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Canada lynx

The Canada lynx Lynx canadensis
is a beautiful wild felid (or cat) of the boreal forest. Like the cougar
and the bobcat, the other two members of the cat family (Felidae) native
to Canada, the Canada lynx (referred to as lynx in this text) tends to be
secretive and most active at night and, like them it is rarely seen in the
wild. Even for trappers who have spent a lifetime in areas where lynxes
are common, encounters with these predators are rare and memorable. Of the
three Canadian wild felids, the lynx and bobcat are most alike and most
closely related to each other. They probably both descended from the
larger Eurasian lynx. The cougar is much larger and more powerful than
either of them, and can be readily identified by its long tail.
The lynx preys almost exclusively on the snowshoe hare, and
snowshoe hare populations follow a 10-year cycle. Lynx numbers thus
fluctuate dramatically, as populations of the hare, its main prey species,
build to a peak and then crash. Scientists who have examined the
fur-trading records of the Hudson's Bay Company have been able to trace
closely linked 10-year cycles of growth and decline in populations of the
two species over the past 200 years. Figure 1 shows the cyclic fluctuations in
the numbers of snowshoe hare and lynx pelts supplied to the company over a
90-year period.

Appearance
| |
 The
Canada lynx has prominent tufts of hair on its
ears |
The lynx resembles a very large domestic cat. It has a short tail, long
legs, large feet, and prominent ear tufts. Its winter coat is light grey
and slightly mottled with long guard hairs; the underfur is brownish, and
the ear tufts and tip of the tail are black. The summer coat is much
shorter than the winter coat and has a definite reddish brown cast.
Its large feet, which are covered during winter by a dense growth
of coarse hair, help the lynx to travel over snow. The lynx, like the
snowshoe hare, can spread its toes in soft snow, expanding its "snowshoes"
still farther.
The lynx has large eyes and ears and depends on its
acute sight and hearing when hunting. The lynx's claws, like those of most
other cats, are retractable and used primarily for seizing prey and
fighting. The lynx has a variety of vocalizations, like those made by
house cats, but louder.
The lynx and the bobcat look much alike,
although on average bobcats are slightly smaller. There are small
differences in appearance. The bobcat's feet are not as large as those of
the lynx, making the bobcat less able to secure food in deep snow; the
lynx's tail has a solid black tip, whereas that of the bobcat has three or
four narrow black bars and a black spot near the tip on its upper surface;
and the bobcat's fur has more pronounced spotting.
Habitat and range
The lynx generally inhabits forested wilderness areas. It favours old
growth boreal forests with a dense undercover of thickets and windfalls.
However, this carnivore will populate other types of habitat as long as
they contain minimal forest cover and adequate numbers of prey, in
particular snowshoe hares. Because hare populations increase in forests
that are growing back after disruption by wildfires or logging operations,
these regenerating forest ecosystems are often able to support denser
populations of lynxes as well.
Lynxes are remarkably tolerant of
human settlement if unmolested. For example, since the early 1960s, they
have occupied the partly cleared mixed-farming district near Rochester, in
central Alberta. A few were shot in farmyards, but there was no intensive
fur trapping, and lynxes remained in the area.
The range of the
lynx is essentially that part of North America covered by boreal forest
and occupied also by the snowshoe hare (see map). Between 1900 and the
mid-1950s, lynxes became scarce in the southern portions of this range.
This was probably due to trapping during periods of snowshoe hare scarcity
(low years in the 10-year cycle). At these times lynx numbers are already
low and fewer young are surviving to adulthood, so trapping can seriously
deplete, or even eradicate, local populations. In the past 25 years,
lynxes have reoccupied some of this southern range, and this may be due to
tighter legal restrictions on trapping. The northern range expansion of
the bobcat in the past century may also have contributed to the overall
decline in lynx numbers. When both species compete for the same space and
food resources, the lynx most often yields to the more aggressive and
adaptable bobcat.

