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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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Figure 3.-- Bymrmrs fireZ<strong>in</strong>e <strong>in</strong>tensity <strong>in</strong> 1-year and 5-year-old<br />

Douglas-fir/larch slash for slashed IS), no sZash<strong>in</strong>g (US), and<br />

near compZete (NC) k ~eahen~s. fie skded areas signal<br />

unacceptabZe hazard.<br />

Load<strong>in</strong>g of fuel smaller than 3 <strong>in</strong>ches <strong>in</strong> diameter was less for near-complete<br />

harvest<strong>in</strong>g than for other treatments. This fuel bed was also more compact as<br />

illustrated by the relative compactness <strong>in</strong> Table 2, Both factors contributed to<br />

1 ower predicted burn<strong>in</strong>g rates. The fuel bed under the near-complete treatment<br />

became very compact--twice that of the sawlog treatment--due to extensive trampl<strong>in</strong>g<br />

and removal of residues. The slash<strong>in</strong>g treatment's fuelbed also was very compact<br />

because of the absence of a fluffy, slashed understory. The least compact (most<br />

porous) fuel bed resulted from the sawlog treatment that had the largest merchantable<br />

diameter 1 imi ts along wi th a slashed understory.<br />

Unlike lodgepole p<strong>in</strong>e at Union Pass, load<strong>in</strong>gs of 3 <strong>in</strong>ch and larger fuels were<br />

left at reasonable levels <strong>in</strong> all treatments (table 2). The reason for this is that<br />

the util i zation standards specified removal of merchantable sound dead wood.

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