar bear is focusing on reproduction and body condition.

An aerial survey to estimate the size of the shared Norwegian-Russian Barents Sea subpopulation was carried out in 2004, and the resulting estimate was 2650 bears +/- ca 30 %. A new survey of the Norwegian part of the population was conducted in August 2015, and the results do not show any sign of a reduction in population size.

Due to the covid-19 pandemic situation in 2020 no fieldwork was conducted this year, and thus no data is available for any of the parameters.

Relations to other monitoring

Monitoring programme

International environmental agreements

Voluntary international cooperation

  • None

Related monitoring

  • None

Further reading

Links

Publications

  1. Aars, J., Marques, T.A., Buckland, S.T., Andersen, M., Belikov, S., Boltunov, A., Wiig, O. 2009. Estimating the Barents Sea polar bear subpopulation size. Marine mammal science 25(1): 35–52.
    DOI:10.1111/j.1748-7692.2008.00228.x
  2. Aars, J., Marques, T.A., Lone, K., Andersen, M., Wiig, Ø., Bardalen Fløystad, I.M., Hagen, S.B., Buckland, S.T. 2017. The number and distribution of polar bears in the western Barents Sea. Polar Research 36.
    DOI:10.1080/17518369.2017.1374125
  3. Aars, J. 2013. Variation in detection probability of polar bear maternity dens. Polar biology 36(8): 1089–1096.
    DOI:10.1007/s00300-013-1331-7
  4. Derocher, A., Andersen, M., Wiig, Ø., Aars, J., Hansen, E., Biuw, M. 2011. Sea ice and polar bear den ecology at Hopen Island, Svalbard. Marine Ecology Progress Series 441: 273–279.
    DOI:10.3354/meps09406
  5. Amstrup SC. 2003. Polar bear, Ursus maritimus. In: Feldhamer GA, Thompson BC, Chapman JA (eds.) Wild mammals of North America: biology, management, and conservation. The Johns Hopkins University Press, Baltimore, Md, pp 587–610.
  6. Andersen, M., Aars, J. 2016. Barents Sea polar bears (Ursus maritimus): population biology and anthropogenic threats. Polar Research 35, 26029
  7. Andersen, M., Derocher, A.E., Wiig, Ø., Aars, J. 2012. Polar bear (Ursus maritimus) maternity den distribution in Svalbard, Norway. Polar Biology 35: 499–508
  8. Aars, J., Marques, T.A., Lone, K., Andersen, M., Wiig, Ø., Bardalen Fløystad, I.M., Hagen, S.B., Buckland, S.T. 2017. The number and distribution of polar bears in the western Barents Sea. Polar Research 36.
    DOI:10.1080/17518369.2017.1374125
  9. Derocher, A.E. 2005. Population ecology of polar bears at Svalbard, Norway.  47(3): 267–275.
    DOI:10.1007/s10144-005-0231-2
  10. Durner, G.M., Douglas, D.C., Nielson, R.M., Amstrup, S.C., McDonald, T.L., Stirling, I., Mauritzen, M., Born, E.W., Wiig, O., DeWeaver, E., Serreze, M.C., Belikov, S.E., Holland, M.M., Maslanik, J., Aars, J., Bailey, D.A., Derocher, A.E. 2009. Predicting 21st-century polar bear habitat distribution from global climate models. Ecological monographs 79(1): 25–58.
    DOI:10.1890/07-2089.1
  11. Ingólfsson Ó, Wiig Ø. 2008. Late Pleistocene fossil find in Svalbard: the oldest remains of a polar bear (Ursus maritimus Phipps, 1744) ever discovered. Polar Research 28: 455–462.
  12. Jenssen BM. 2006. Endocrine-disrupting chemicals and climate change: A worst-case combination for arctic marine mammals and seabirds? Environmental Health Perspectives 114: 76–80.
  13. Mauritzen M, Derocher AE, Wiig Ø. 2001. Space-use strategies of female polar bears in a dynamic sea ice habitat. Canadian Journal of Zoology 79: 1704–1713.
  14. Regehr EV, Hunter CM, et al. 2010. Survival and breeding of polar bears in the southern Beaufort Sea in relation to sea ice. Journal of Animal Ecology 79: 117–127.
  15. Wiig Ø. 1998. Survival and reproductive rates for polar bears at Svalbard. Ursus 10: 25–32.