Grazing exclosures were erected in wet sedge
meadow habitat on southern Banks Island at the start of the
1993 growing season. Exclosures (n=5) were established in
areas of high (1.6-1.9 muskox/km2) and low
(0.3-0.4 muskox/km2) muskox density. In
late-August (21-25), we clipped the aboveground standing
crop of forages in plots (n=2) located within and adjacent
to each exclosure. Late-August clipping within and adjacent
to exclosures was repeated annually in 1994, 1996, and
1997. Early snow and freezing temperatures prevented
clipping in late-August 1995. Exclosures in the low density
muskox area were often damaged, and the experiment was ended
in this area after one season; time series data were limited
to the area of high muskox density. Mean aboveground
standing crop (dry weight) of sedge material varied annually
(P<0.05) in both grazed and excluded areas, ca.
500-1100 kg/ha, being greatest in 1997 and lowest in 1993
and 1994. The mean proportion of live sedge material (dry
weight) in aboveground sedge biomass also varied annually
(P<0.05) in both grazed and excluded areas, ca.
0.05-0.40, being lowest in 1996. The aboveground standing
crop of sedge exposed to grazing did not differ (P>0.9) from
that found in areas excluded from grazing, regardless of the
amount of time excluded from grazing. However, the
proportion of live sedge in the late-August aboveground
sedge standing crop in excluded areas increased (P<0.02)
relative to grazed areas over time implying selective
herbivory of green sedge material. At current grazing
levels the data are not indicative of degradation of wet
sedge meadow habitat during summer.
The user agrees to the Terms
of Use of the Government of the Northwest Territories
Site last updated
Tuesday, February 19, 2008