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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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Survival, growth and form will be monitored for several years to compare these<br />

characteristics with those of naturally regenerated trees,<br />

MANAGEMENT IMPLICATIONS<br />

Seedfall of western larch <strong>in</strong> 1974 and 1976 and of Douglas-fir <strong>in</strong> 1976 was<br />

sufficient to expect excellent natural regeneration throughout most of the cutover<br />

blocks. However, seedl<strong>in</strong>gs were slow to establish under nearly a1 1 conditions<br />

created by the several comb<strong>in</strong>ations of cutt<strong>in</strong>g methods, util ization 1 eve1 s, under-<br />

story treatments and seedbed preparation. The comb<strong>in</strong>ed effects of scarification<br />

dur<strong>in</strong>g yard<strong>in</strong>g (which occurred on probably no more than five percent of the study<br />

area) and of prescribed broadcast burn<strong>in</strong>g were <strong>in</strong>adequate for the establishment of<br />

sufficient natural regeneration. Most of these seed1 <strong>in</strong>gs are found on m<strong>in</strong>eral soil<br />

exposed dur<strong>in</strong>g sky1 <strong>in</strong>e yard<strong>in</strong>g. Results of this study once aga<strong>in</strong> po<strong>in</strong>t out the<br />

necessity of creat<strong>in</strong>g we1 1-distributed patches of exposed m<strong>in</strong>eral soi 1 on cutover<br />

areas with<strong>in</strong> these habitat types.<br />

Dur<strong>in</strong>g the early 19701s, the western spruce budworm heavily defol iated vulnerable<br />

species and probably decimated the cone crops with<strong>in</strong> the study area. In June 1974<br />

(lower budworm population) cone counts showed the crops were fair to good ip western<br />

larch and poor to fair <strong>in</strong> Douglas-fir and Engelmann spruce, but none In subalp<strong>in</strong>e<br />

fir. However, only the western larch cones matured to disperse much seed. In<br />

nearby stands, without noticeable defoliation <strong>in</strong> the early 19701s, all vulnerable<br />

species produced abundant cones <strong>in</strong> 1974. Probably, the budworm population on the<br />

study area <strong>in</strong> 1974 was sufficiently high and/or the residual effects of previous<br />

years heavy defoliation carried over to greatly decrease the cone production there <strong>in</strong><br />

contrast to the nearby areas without noticeable defoliation. Subsequent seed1 <strong>in</strong>g<br />

counts showed that <strong>in</strong> 1975 only larch regenerated on the study area.<br />

When the land manager must restock an area through natural regeneration but<br />

cannot assure adequate site preparation, the shel terwood system provides conditions<br />

most favorable to seedl<strong>in</strong>g establishment. It not only produces more seed for the<br />

area but also ameliorates the extremes <strong>in</strong> temperature at the surface and reduces<br />

evapotranspiration. Once sufficient regeneration is establ ished, the shel terwood<br />

should be removed to optimize growth opportunities for seedl<strong>in</strong>gs and to ma<strong>in</strong>ta<strong>in</strong><br />

dom<strong>in</strong>ance of shade <strong>in</strong>to1 erant species.<br />

This study demonstrates that any site prepqration performed usually <strong>in</strong>creases<br />

germ<strong>in</strong>ation rates and establ ishment of seed1 <strong>in</strong>gs. Wherever m<strong>in</strong>eral soil was exposed,<br />

seedl <strong>in</strong>gs are now evident. Prescribed burn<strong>in</strong>g enhanced germ<strong>in</strong>ation and <strong>in</strong>itial<br />

survival of seedl<strong>in</strong>gs.<br />

The planted Douglas-fir and Engelmann spruce seedl<strong>in</strong>gs have survived well on all<br />

treatments. If other species had been planted, such as western larch or lodgepole<br />

p<strong>in</strong>e, <strong>in</strong>itial survival probably would have been<br />

e<br />

high. The forest manager may consider<br />

plant<strong>in</strong>g more shade-tolerant species on poorly repared sites because bare root and<br />

conta<strong>in</strong>erized seedl<strong>in</strong>gs are not as subject to t e multitude of adverse site factors as<br />

are new1 y regenerated seed1 i ngs.<br />

The effects of differ<strong>in</strong>g residue utilization standards, or of different under-<br />

story treatments, on growth of natural or planted tree seed1 <strong>in</strong>gs is not evident yet.<br />

These treatments may be more important <strong>in</strong> the later growth of conifers than <strong>in</strong> the<br />

establishment stage.

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