All eight of the species of bears
living today had a common ancestor, Ursavus, that lived during
the Miocene period over 20 million years ago. The evolutionary
routes (phylogeny) that bears took to reach their present positions
make an interesting story, which will undoubtedly change as new
evidence becomes available. Two lines of evidence for bear
phylogeny are presently available: paleontological (fossil) and
molecular. Both sets of data are in general agreement as to the
timing of speciation (the formation of new species) events. The
fossil data suggest that Ursavus and his relatives were forest-dwelling
carnivores that probably lived much as foxes or raccoons do today.
They had warm fur coats that enabled them to live in cool climates
with cold winters. They ate meat, but probably also fed on a
variety of plant foods, especially when prey was not available.
Their teeth were primarily the teeth of carnivores; sharp, cutting
teeth adapted for tearing and ripping, but they were beginning
to develop teeth for grinding plant foods. During winter periods,
they were probably restricted to areas where their prey could
also survive.
The evolutionary process has been at work shaping the animals
we call bears for over 20 million years. The formation of new
species is a continuous process that takes place over long periods
of time. Generally a new species is formed from a population
of animals after they become isolated from other populations
of the species. At some point, after about half a million years
or so, the isolated population becomes so different genetically
that it is unable to reproduce with its parent population, which
has also diverged over time. This is called reproductive isolation.
Many groups of animals that we all would consider to be distinct
species are actually able to breed successfully with other species
on a physiological and genetic basis. In some cases they are
prevented from doing so because they have developed distinct
breeding behaviors which keep them from 'recognizing' the other
species and consummating the reproductive act. This is called
behavioral isolation.
In other cases they are separated by geographic barriers that
effectively prevent any individuals from the two groups from
coming in contact with each other. If this geographic isolation
lasts long enough, they may become behaviorally or reproductively
isolated, or both. Grizzly bears and polar bears are a case in
point. Their genetic lineages diverged less than one million
years ago according to the evidence of mitochondrial DNA. They
have produced viable offspring from matings in zoos; in one case
a male polar bear accidentally got into an enclosure with a female
Kodiak bear at the U.S. National Zoo in 1936. They mated and
had three hybrid offspring. A breeding experiment was then conducted
and the hybrid offspring proved able to breed successfully with
each other, indicating that these two species of bears were much
more closely related than previously expected. In fact all the
species in the subfamily Ursinae (all bears except the giant
panda and the spectacled bear) probably have the ability to crossbreed,
and several combinations have actually occurred.
Bears and
Humans
Humans and bears coexisted until technologies arose to give humans
an advantage. As human populations have grown, people have
required more space. In the competition for space humans
are now easily able to exclude bears and other species from the
land. This has happened fast enough to drive species to
extinction and to threaten them even in protected areas. Small
populations tend to go extinct. If an entire species is reduced
to one small population, the entire species will almost certainly
wink out of existence, never to return. In the early 70's
scientists introduced a systems approach to the study of extinction,
distinguishing between deterministic (caused) and stochastic
(random) factors.
These ideas were further refined so that now it is understood
that the primary factors affecting the survival of small populations
are: (1) deterministic extinction, which occurs when something
essential is removed (such as space, shelter, or food) or when
something that has negative effects (like a competing exotic
species or a disease) is introduced, (2) environmental
stochasticity, or random changes in the environment such as drought,
global warming, or severe winters, (3) demographic stochasticity,
or the chance variation in individual birth and death (demographic)
events, which has very large effects once a population becomes
very small, (4) genetic deterioration, which can reduce
fitness through increased genetic drift, inbreeding, and the
subsequent loss of heterozygosity and genetic variance, and (5)
catastrophes, or rare but widespread events that can extinguish
a population or species, such as a huge meteorite, an epic flood,
or the eruption of a large volcano.
Loss of habitat and fragmentation are the immediate threat to
bears today. Fragmentation of bear habitat and small bear population
sizes are the result of centuries of competition with human beings. Once
a population becomes small (less than 100 animals) the stochastic
or random factors become much more important. Although populations
tend to become extinct from the direct random processes of small
populations such as few females of breeding age, inability to
find a mate etc., those demographic effects are made worse by
genetic effects.
Bear Conservation
Due to their intolerance of human beings and utilization of diverse
foods over large areas grizzly bears require specific considerations
when developing a conservation design for a region. These characteristics
also make the grizzly bear a good choice as an umbrella
species a species whose needs are co-incident with
many others species and thereby provides an Umbrella of protection.
Although grizzly bears are intelligent, adaptable animals, their
survival is dependent upon their ability tohigh quality food
find sources.Contacts with human beings for any reason increases
the probability that the bear will be killed.Basically, bears
need areas where they can find good quality food without being
killed by humans.
Predators such as bears are just the tip of the iceberg; we are
losing populations of plants and animals at alarming rates.In
one sense this is a moral and spiritual failure on our part.
On a more practical level what we are ultimately losing is information.We
are losing information on how life operates.We are losing data
and systems that capture energy from the sun and pass it along
to support species and ecosystems; and one of those species is
us.We need to keep the systems intact so that we can continue
to lead healthy, interesting lives.We need to keep the information
intact because it could be very important for us at sometime
in the future.If we lose genetic and ecological information,
from almost any plant or animal, we are reducing our own options.
The maintenance of large conservation
networks (the science of Conservation Area Design) requires a
degree of sacrifice by humans. We must be willing to give
up some areas for other species to survive. This is what
saving the rainforest, or saving the desert tortoise, or saving
the bears, is all about. It is not an unrewarded sacrifice
however; it is essential to maintaining our current quality of
life, and of improving the quality of life for others.
If we reduced the natural world to monocultures of a few agricultural
plants, and a few domesticated animals, we would have very few
options in the face of environmental change. To feed human
populations and to support our civilizations however, we need
these simplified agricultural systems, at least until we devise
more complex ones. The critical balance that society needs
to find now is how to maintain the function of natural systems
at the same time and in the same areas, that we maintain our
own domestic systems.
We need to maintain this balance; between the immediate needs
of human beings, and the long-term needs of natural systems including
humans. Visions to do this must cut across many artificial
human boundaries and be based on the ecological and evolutionary
networks we need to maintain. Borders and boundaries are
irrelevant to gene flow, nutrient cycling, or seed propagation. Such
visions have primarily been formulated by independent scientists
and non-governmental organizations. However, as the science
progresses, and as government agencies develop cooperative strategies,
interagency approaches are also beginning to develop conservation
area design strategies.
In the U.S., visions such as
The Wildlands Project and the the Yukon-to-Yellowstone Conservation
Initiative have developed on a local basis by groups and individuals
that work on areas where they live.These are projects designed
to improve or maintain natural ecosystems, native species,
and air and water quality by protecting core areas of wildlife
habitat and habitat connections within the matrix of human-altered
landscapes. They are projects designed to maintain human options
as well as maintaining options for other species. Based
upon core areas that are already protected as national parks
and wilderness areas, scientists are working to determine what
additional areas, if any, are needed in order to maintain viable
populations of large carnivores such as bears. If large carnivore
populations are preserved, then most other native animals and
plants will also be protected. This applies to other species
than bears, and applies to all ecosystems on the planet. The
best hope for preserving species is to provide habitat. The best
way to provide more habitat where it is fragmented into isolated
patches is to connect the patches somehow so that animals can
move between them. The best thing that individuals can do to
promote conservation is to tolerate wildlife nearby, avoid attracting
them to areas where they will cause conflicts, understand their
needs, and give them the space they need.