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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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surface. Use of dozers to pile logg<strong>in</strong>g debris has the greatest physical impact on<br />

the surface organic layer--often completely remov<strong>in</strong>g it and always exacerbat<strong>in</strong>g the<br />

physical disturbance from 1 oggi ng.<br />

The immediate physical changes <strong>in</strong> the surface organic layer, the removal of the<br />

forest overstory, and microclimatic changes at and near the soil surface, all<br />

contribute to chemical and physical alteration of both the surface organic horizon<br />

and the m<strong>in</strong>eral soil beneath. This is true for a period of years or even decades<br />

after clearcutt<strong>in</strong>g and slash disposal. Many of the changes cited <strong>in</strong> this study were<br />

recorded at the end of 5 years--long enough after treatment to miss any immediate<br />

and transitory effects, but late enough for more subtle and long-term effects to<br />

have emerged. For example, the data <strong>in</strong> table 4 show an <strong>in</strong>crease <strong>in</strong> potassium <strong>in</strong> the<br />

A. horizon dur<strong>in</strong>g the first year after treatment. The <strong>in</strong>creased amount of this<br />

readily soluble element, however, was largely gone after 5 years. Dur<strong>in</strong>g this time<br />

span, many of the losses or changes <strong>in</strong> the surface organic horizon exhibited their<br />

<strong>in</strong>fluence on measurabl e parameters <strong>in</strong> the m<strong>in</strong>eral soi 1 . For exampl e, the potassium<br />

content of m<strong>in</strong>eral soil had <strong>in</strong>creased under most treatments by 1977 (table 5).<br />

The m<strong>in</strong>eral soil, immediately after logg<strong>in</strong>g and slash disposal, is less severely<br />

impacted than is the surface organic layer. Nevertheless, the m<strong>in</strong>eral soil may be<br />

physically altered. Porosity, bulk density, organic matter content, and related<br />

hydrologic characteristics are often immediately changed (Packer and W i 11 iams 1976,<br />

and this vo~wne). Chemical changes <strong>in</strong> the m<strong>in</strong>eral soil are most pronounced after<br />

thorough leach<strong>in</strong>g by ra<strong>in</strong>fall or snowmelt water. This water dissolves the soluble<br />

components <strong>in</strong> the logg<strong>in</strong>g slash, the ash layer (if fire was employed after logg<strong>in</strong>g),<br />

and the surface organic soil horizon. The water then moves these solutes <strong>in</strong>to the<br />

m<strong>in</strong>eral soil, where they are precipitated and picked up by the ion exchange system,<br />

or where they otherwise alter the chemical characteristics of m<strong>in</strong>eral soil horizons.<br />

The pH of acid soils rises when enough cations are leached from surface<br />

materials. This a1 teration lasted 5 years only under burned piles of slash on the<br />

studied sites (fig. 5). Only here was there a sufficient spike of soluble cations<br />

to have a last<strong>in</strong>g and measurable effect. It is possible, however, that the lower<br />

pH of the slowly decompos<strong>in</strong>g wood chip mulch will result <strong>in</strong> a decrease <strong>in</strong> m<strong>in</strong>eral<br />

soil pH on these sites <strong>in</strong> future years.<br />

The organic matter content of the surface m<strong>in</strong>eral soil <strong>in</strong>creased dur<strong>in</strong>g the<br />

logg<strong>in</strong>g operation. Afterwards the lack of annual additions through 1 i tter-fall<br />

caused a decl<strong>in</strong>e on most treated sites. It is uncerta<strong>in</strong> at this po<strong>in</strong>t <strong>in</strong> time if<br />

organic matter contents will cont<strong>in</strong>ue to decrease on these treated sites due to<br />

decay rates exceed<strong>in</strong>g the <strong>in</strong>put of plant rema<strong>in</strong>s, or if relative stability has been<br />

reached. In general, the content of total nitrogen and, to a lesser extent, phosphorus<br />

will parallel that of organic matter content because almost all of the<br />

nitrogen and about half of the phosphorus are part of organic compounds.<br />

In terms of plant nutrition, the content of available nutrients perhaps was the<br />

most important parameter measured <strong>in</strong> these soils. It must be kept <strong>in</strong> m<strong>in</strong>d, however,<br />

that the laboratory techniques used to measure available nutrients provide only<br />

approximations of what is available for uptake by plant roots. They sometimes are<br />

poor approximations, particularly for forest tree nutrition.<br />

The treatments--especial ly the pi1 <strong>in</strong>g and burn<strong>in</strong>g of slash--are the imp1 ied<br />

cause for significant differences <strong>in</strong> available nutrients on these sites <strong>in</strong> 1977.<br />

Clearcutt<strong>in</strong>g and most slash disposal treatments usually <strong>in</strong>creased available nutrients.<br />

An exception occurred between burned piles, where dozer operations frequently removed<br />

the nutrient-rich surface soil and pushed it <strong>in</strong>to the slash piles. These piles of<br />

logg<strong>in</strong>g debris occupied about 18 percent of the clearcut area. Hence, pil<strong>in</strong>g caused<br />

a five-fold concentration of nutrients held <strong>in</strong> the slash and surface debris on these

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