Food habits and hunting behaviour
More than 75% of the lynx's diet in winter is snowshoe hares, and when
hares are abundant a lynx may kill one every one or two days. In summer
the lynx's diet is more varied. But even in summer hares remain the main
prey, supplemented by grouse, voles, mice, squirrels, and foxes. A hungry
lynx will devour an entire hare in one meal; partially-eaten prey may be
hidden and eaten later. When it is available, lynxes will also supplement
their diet with carrion from domestic livestock and/or big game animals,
such as deer, but they rarely attack large prey. An exception is in
Newfoundland where, after people introduced the snowshoe hare to the
island in the 1870s, lynxes began to prey on caribou calves when snowshoe
hares became scarce. In the 1960s, lynxes were killing so many calves that
wildlife managers removed many of the lynxes found on the calving grounds.
Today, the caribou population has increased to the point that lynx
predation is not considered a threat.
Lynxes hunt at night. They
watch and listen for prey, but they do not seem to track it by smell. Like
all members of the cat family, they move very silently. Although excellent
climbers, they are seldom found in trees. Because they cannot run fast
except over short distances, they stalk or ambush their prey at close
range. A common strategy is to lie in wait beside the well-used trails, or
runways, of the snowshoe hare, and success usually depends on whether the
lynx manages to capture the hare at one bound (about 6.5 m, four hops
for the hare).
Male lynxes hunt alone, except briefly during the
mating season. By autumn, females travel with their kittens, the young
learning to hunt, and the family group may stay together until the
breeding season, in late February or March. Family groups cooperate to
increase their hunting success. The mother and young often travel in
single file through habitat where hares are scarce, but will travel
abreast when hunting in habitat where hares are plentiful. A hare flushed
by one lynx may be caught by another.
Home range, territoriality, and long-range movements
The size of the home range varies with numbers of lynxes and snowshoe
hares in the area, available cover, and season. When there are fewer
hares, each lynx needs a larger area on which to hunt. In summer, home
ranges are larger than in winter. In Alberta, lynx tracked in winter had
home ranges varying from 15 to 47 km². On Cape Breton Island, a study
that involved radio transmitters attached to adult lynxes measured home
ranges of 12–19 km² in winter and 27–32 km² in summer. In
Canada, scientists have measured daily travelling distances for lynxes
ranging from less than a kilometre to 19 km.
The
territoriality of these mammals is still poorly understood. Home ranges
may overlap, especially where the neighbours are of different ages and
sexes. In general, the home ranges of adults do not seem to overlap with
other adults of the same sex. The animals urinate frequently to mark their
home range.
Periodically, there have been conspicuous mass
movements of lynxes out of the boreal forest and onto the prairie
grasslands. These were well known to early fur traders and trappers, but
they ceased in 1925–26. During 1962–63, however, there was once again a
notable movement out of the north. Lynxes entered large cities such as
Edmonton, Calgary, and Winnipeg; appeared on the open grasslands of
southern Alberta, Saskatchewan, and North Dakota; and reached Iowa and
southwestern Wisconsin. These same events were repeated during 1972–73.
Like so many other aspects of the natural history of the lynx, these
movements can be understood by relating them to the cyclical declines in
snowshoe hare populations. Lynx populations that increase during periods
of hare increase must either starve or emigrate when the hares disappear.
The absence of any obvious movement between 1925–26 and 1962–63 probably
reflected unusually low numbers of lynxes.
Breeding
Mating occurs during February or March each year, and the young
(usually four) are born in April and May, 60–65 days later. Although the
lynx seldom uses an underground den, young may be born under brush piles
or uprooted trees, or in hollow logs, which provide shelter from rain and
cold. The kittens, reared solely by the female, look like those of the
domestic cat. Female kits may breed for the first time as they approach
one year of age, but this depends on the abundance and availability of
snowshoe hares and the physical and nutritional condition of the lynx.
