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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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Dispersal of sound seed on the upper shelterwood area (block 21) was extremely<br />

variable from 1974 - 1977, averag<strong>in</strong>g 160,000 seeds per acre (395,000 per hectare),<br />

but rang<strong>in</strong>g from 8,000 to 550,000 seeds per acre (20,000 to 1,359,000 per hectare)<br />

at the 20 sampl<strong>in</strong>g po<strong>in</strong>ts. Heaviest seedfall (averag<strong>in</strong>g 204,000 sound seeds per<br />

acre, or 504,000 per hectare) occurred on the south half of the area. An average of<br />

117,000 sound seeds per acre (289,000 per hectare) fell on the north ha1 f of the<br />

area. Because the heavier seedfall <strong>in</strong> 1974 was on the area that was prescribed<br />

burned <strong>in</strong> September 1975, many of the seedl<strong>in</strong>gs that germ<strong>in</strong>ated <strong>in</strong> the spr<strong>in</strong>g of<br />

1975 were killed by the fire.<br />

Dur<strong>in</strong>g the period September 23 - October 17, 1974, seed dispersal followed a<br />

characteristic pattern on the study units. Greatest seedfall occurred dur<strong>in</strong>g the<br />

w<strong>in</strong>dy portions of the day (fig. 8).<br />

NOON<br />

HOUR (M. 5. T. I<br />

Figure 8.--Average number of seed caught per hour <strong>in</strong> four seed coZZectors<br />

and average u<strong>in</strong>d veZocity fm.p. h, ) by hour of day, Corm ExperimentaZ<br />

Forest. CoZZections of seed were made dur<strong>in</strong>g 20 days of the period<br />

September 23 through October 17, 1974; w<strong>in</strong>d measurements were taken<br />

each day of the period.<br />

Temperature, humidity and probably other factors <strong>in</strong>fluenced the amount of seed<br />

dispersed. Figure 8 shows averages only; periods of high seedfall usually were<br />

associated with ups1 ope (easterly) w<strong>in</strong>ds of greater than average el oci ty, lower<br />

than average humidity and warmer than average temperature, Because seed counts were<br />

not made dur<strong>in</strong>g the hours of 1600 through 0700, an average of overnight seedfall is<br />

shown <strong>in</strong> figure 8. Seedfall probably <strong>in</strong>creased dur<strong>in</strong>g the hours of 2000 through<br />

2200, <strong>in</strong>stead of rema<strong>in</strong><strong>in</strong>g constant as shown <strong>in</strong> figure 8.<br />

Seed Loss<br />

The amount of seed eaten or otherwise removed from the seedbed between the time<br />

of seedfall <strong>in</strong> 1974 and germ<strong>in</strong>ation <strong>in</strong> May 1975 was estimated by count<strong>in</strong>g the seed<br />

<strong>in</strong> seed traps and <strong>in</strong> adjacent duff samples at the time of em<strong>in</strong>ation <strong>in</strong> the spr<strong>in</strong>g.<br />

The data show that only about 9 percent of the sound seed 9 mostly western larch)<br />

dispersed <strong>in</strong> 1974 was available for germ<strong>in</strong>ation <strong>in</strong> May 1975; the amounts ranged from<br />

3 percent on clearcuts to 16 percent <strong>in</strong> uncut timber.

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