American Bison - Buffalo Field Campaign
American Bison - Buffalo Field Campaign
American Bison - Buffalo Field Campaign
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9.2.2 Herd-level population and<br />
genetic management<br />
For many conservation herds, the most frequent and contentious<br />
decisions will concern herd level management, especially<br />
population control. Key decisions address how many animals to<br />
maintain, which ones to remove, and how often to remove them,<br />
when to add animals, and where to source them. This section<br />
provides advice for active population management at the herd<br />
level—guidelines for establishing a new herd, maintaining the size<br />
of an existing herd, reducing the size of a herd that has become<br />
much too large, and how to deal with known genetic issues.<br />
9.2.2.1 Soft release procedures<br />
<strong>Bison</strong> may need to be moved to supplement an existing herd,<br />
or to establish a new herd. In such cases, the use of a “soft”<br />
release process should be considered in virtually all cases.<br />
Soft releases typically involve placing animals in a (usually<br />
large) holding facility prior to full release. Holding bison in a<br />
large pen may increase their tendency to remain in the area of<br />
release and establish some degree of site fidelity. <strong>American</strong><br />
Prairie Foundation, for example, held bison for one month in a<br />
large corral prior to release on the <strong>American</strong> Prairie Reserve in<br />
Montana. An additional benefit of a soft release procedure is the<br />
effective quarantine and associated ability to monitor and more<br />
easily re-capture animals if any health issues become apparent.<br />
9.2.3 Establishing a new herd<br />
Establishing and maintaining related, isolated or semi-isolated<br />
herds (i.e., parental and one or more satellite herds) is critical<br />
to long-term species conservation in that multiple herds act to<br />
increase effective population size (N e ) and reduce the total loss<br />
of genetic variation over time (Lande and Barrowclough 1987).<br />
Furthermore, the maintenance of a unique genetic population<br />
in several small herds reduces the probability of accidental<br />
extinction, such as from a natural catastrophe by disease, and<br />
increases the opportunity for local adaptation (Franklin 1980;<br />
Lacy 1987). In theory, and under experimental conditions,<br />
several small groups (e.g., N e about 50) may preserve more<br />
genetic diversity than a single herd with as many individuals as<br />
the smaller herds combined (Margan et al. 1998). Genetic drift<br />
within each related herd can be countered by the occasional<br />
movement of individuals between related herds (Mills and<br />
Allendorf 1996). Therefore, several moderately sized herds<br />
(i.e., more than 300 and fewer than 1,000 animals) of the<br />
same genetic stock can, if managed properly, act as a large<br />
metapopulation with an effective population size sufficient to<br />
impede genetic erosion (Lacy 1987). In this section, we articulate<br />
considerations for the establishment and maintenance of new<br />
bison herds from existing resources.<br />
1. Source<br />
88 <strong>American</strong> <strong>Bison</strong>: Status Survey and Conservation Guidelines 2010<br />
Priority should be given to establishing satellite herds from<br />
extant conservation herds, within the respective original ranges<br />
for wood and plains bison, especially for those herds with unique<br />
genetic characteristics (Halbert 2003; Wilson and Strobeck<br />
1999) and those which appear to be free of domestic cattle<br />
introgression (Ward et al. 1999; Halbert 2003; Halbert et al.<br />
2005b). Beyond this, establishment of herds of mixed ancestry<br />
should be considered to maximise genetic diversity and the<br />
potential for adaptive response.<br />
Although bison are likely to be more readily available from herds<br />
subjected to artificial selection and some level of domestication,<br />
we strongly recommend acquiring bison from “wild” herds not<br />
subjected to these influences.<br />
2. Number of animals<br />
Little specific information is available regarding appropriate<br />
foundation populations sizes. In general, a few (4-10) individuals<br />
should be sufficient to avoid very short-term inbreeding effects<br />
(Senner 1980). However, the loss of variation in such a small<br />
population will be substantial after the first few years (Nei et al.<br />
1975) and additional bison should be imported over a period<br />
of several years to increase genetic variation. If the goal is to<br />
conserve or duplicate most of the genetic material in a source<br />
herd, many more animals are required. Shury et al. (2006)<br />
proposed a base of 200 “founder” animals to preserve most of<br />
the genetic variability in “re-established” wood bison herds.<br />
3. Sex ratio<br />
The initial imported bison should consist of approximately 50% of<br />
each sex, and the herd should be maintained with a balanced sex<br />
ratio to reduce inbreeding and maximise effective population size.<br />
4. Breeding strategy<br />
If a small number of bison are used to found a herd, and<br />
especially if additional bison are not brought into the new herd,<br />
breeding strategies to maximise the transfer of genetic diversity<br />
across generations should be considered (e.g., avoid excessive<br />
breeding by one or a few males). Appropriate genetic tools are<br />
available to accurately assign parentage in bison (Schnabel et<br />
al. 2000; Wilson et al. 2002), and these may be used to assist in<br />
captive breeding decisions by evaluating the breeding success<br />
of individual bulls and relatedness among calves.<br />
5. Age composition and behaviour<br />
<strong>Bison</strong> are social animals and the importance of social structure<br />
within a herd is critical to overall herd health and survival<br />
(McHugh 1958). We recommend establishing a new herd with<br />
both adult and sub-adult individuals to prevent disintegration<br />
of social structure and behavioural anomalies (e.g., foraging<br />
behaviour; Ralphs and Provenza 1999).