3.0 Affected Environment - Knik Arm Bridge and Toll Authority
3.0 Affected Environment - Knik Arm Bridge and Toll Authority
3.0 Affected Environment - Knik Arm Bridge and Toll Authority
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<strong>Knik</strong> <strong>Arm</strong> Crossing DraftFinal EIS<br />
<strong>Affected</strong> <strong>Environment</strong><br />
Among the fastest growing areas of the state, the Mat-Su is characterized by l<strong>and</strong> clearing<br />
activities associated with settlement <strong>and</strong> road construction. These activities promote the<br />
growth of moose browse <strong>and</strong> in turn increase the number of moose/human conflicts<br />
(Del Frate 2004a). Accidental human-caused moose mortality during the 5-year period<br />
1998-2002 averaged 166 moose killed by highway vehicles <strong>and</strong> 15 by train (Del<br />
Frate 2004a). In 1995, the Glenn Highway (from the Matanuska River north to the junction<br />
with the Parks Highway) <strong>and</strong> the <strong>Knik</strong>-Goose Bay Road ranked fifth <strong>and</strong> sixth, respectively,<br />
for highest moose accident rates in the state (ADOT&PF 1995). Accident rates on the Glenn<br />
Highway along the Palmer Hay Flats SGR have decreased since those reported in 1995. For<br />
the period 1988-1992, the accident rate for this Glenn Highway segment exceeded<br />
1.00 accident per million vehicle miles (MVM) for its entire length (ADOT&PF 1995). The<br />
maximum accident rate for this segment for the period 1999-2003 was 0.32 accidents per<br />
MVM (Terrestrial Mammal Technical Report [KABATA 2006p]). The Big Lake fire in 1996<br />
likely reduced the movement of moose through that area, which has contributed to the lower<br />
moose-vehicle accident rate in that highway segment.<br />
Anchorage<br />
Moose were uncommon in the Anchorage area before the 1940s. However, the development<br />
of Anchorage <strong>and</strong> Fort Richardson in the late 1940s resulted in the creation of moose browse<br />
which increased moose population in the area (Sinnott 2004). Currently in the Anchorage<br />
Bowl, approximately 200–300 moose inhabit the area year-round <strong>and</strong> 700–1,000 inhabit the<br />
area during the winter (ADF&G 2000). In GMU 14C, prime browse occurs in opencanopied,<br />
second-growth willow, birch, <strong>and</strong> aspen st<strong>and</strong>s on burned-over military l<strong>and</strong>s, <strong>and</strong><br />
on several hundred acres of military l<strong>and</strong>s that have been rehabilitated during the last<br />
2 decades (Sinnott 2004). Several thous<strong>and</strong> acres of lowl<strong>and</strong> moose habitat are on military<br />
l<strong>and</strong>s between lower Ship Creek <strong>and</strong> Eagle River (Sinnott 2004). Moose in Anchorage are<br />
primarily found in parks, greenways, <strong>and</strong> undeveloped space, <strong>and</strong> frequently visit suburban<br />
neighborhoods where browse is available (ADF&G 2000). Figure 3.59 shows moose habitat<br />
in <strong>and</strong> around the Study Area.<br />
Hunting regulations vary; moose may be hunted, however, in every Management Area within<br />
GMU 14C (ADF&G 2005d). The average annual moose harvest for GMU 14 from 1999<br />
to 2004 was 587 moose (ADF&G 2005e). About 100 moose are harvested annually in local<br />
hunts, most of which occur on the military reservations (ADF&G 2000).<br />
An average of about 156 moose were killed each year in vehicle collisions in the entire<br />
Anchorage area between 1994 <strong>and</strong> 1999 (ADF&G 2000). The high number of moose-vehicle<br />
accidents in 1994–1995 (about 240) resulted from a severe winter that forced record numbers<br />
of moose into the Anchorage area seeking relief from deep snow.<br />
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