American Bison - Buffalo Field Campaign
American Bison - Buffalo Field Campaign
American Bison - Buffalo Field Campaign
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Plate 4.1 Hereford x bison hybrid; cattle gene<br />
introgression is morphologically evident. Photo:<br />
Bob Heinonen.<br />
that the introduction site was isolated from,<br />
and unused by, the wood bison population,<br />
and suggesting that the introduced animals<br />
were too young to carry BTB (Fuller 2002;<br />
Graham 1924). These arguments did not<br />
consider the future habitat needs of the<br />
growing wood or plains bison populations,<br />
nor the likelihood that the two subspecies<br />
would not remain isolated. As well, a<br />
recommendation that only yearlings that<br />
passed a tuberculin test be shipped to<br />
WBNP was rejected (Fuller 2002).<br />
It was not until 1957 that the discovery of<br />
a seemingly isolated herd of 200 animals<br />
near the Nyarling River and <strong>Buffalo</strong> Lake<br />
alleviated fears that wood bison was lost<br />
to hybridisation (van Camp 1989). Canadian Wildlife Service<br />
researchers determined that these animals were morphologically<br />
representative of wood bison (Banfield and Novakowski 1960).<br />
To salvage the wood bison subspecies, bison from the Nyarling<br />
herd were captured and relocated to establish two new herds.<br />
Sixteen animals were moved to the MBS north of Great Slave<br />
Lake in 1963 (Fuller 2002; Gates et al. 2001c), and 22 animals<br />
were successfully transferred to Elk Island National Park (EINP)<br />
east of Edmonton, Alberta in 1965 (Blyth and Hudson 1987).<br />
Two additional calves were transferred to EINP between 1966<br />
and 1968 (Blyth and Hudson 1987; Gates et al. 2001c). Of those<br />
bison transferred, 11 neonates formed the founding herd.<br />
Subsequent studies revealed that there was contact between<br />
the Nyarling herd and the introduced plains bison (van Zyll de<br />
Jong 1986). Although hybridisation within WBNP did not result<br />
in a phenotypically homogenous population (van Zyll de Jong<br />
et al. 1995), genetic distances among subpopulations in the<br />
park are small, indicating that there is gene flow and influence<br />
of the plains bison genome throughout all regions of the park<br />
(Wilson 2001; Wilson and Strobeck 1999). Despite hybridization,<br />
genetic distances between plains and wood bison are generally<br />
greater than those observed within subspecies. Moreover, wood<br />
bison form a genetic grouping on a Nei’s minimum unrooted<br />
tree, suggesting genetic uniqueness (Wilson 2001; Wilson and<br />
Strobeck 1999).<br />
Morphological and genetic evidence suggest that care should<br />
now be taken to maintain separation between these historically<br />
differentiated subspecies. Efforts are in place to ensure<br />
representative wood bison and plains bison herds are isolated<br />
from each other to prevent future hybridisation between these<br />
important conservation herds (Harper et al. 2000).<br />
22 <strong>American</strong> <strong>Bison</strong>: Status Survey and Conservation Guidelines 2010<br />
4.2.2 Domestic cattle x bison<br />
The concept of crossing bison with domestic cattle dates back<br />
to Spanish colonisers of the 16th Century (Dary 1989). There<br />
are many accounts of historical attempts to hybridise bison<br />
and cattle (Coder 1975; Dary 1989; Ogilvie 1979; McHugh<br />
1972; Ward 2000). Private ranchers involved with salvaging<br />
bison had aspirations to combine, through hybridisation, the<br />
hardiness and winter foraging ability of bison with the meat<br />
production traits of cattle (Dary 1989; Ogilvie 1979; Ward 2000).<br />
The Canadian government actively pursued the experimental<br />
production of crossbred animals from 1916-1964 (Ogilvie 1979;<br />
Polziehn et al. 1995).<br />
Historical crossbreeding attempts have created a legacy<br />
of genetic issues related to the introgression of cattle DNA<br />
into bison herds. Introgression refers to gene flow between<br />
populations caused by hybridisation followed by breeding of<br />
the hybrid offspring to at least one of their respective parental<br />
populations (Rhymer and Simberloff 1996). The introgressed<br />
DNA replaces sections of the original genome, thereby<br />
affecting the genetic integrity of a species, and hampering the<br />
maintenance of natural genetic diversity. Many contemporary<br />
bison herds are founded on, and supplemented with, animals<br />
from herds with a history of hybridisation (Halbert 2003; Halbert<br />
et al. 2005a; 2006; Ward et al. 1999; 2000). This extensive history<br />
of hybridisation between these two species raises questions<br />
about the integrity of the bison genome and the biological<br />
effects of cattle DNA introgression.<br />
Fertility problems thwarted many of the original crossbreeding<br />
attempts because crosses result in high mortality for offspring<br />
and mother (Ward 2000). Experimentation has revealed that<br />
crosses of bison females with domestic cattle males produce<br />
less mortality in the offspring than the more deadly reverse