American Bison - Buffalo Field Campaign
American Bison - Buffalo Field Campaign
American Bison - Buffalo Field Campaign
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and foothills. <strong>Bison</strong> have a profound influence on ecosystems<br />
and create habitat heterogeneity through various means. As<br />
primarily graminoid (grasses and sedges) eaters, variable grazing<br />
pressure by free-ranging bison and their interaction with fire<br />
create habitat patchiness on which grassland bird diversity<br />
depends. Wallowing behaviour further promotes heterogeneity<br />
by forming temporary pools and changing surface hydrology and<br />
runoff and creating local patches of disturbed soil in which some<br />
flowering plant species prosper. <strong>Bison</strong> are dispersers of seeds,<br />
and are sources and redistributors of nutrients for predators,<br />
scavengers, plants, and ecosystem processes. Gogan et al.<br />
describe foraging patterns and habitat use by wood and plains<br />
bison in various ecoregions, from the arid southwest to humid<br />
cold boreal regions. The authors also review bison population<br />
structure and reproduction and demonstrate that under natural<br />
conditions newly established bison populations can double<br />
every four to six years. Population numbers are affected by both<br />
density-independent events, such as severe winters and wild<br />
fires, and density-dependent factors such as disease and wolf<br />
predation. While humans were a bison predator for thousands of<br />
years, the advent of firearms greatly increased human predation,<br />
so that by the mid-1800s, an estimated 500,000 plains bison<br />
were killed annually for subsistence and 100,000 for hides. The<br />
human-firearm-commerce combination, it would seem, largely<br />
voided the density-dependent relationship between bison and<br />
human predation until it was almost too late for the <strong>American</strong><br />
bison.<br />
In Chapter 7, C. Gates and co-authors assess the status of<br />
conservation herds using seven criteria: numerical status,<br />
geographic status, population size and class distribution,<br />
opportunity for mate competition among mature males, presence<br />
of wolves, presence of diseases that could affect conservation<br />
status, and occurrence or likely occurrence of cattle-gene<br />
introgression. The designation “conservation herd” is assigned<br />
to herds managed by federal or state/provincial governments<br />
or non-governmental organisations (NGOs) whose mission<br />
is nature conservation. Remarkably, little progress has been<br />
made in recent decades in increasing the number of animals<br />
in conservation herds. From the few hundred that remained in<br />
the late 1800s, the number of animals in conservation herds<br />
increased in the first half of the 1900s, but then levelled off, or<br />
in the case of the wood bison, even declined, while the number<br />
of conservation herds has continued to grow to the present<br />
day. As of 2008, there were 62 plains bison conservation herds<br />
containing about 20,500 animals, and 11 conservation herds<br />
of wood bison containing nearly 11,000 animals. Meanwhile,<br />
starting in the 1980s, the commercial bison industry prospered<br />
with the total population growing to around 400,000 animals<br />
in 2007, roughly evenly divided between the U.S. and Canada.<br />
Although a few conservation herds exceed 1,000 animals, most<br />
conservation herds of both wood and plains bison have fewer<br />
than 400 animals and, in the case of the plains bison, many<br />
are fenced in areas of only a few thousands hectares and not<br />
subject to natural predation. Until recently, there was a wild<br />
bison herd inhabiting a trans-boundary area between Mexico<br />
and the U.S., the only herd meriting conservation status in<br />
Mexico. But now, it has been restricted to a private ranch on<br />
the U.S. side. The <strong>American</strong> bison nearly qualifies for listing as<br />
Vulnerable Ca2(1) under IUCN criteria and is currently listed as<br />
Near Threatened on the IUCN Red List.<br />
As K. Aune and co-authors describe in Chapter 8, bison<br />
conservation must deal with a complex maze of legal and<br />
policy issues. Much of this complexity is due to a history of<br />
bison being treated like livestock. As the authors note, “During<br />
the great restoration period of wildlife management, bison<br />
were routinely classified and managed by state/provincial and<br />
federal agencies across North America as a form of livestock,<br />
while other wildlife were classed and managed as free-roaming<br />
wild animals.” They subsequently provide a detailed review of<br />
the legal status of, and conservation initiatives underway for,<br />
bison in Mexico, the U.S., and Canada. The legal recognition<br />
of bison as wildlife or livestock, or both, varies across various<br />
federal, state, and provincial jurisdictions in North America. For<br />
example, only ten U.S. states, four Canadian provinces and<br />
two territories, and one Mexican state classify bison as wildlife;<br />
all other states and provinces within the bison’s historic range<br />
designate them as domestic livestock. Overlaying this legal<br />
map for bison are several stakeholder groups that manage<br />
bison: public wildlife and land management agencies, Native<br />
<strong>American</strong> groups, non-profit conservation organisations, and<br />
private producers. Reportable diseases present another set<br />
of legal issues that affect international and interstate transport<br />
of bison. Aune et al. suggest that a paradigm shift is required<br />
whereby the public recognises bison as wildlife, and that there<br />
is much greater social tolerance, especially in the agricultural<br />
community, if major progress is to be made in re-establishing<br />
free-ranging bison on their native range. Moreover, large-scale<br />
restoration over big landscapes will typically require partnerships<br />
and co-management among multiple landowners and resource<br />
managers, and more enlightened and coordinated government<br />
regulations and policies.<br />
In Chapter 9, J.E. Gross and co-authors provide guidelines<br />
for population, genetic, and disease management for both<br />
existing conservation herds and for the full recovery of bison<br />
over both the short and long term. As the authors explain,<br />
conservation focuses on retaining existing ecological, cultural,<br />
and genetic characteristics of bison, whereas full recovery<br />
entails a broader vision of bison inhabiting landscapes that<br />
permit the full expression of natural behaviours and ecosystem<br />
interactions that once existed. The guidelines first address bison<br />
behaviour, particularly the importance of ensuring natural mating<br />
systems that involve avoiding a skewed sex ratio and allowing<br />
<strong>American</strong> <strong>Bison</strong>: Status Survey and Conservation Guidelines 2010 xvii