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American Bison - Buffalo Field Campaign

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Figure 7.5 Area classes of ranges available for existing bison conservation herds.<br />

7.5 Mate Competition<br />

The sex and age structure of small populations are sometimes<br />

manipulated to reduce the risk of escapes, remove aggressive<br />

animals, compensate for unequal mating by males, alter<br />

fecundity, or to increase the rate of population increase. A<br />

common practice for both small conservation herds and<br />

commercial herds is to remove males before they become<br />

morphologically and behaviourally mature (six to seven years<br />

old and older), when they may become dangerous to people or<br />

other animals and property (e.g., fences). Furthermore, the sex<br />

ratio may be manipulated to maintain only sufficient young males<br />

to ensure fecundity (e.g. 10 males: 100 females). In contrast, in<br />

non-manipulated wild herds the mature male: female ratio can<br />

exceed 50:100 (Gates et al. 1995) and mate competition among<br />

males is assured.<br />

The bison is a polygynous species in which mature males (six<br />

or seven years old) compete vigorously for mating opportunities<br />

(Komers et al. 1992). In the absence of mature males, juvenile<br />

and subadult males are capable of breeding successfully, but<br />

60 <strong>American</strong> <strong>Bison</strong>: Status Survey and Conservation Guidelines 2010<br />

there is little competition among<br />

them for mating opportunities<br />

(Komers et al. 1994a,b). We<br />

considered that the presence of<br />

two or more mature males indicates<br />

the potential for mate competition.<br />

Sixteen percent of plains bison<br />

conservation herds did not contain<br />

mature males. In contrast, two or<br />

more mature males were maintained<br />

in all wood bison conservation<br />

herds, thus providing opportunity for<br />

mate competition.<br />

7.6 Presence of Wolves<br />

Key species, such as bison, have<br />

a disproportionate influence<br />

on the patterns of occurrence, distribution, and density of<br />

other species. Where present, bison influence the structure,<br />

composition, and stability of plant (Campbell et al. 1994; Knapp<br />

et al. 1999) and animal communities (Bogan 1997; Roe 1970;<br />

Truett et al. 2001). Grazers like bison also enhance mineral<br />

availability and nutrient cycling through faeces and urine<br />

deposition, and carcass decomposition (Augustine and Frank<br />

2001; Towne 2000; Wallis DeVries et al. 1998). The presence of<br />

wolves, the only effective predator of bison (aside from humans),<br />

is an indicator that the maximum number of interactions is<br />

possible between bison and other species in an ecosystem. If<br />

wolves are present we assumed that all other natural limiting<br />

factors would likely be present in the ecosystem. Wolves are<br />

associated with only 10% of plains bison conservation herds (6<br />

of 62) in contrast to 82% of wood bison herds (9 of 11).<br />

7.7 Presence of Reportable Diseases<br />

Although diseases may limit bison population growth and<br />

productivity they are unlikely to cause extirpation. However,<br />

the presence of diseases reportable<br />

under federal or state/provincial<br />

statutes may lead to management<br />

interventions that impact<br />

conservation (Chapter 5). The<br />

type of intervention varies with the<br />

disease and jurisdiction (Chapter 5).<br />

For example, captive conservation<br />

herds that test positive for BTB<br />

or brucellosis would normally be<br />

depopulated, while less serious<br />

interventions (such as the use of<br />

Figure 7.6 Number of bison conservation<br />

herds in four size classes.

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