Limits to population
Probably starvation following the rapid cyclic declines in snowshoe
hare populations is the greatest single source of natural mortality among
adult and yearling lynxes. About 40% of the total lynx population may
starve to death following a crash in the snowshoe hare population. During
the following three to four years, when the hare population is starting to
rebuild, lynxes breed, but the kittens die before winter. This suggests
that an adult female simply cannot support both herself and her litter
when hares are scarce.
In Canada, the only other important cause
of death seems to be trapping. Although the wolf is alleged to be the
chief natural enemy of the lynx in northern Europe, nothing is known of
lynx-wolf interactions in North America. The incidence of diseases, such
as rabies and distemper, among lynxes and their impact on populations are
also unknown.
The effects of people on the lynx
The most important influence of people on the lynx has been through
trapping. The lynx is easily trapped, and when fur prices rise, trappers
take a larger proportion of the lynx population. Intense trapping can
remove most lynxes from a given area. Historically, trapping has caused
long-term changes in the size of the lynx population in Canada. Lynx
populations began to decline after 1900, and the decline continued to the
mid-1950s. At that time, garments made of long-haired furs went out of
fashion, there was a major depression in fur prices and a decline in
trapping, and the lynx population was able to recover. Since the early
1970s, the demand for lynx pelts has risen steadily. The average price
paid per pelt went from about $30 in 1970 to peak in the mid-1980s at over
$500 per pelt. By 1990, it had fallen to $117.
Today, the lynx is
trapped in all provinces and territories except Prince Edward Island, Nova
Scotia, and New Brunswick. Trapping is confined to regulated seasons, and
wildlife managers can vary the regulations as needed from year to year and
among districts within a province. Many jurisdictions have also placed
restrictions on the number of lynxes that may be killed. Some biologists
have recommended closing trapping seasons entirely during lows in the
population cycle. Several provinces are carefully studying the influence
of trapping on their lynx populations and adjusting regulations to protect
this renewable resource. High fur prices have also stimulated interest in
raising lynxes on ranches, and it is possible that ranching may one day
provide a considerable number of the pelts that enter trade, as is now the
case with mink and fox.
In general, human activities do not seem
to be threatening lynx populations. Although the lynx is usually
considered to be a wilderness animal, human settlement does not seem to
have reduced its range. Logging in the boreal forest that results in a
good mix of mature conifer stands (for cover and travel) and regenerating
stands (in which snowshoe hares abound) may even enhance habitat for lynx.
Forestry operations, however, provide roads and ease of access to the
trapper. If the regulations governing logging are not conservative and
flexible enough, extensive clearcutting that results in the virtually
complete removal of conifer forests from large tracts of land is probably
harmful to resident lynx populations.
Reading list
- Banfield, A.W.F. 1974. The mammals of Canada. University of Toronto
Press. Toronto.
- Brand, C.L. and L.B. Keith. 1979. Lynx demography during a snowshoe
hare decline in Alberta. Journal of Wildlife Management 43:827–849.
- Elton, C. and M. Nicholson. 1942. The ten-year cycle in numbers of
the lynx in Canada. Journal of Animal Ecology 11:215–244.
- MacLulich, D.A. 1937. Fluctuations in the numbers of the varying
hare (Lepus americanus). University of Toronto Studies Biological
Series 43. University of Toronto Press. Toronto.
- Parker, G.R., J.W. Maxwell, L.D. Morton, and G.E.J. Smith.
1983. The ecology of the lynx on Cape Breton Island. Canadian Journal of
Zoology 61(4):770–786.
- Quinn, W.S. and G.R. Parker. 1987. Lynx. Pages 684-694 in M. Novak, J.A. Baker,
M.E. Obbard, and B. Malloch, editors. Wild furbearer
management and conservation in North America. Ontario Trappers'
Association. North Bay.
Published by authority of the Minister of the Environment
© Minister of
Publics Works and Government Services Canada 1977, 1988, 1993
Catalogue No.CW69-4/59-1992E ISBN: 0-662-19412-8 Text: L.B.
Keith
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