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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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Lowest daily water use occurred at the end of the grow<strong>in</strong>g season (previously<br />

def<strong>in</strong>ed as May 2 to October 17) when soil moisture was at its seasonal low and the<br />

frost had already taken its toll of the herbs and shrubs. Interest<strong>in</strong>gly, the under-<br />

story-protected treatments of both clearcuts were the lowest water users at the end<br />

of the grow<strong>in</strong>g season, yet were high mid-season users. I<br />

The most predictable and least variable use patterns were displayed by the<br />

residues-removed treatment followed by the conventional-utilization-and-burn and the<br />

unders tory-protected treatments.<br />

The greatest variation <strong>in</strong> daily water use occurred consistently <strong>in</strong> mid-July on<br />

a1 1 rep1 icates and treatments. Both upper and lower clearcuts consistently demonstrated<br />

the greatest variability <strong>in</strong> the pattern of water use. This observation is<br />

consistent wi th the range <strong>in</strong> treatment diversity that resul ted from the imposi tion of<br />

si lvicul tural and residue treatment comb<strong>in</strong>ations.<br />

The trends shown <strong>in</strong> this study are <strong>in</strong> agreement with Tew (1967), Johnston and<br />

others (1969), and Zeimer (1964). They found that the period of greatest water use<br />

occurred early <strong>in</strong> the grow<strong>in</strong>g season and that average daily water use decreased as<br />

availability of moisture decreased. Tew (1967) reported that 4.7 <strong>in</strong>ches (12 cm) was<br />

used from May 25 to July 13 while 1.2 <strong>in</strong>ches (3 cm) was used from July 13 to September<br />

22. Evapotranspiration data from two sagebrush watersheds <strong>in</strong> northwest and south-<br />

central Wyom<strong>in</strong>g (Sturges 1979) also fits very nicely <strong>in</strong> the lower third of the daily<br />

use envelope that we developed <strong>in</strong> this study (fig. 15). Rich and Thompson (1974)<br />

listed average daily evapotranspiration rates for some mixed conifer species <strong>in</strong> differ-<br />

ent localities. All but three of the rates listed are easily encompassed with<strong>in</strong> our<br />

envelope.<br />

Daily and annual consumptive use rates are be<strong>in</strong>g governed by many factors. Kovner<br />

(1956) suggests that evapotranspiration opportunity is usually related to extent of<br />

cover on an area rather than its character. Cl<strong>in</strong>e (1974) related soil moisture loss<br />

dur<strong>in</strong>g the grow<strong>in</strong>g season to not only degree of occupancy and type of vegetation<br />

exist<strong>in</strong>g on a site, but also aspect and the result<strong>in</strong>g potential evapotranspiration for<br />

a particular site. Cl<strong>in</strong>e and others (1977) reported that on a south slope, <strong>in</strong>vad<strong>in</strong>g<br />

shrub species rapidly reoccupiedothe soil mantle, and after 4 years, the shrub mono-<br />

culture probably extracted more water from the soil dur<strong>in</strong>g the extremely dry summer<br />

than did the orig<strong>in</strong>al stand. Effects of slope and aspect on solar radiation and<br />

subsequent water consumption are also discussed by Cl<strong>in</strong>e and others (1977) as well as<br />

Lee (1964, 1967) and Douglass (1967), and are believed to play a major role <strong>in</strong> regulat-<br />

<strong>in</strong>g consumptive use. Stearns and Carlson (1960) found that soi 1 moisture correlated<br />

best with soi 1 temperature, evaporation-pan data, and solar radiation.<br />

S treamf 1 ow<br />

There were no noticable departures from expected values <strong>in</strong> either peak flow or<br />

base flow of Abbott Creek. The probable reasons for this are: (1) there were no<br />

preharvest streamflow data for mak<strong>in</strong>g comparisons, (2) the watershed is not a closed<br />

system, (3) the hydrologic and geologic divides do not co<strong>in</strong>cide, and (4) the equivalent<br />

clearcut area was only 5 percent of the gauged watershed.<br />

The chemistry of Abbott Creek (at the flume) was not significantly changed accord-<br />

<strong>in</strong>g to Stark (1979, 1980).<br />

Other <strong>in</strong>formation concern<strong>in</strong>g the Abbott Creek watershed appears <strong>in</strong> appendix A and<br />

B. It is presented primarily to document streamflow pattern <strong>in</strong> this dra<strong>in</strong>age and<br />

geographic area.

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