Contagious Ecthyma, Rangiferine Brucellosis, and Lungworm Infection in a Muskox (Ovibos moschatus) from the Canadian Arctic, 2014

2016 ◽  
Vol 52 (3) ◽  
pp. 719-724 ◽  
Author(s):  
Matilde Tomaselli ◽  
Chimoné Dalton ◽  
Pádraig J. Duignan ◽  
Susan Kutz ◽  
Frank van der Meer ◽  
...  
2022 ◽  
Vol 58 (1) ◽  
Author(s):  
Matilde Tomaselli ◽  
Bjørnar Ytrehus ◽  
Tanja Opriessnig ◽  
Pádraig Duignan ◽  
Chimoné Dalton ◽  
...  

1985 ◽  
Vol 26 (1) ◽  
pp. 120-126
Author(s):  
S. D. Mathiesen ◽  
T. Jørgensen ◽  
T. Traavik ◽  
A. S. Blix

2008 ◽  
Vol 127 (1-2) ◽  
pp. 10-20 ◽  
Author(s):  
Turid Vikøren ◽  
Atle Lillehaug ◽  
Johan Åkerstedt ◽  
Tord Bretten ◽  
Magne Haugum ◽  
...  

2021 ◽  
Vol 57 (1) ◽  
Author(s):  
Jamie L. Rothenburger ◽  
Juliette Di Francesco ◽  
Lisa-Marie Leclerc ◽  
Frank van der Meer ◽  
Matilde Tomaselli ◽  
...  

Rangifer ◽  
2003 ◽  
Vol 23 (5) ◽  
pp. 213 ◽  
Author(s):  
Frank L. Miller ◽  
Anne Gunn

The Peary caribou (Rangifer tarandus pearyi) was recognized as 'Threatened' by the Committee on the Status of Endangered Wildlife in Canada in 1979 and 'Endangered' in 1991. It is the only member of the deer family (Cervidae) found on the Queen Elizabeth Islands (QEI) of the Canadian High Arctic. The Peary caribou is a significant part of the region's biodiversity and a socially important and economically valuable part of Arctic Canada's natural heritage. Recent microsatellite DNA findings indicate that Peary caribou on the QEI are distinct from caribou on the other Arctic Islands beyond the QEI, including Banks Island. This fact must be kept in mind if any translocation of caribou to the QEI is proposed. The subspecies is too gross a level at which to recognize the considerable diversity that exists between Peary caribou on the QEI and divergent caribou on other Canadian Arctic Islands. The Committee on the Status of Endangered Wildlife in Canada should take this considerable diversity among these caribou at below the subspecies classification to mind when assigning conservation divisions (units) to caribou on the Canadian Arctic Islands. In summer 1961, the first and only nearly range-wide aerial survey of Peary caribou yielded a population estimate on the QEI of 25 845, including about 20% calves. There was a strong preference for range on the western QEI (WEQI), where 94% (24 363) of the estimated caribou occurred on only 24% (ca. 97 000 km2) of the collective island-landmass. By summer 1973, the overall number of Peary caribou on the QEI had decreased markedly and was estimated at about 7000 animals. The following winter and spring (1973-74), the Peary caribou population declined 49% on the WQEI. The estimated number dropping to <3000, with no calves seen by us in summer 1974. Based on estimates from several aerial surveys conducted on the WQEI from 1985 to 1987, the number of Peary caribou on the QEI as a whole was judged to be 3300-3600 or only about 13-14% of the 1961 estimate. After a partial recovery in the late 1980s and early 1990s, Peary caribou on the WQEI declined drastically between 1994 and 1997 and were estimated at an all-time known low of about 1100 animals by summer 1997. The number of Peary caribou on the QEI in summer 1997 was likely no more than 2000-2400 or only 8-9% of the 1961 estimate. The four known major die-offs of Peary caribou on the WQEI between 1973 and 1997 occurred during winter and spring periods (1 Sep-21 Jun) with significantly greater (P<0.005) total snowfall, when compared to the long-term mean obtained from 55 caribou-years (1 Jul-30 Jun), 1947/48-2001/02, of weather records from Resolute Airport on Cornwallis Island. Of ecological significance is that the die-offs occurred when the caribou were at low mean overall densities and involved similar high annual rates of loss among muskoxen (Ovibos moschatus). All of the available evidence indicates that Peary caribou (and muskoxen) on the QEI experienced die-offs from prolonged, under-nutrition (starvation) caused by relative unavailability of forage-the forage was there but it was inaccessible to the caribou due to snow and/or ice cover. We cannot control the severe weather that greatly restricts the forage supply but we should try to reduce the losses of Peary caribou from other sources-humans, predators and competitors.


Polar Record ◽  
1974 ◽  
Vol 17 (106) ◽  
pp. 13-22 ◽  
Author(s):  
Paul F. Wilkinson

If one is sufficiently bold or foolish to ask why the musk-ox Ovibos moschatus was domesticated, even a superficial review of the available evidence suggests that several answers may be given, depending upon the viewpoint from which the question is posed. I have argued elsewhere (Wilkinson, 1972a; 1973) that the domestication of the musk-ox was inevitable if the exploitation of musk-oxen was to continue in the present century. Because of certain biological and behavioural characteristics, musk-oxen can be exploited in only two ways without endangering their survival or exceeding their capacity to regenerate their numbers: they may be hunted as what I have called a critical resource, by which I mean a resource that is not exploited regularly (including seasonally) or intensively, but without which human survival is difficult or impossible incertain areas and periods; alternatively, musk-oxen may be exploited on a sustained basis for a combination of meat, milk, robes, or qiviur through domestication. Archaeological and ethnographic evidence is consistent with the hypothesis that, as a general rule, musk-oxen were hunted as a critical resource before the arrival of Europeans in the Canadian Arctic.


1989 ◽  
Vol 67 (5) ◽  
pp. 1106-1111 ◽  
Author(s):  
Anne Gunn ◽  
Frank L. Miller ◽  
Bruce McLean

Muskoxen (Ovibos moschatus) were classified by sex and age at 12 locations on four islands in the Canadian Arctic Archipelago, Northwest Territories. We classified 147 muskoxen on Bailey Point, southwestern Melville Island, and 92 on northeastern Prince of Wales Island in August 1983. We subsequently classified 5449 muskoxen on western Victoria and Banks islands in July–August 1986, which we used as a basis for evaluating the 1983 samples. The pooled sex ratio for muskoxen ≥ 3 years old was significantly skewed toward females, and the proportion of single bulls was also lower on Bailey Point than on northeastern Prince of Wales Island in August 1983 or on Banks or Victoria islands in July–August 1986. Sexual behaviour was frequently observed at Bailey Point in August 1983, which suggests that both bulls and cows were in breeding condition. Almost no aggressive rutting behaviour was seen at Bailey Point, in contrast to observation of the complete range of sexual and aggressive behaviours on Prince of Wales Island. Above-average (1970–1985) snow depths were experienced from March to May in five of the six winters preceding winter 1982–1983. We suggest that severe winters imposed malnutrition-related mortality on spent bulls. The depleted fat reserves of these bulls apparently could not sustain them during severe and prolonged winters. This kind of winter mortality among breeding bulls likely is higher in areas of high muskox densities where more interactions between bulls during the rut lead to greater energetic costs.


1978 ◽  
Vol 19 (3) ◽  
pp. 461-462
Author(s):  
Knut Kummeneje ◽  
Johan Krogsrud

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