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Yellowstone's Northern Range - Greater Yellowstone Science ...

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THE NORTHERN RANGE<br />

88<br />

not aware of a decline in big sagebrush anywhere<br />

else on the mule deer winter range, and lacking any<br />

other lines of evidence, we can speculate that the<br />

sagebrush decline may be due to heavy, year-round<br />

use by pronghorn. To further complicate this<br />

question, the sagebrush decline seems to be<br />

restricted to the Wyoming subspecies, and mostly<br />

to high ground such as ridges, upland slopes, and<br />

rolling terrain with a high soil clay component. In<br />

the lower areas and swales where the basin<br />

subspecies dominates, sagebrush is tall, abundant,<br />

and apparently vigorous.<br />

The composition of the northern <strong>Yellowstone</strong><br />

mule deer herd has been estimated each year since<br />

1990 using a helicopter. These surveys show a<br />

steady increase in the proportion of adult males in<br />

the herd, presumably in response to modifications<br />

of hunting regulations promulgated by the Montana<br />

Department of Fish, Wildlife and Parks.<br />

PRONGHORN<br />

Early accounts of the greater <strong>Yellowstone</strong><br />

ecosystem report large numbers of pronghorn in all<br />

the major river valleys radiating out from the<br />

present park area (Figure 7.9). Agriculture,<br />

settlement, and market hunting were probably<br />

responsible for the demise of these large, continuous<br />

populations. Many accounts of the northern<br />

range prior to 1882 also mention frequent sightings<br />

of pronghorn, but these are reports of summering<br />

animals (Schullery and Whittlesey 1992). It does<br />

not appear that the park contains significant winter<br />

range for pronghorn; their winter range is at lower<br />

elevations downstt'eam of the north park boundary,<br />

where they are competing with a growing amount<br />

of human activity and development (Figure 7.10).<br />

Pronghorn is a species of special interest on<br />

the northern range because their numbers have at<br />

times been very low, causing concerns over their<br />

genetic wellbeing and even their long-term survival<br />

as a population entity (Appendix B) (Barmore<br />

1980, Houston 1982, O'Gara 1990, Scott and<br />

Geisser 1996). Lee et al. (1994) added a further<br />

reason for special interest: <strong>Yellowstone</strong> pronghorn<br />

carry a unique genetic element (mtDNA haplotype<br />

J) found in no other pronghorn herd in the west.<br />

Surprisingly, the <strong>Yellowstone</strong> pronghorn contains<br />

more genetic diversity than any other North<br />

American herd studied, yet has never received<br />

stocked pronghorn from elsewhere. The authors<br />

stated:<br />

The pronghorn herd of <strong>Yellowstone</strong><br />

National Park is one of the few remaining<br />

undisturbed populations. The most<br />

parsimonious explanation for the great<br />

amount of mtDNA variation in the<br />

<strong>Yellowstone</strong> herd is that <strong>Yellowstone</strong><br />

was a refuge when other herds were<br />

exterminated or greatly reduced. This<br />

genetic resource should be conserved.<br />

<strong>Yellowstone</strong> pronghorn populations of 550 to<br />

700 were reported in the 1930s, and these increased<br />

to 600 to 800 in the 1940s following the addition of<br />

Figure 7.9.<br />

Pronghorn were<br />

extremely abundant<br />

in the lower river<br />

valleys of greater<br />

<strong>Yellowstone</strong> prior to<br />

the creation of the<br />

park in 1872.<br />

Because of its small<br />

sile alld isolation,<br />

the northern<br />

YellowstOlle<br />

pronghorn<br />

population is at<br />

some risk of<br />

extinction. NPS<br />

photo.

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