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

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THE NORTHERN RANGE<br />

38<br />

grazed and ungrazed sites (Merrill et al. 1994a,<br />

1994b,1996). In other words, grasses grazed in<br />

winter and spring "caught up" with their ungrazed<br />

counterparts by the end of the growing season.<br />

Singer and Harter (1996) studied the effects<br />

of long-term protection of plants from elk grazing,<br />

"at 8 large ... exc1osures constructed in 1958 and<br />

1962:"<br />

Winter grazing by elk resulted in<br />

less standing crop biomass of grasses<br />

only in 1986, following a drier than<br />

normal spring. Total grasses were not<br />

influenced by grazing in any other year,<br />

and total forbs were not influenced by<br />

grazing in any year ....<br />

Use of exc10sures (that is, ungulate-proof<br />

fences) to study plant communities on the northern<br />

range has been quite productive, but it has also<br />

caused considerable confusion. Critics of park<br />

management sometimes publish photographs of<br />

these exc10sures showing that inside the fence the<br />

plant growth is taller; if the exc10sure contains<br />

shrubs and other woody vegetation, the difference<br />

is even more dramatic. These exclosures are easily<br />

seen at several locations along the road from<br />

Mammoth Hot Springs to the Lamar River Valley,<br />

on the northern range. The implication of the<br />

publishers of the photographs is that the vegetation<br />

condition inside of the fence is what a "healthy"<br />

range should look like, when in fact the vegetation<br />

inside the fence only shows what the range would<br />

look like if it had no large mammals grazing it at<br />

all. As already noted, at least one researcher (Kay<br />

1994a) believes that there were very few if any<br />

large animals on the northern range prior to 1872;<br />

if that were the case, then it might be argued that<br />

the exclosures represent the "natural" condition of<br />

the range. However, until evidence is presented to<br />

demonstrate such a paucity of grazers prehistorically<br />

(evidence that will have to overcome a<br />

mounting body of documentation indicating that<br />

grazers were present and abundant), the exclosures<br />

must be regarded as maintaining the artificial<br />

protection of plants from all large, native herbivores.<br />

Last in the discussion of grassland production,<br />

Pearson et al. (1995) concluded that in the<br />

first few years after the fires of 1988, elk preferred<br />

to graze in burned areas, "presumably because<br />

burning had enhanced the abundance of forage,"<br />

but that "fire effects on northern <strong>Yellowstone</strong><br />

ungulates are likely to be relatively short-lived, and<br />

in the long term, may have minimal impact on<br />

population dynamics compared to winter conditions."<br />

Tracy (1997) found increased aboveground<br />

net primary productivity and forage consumption<br />

on transitional and winter range sites used by elk.<br />

But, results suggested that burning effects, if<br />

present at all, persisted for no more than three<br />

years postfire in most <strong>Yellowstone</strong> grasslands. Fire<br />

had either positive or neutral effects on<br />

aboveground production and the cycling of<br />

nutrients.<br />

FORAGE QUALITY<br />

Grazing enhanced the protein content of the<br />

three most common native northern range grasses<br />

(bluebunch wheatgrass, Junegrass, and Idaho<br />

fescue) between 10 percent and 36 percent (Singer<br />

1996a). Grazing enhanced nitrogen content of<br />

forage plants in three other independent studies<br />

(Coughenour 1991, 1996; Mack and Singer 1992a;<br />

Merrill et al. 1994a, 1996). Grazing slightly<br />

enhanced other nutrient concentrations (calcium,<br />

phosphorus, magnesium, and potassium) in<br />

selected grasses.<br />

NUTRIENT CYCLING<br />

The nutrient dynamics of wildland ecosystems<br />

are quite complex. They are influenced by a<br />

variety of forces, including climate, soils, and the<br />

plant and animal species that inhabit the setting.<br />

Frank et al. (1994) examined the mechanisms<br />

surrounding the sustainability of grazing ecosystems<br />

such as the northern range through the study<br />

of nitrogen cycling. They reported that ungulates<br />

were a "particularly important component" of the<br />

nitrogen budget of the northern range, noting that<br />

the nitrogen flow from the animals to the soil was<br />

about 4.5 times that found in senescent plants.<br />

Their results suggested that herbivores increased<br />

both aboveground and belowground production.

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