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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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Per unit of depth, there was almost twice as much nitrogen <strong>in</strong> the surface 5 cm<br />

of m<strong>in</strong>eral soil than <strong>in</strong> the next 5-15 cm layer.<br />

Organic matter content<br />

The content of organic matter <strong>in</strong> the surface 5 cm of the undisturbed forest<br />

soil ranged between 5 and 6 percent. In the 5-15 cm layer it decl<strong>in</strong>ed to half this<br />

concentration. The organic fraction of the surface 5 cm under each of the treatments<br />

were:<br />

Forest 6.0 5.2<br />

Broadcast burned 7.2 5.9<br />

Pi 1 ed- burned (under) 6.9 4.1<br />

Pi 1 ed- burned (between) 7.1 4.6<br />

Chi pped-removed 6.6 5.9<br />

Chi pped-returned 7.1 8.6<br />

Logg<strong>in</strong>g, broke up the f<strong>in</strong>e organic debris <strong>in</strong> the A. horizon and <strong>in</strong>corporated<br />

it <strong>in</strong>to the m<strong>in</strong>eral soil beneath, likely caus<strong>in</strong>g the <strong>in</strong>itial <strong>in</strong>crease <strong>in</strong> organic<br />

matter content <strong>in</strong> 1972-1973. Burn<strong>in</strong>g and decomposition of this <strong>in</strong>crement (and of<br />

the residual organic material <strong>in</strong> the surface 5 cm) no doubt produced the decl<strong>in</strong>e<br />

shown <strong>in</strong> 1977 on most treatments. Dur<strong>in</strong>g this timespan new plant growth added<br />

little organic matter to the soil on these clearcut sites; hence, the decrease could<br />

be expected.<br />

Available nutrients<br />

Table 5 shows the amounts of available nutrient elements (except sodium)<br />

extracted from the 1977 soil samples. Total extractable sodium was the same for a1 1<br />

sites--approximately 0.1 meq per 100 g of soil at both depths.<br />

Available phosphorus was almost twice as abundant <strong>in</strong> the surface soils 5 years<br />

after logg<strong>in</strong>g than it was <strong>in</strong> the undisturbed forest. The largest quantity was found<br />

under chip mulch, followed by the soil under burned piles. In contrast, the soils<br />

between burned piles did not differ significantly from those of the forest.<br />

Table 5 expresses potassium, calcium, and magnesium cations <strong>in</strong> the form of<br />

mill iequivalent weights of the total extractable amounts per 100 g of soil. The<br />

total extractable amount is the sum of the exchangeable content plus the water<br />

soluble content. Exchangeable cations comprised 90 percent or more of the total<br />

extractable cations <strong>in</strong> these soils.<br />

Extractable potassium was greatest <strong>in</strong> 1977 at both depths under the burned<br />

piles of debris. Otherwise, the amounts of this element did not differ significantly<br />

among treatments. There was about 20 percent more potassium <strong>in</strong> the surface 5 cm of<br />

soil than <strong>in</strong> the 5-15 cm depth.<br />

Logg<strong>in</strong>g <strong>in</strong>creased slightly the amounts of extractable calcium <strong>in</strong> soils. In<br />

1977 the surface 5 cm of soil under the burned piles conta<strong>in</strong>ed almost twice the<br />

calcium concentration of the undisturbed forest, this amount--14.6 meq per 100 g--<br />

was significantly greater than all others. The highest amount of calcium <strong>in</strong> the<br />

next 10 cm layer also were found under this treatment. Levels of extractable<br />

magnesium, a similar divalent cation, followed the same pattern. There was only

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