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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

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