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PE EIE[R-Rg RESEARCH ON - HJ Andrews Experimental Forest

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Figure 1 . Aerial photo of Findley Lake basin indicating<br />

drainage basin of upper lake and two smalle r<br />

ponds.<br />

cepts each of the other two basins as well a s<br />

26 percent of the watershed directly .<br />

The soils of the watershed have bee n<br />

mapped by Bockheim and Ugolini (n .d .) .<br />

Many of the slopes range from 30 to 40 percent<br />

; widespread talus accounts for 16 .2 percent<br />

of the total basin. Soils of mixed materials<br />

are divided as forested, semiforested, an d<br />

nonforested ; they account for 56 .2, 4 .3, an d<br />

1.6 percent, respectively, of the total basin .<br />

The residual soils on the ridges are 17 .5 percent<br />

forested and 4 .2 percent nonforested .<br />

Del Moral (1972) has completed a vegetation<br />

survey of the watershed . Seven vegetation<br />

types were distinguished and their distributions<br />

mapped . Most of the area is timbere d<br />

by relatively homogenous old-growth Pacifi c<br />

silver fir (Abies amabilis) .<br />

Taber' has conducted a preliminary survey<br />

of the terrestrial vertebrate activity in the<br />

1 P. R. Olson, J . S . Bockheim, F . C. Ugolini, an d<br />

others . A terrestrial-lake interface program, Findle y<br />

Lake watershed. Coniferous <strong>Forest</strong> Biome Interna l<br />

Report No . 25 . (In press .)<br />

watershed. The elk (Germs canadensis) and<br />

pikas (Ochotona princeps) have a noticeable<br />

impact on the vegetation of the basin . Migratory<br />

,vertebrates such as deer (Odocoileus<br />

hemionus), elk, and birds could influence the<br />

movement of nutrients in or out of the basin .<br />

In addition, the elk activity in some of the<br />

meadow areas has obviously disturbed th e<br />

soil .<br />

Snow accumulations of 4 m often occur i n<br />

the Findley Lake basin . The open surface<br />

period on Findley Lake is approximately 4<br />

months. The lake frequently is not free of<br />

snow cover until late July and usually start s<br />

to close about mid or late November. A thin<br />

layer of ice will often form in early November<br />

and soon thereafter, snowfall will cover th e<br />

surface. The snowfall accumulates rapidly and<br />

insulates the surface from additional freezing .<br />

The latent heat of the lake water thaws th e<br />

ice layer originally formed and the snowpac k<br />

effectively supports itself . As snow accumulates,<br />

the light penetration is greatly reduced .<br />

In February of 1972 there were 2 .9 m (9 . 5<br />

feet) of snow ; the light readings beneath th e<br />

snowpack were approximately 1 .4 lux-0 .0 3<br />

percent of the surface illumination . Th e<br />

oxygen concentration of the water colum n<br />

was close to saturation except within 2 m o f<br />

the bottom where the oxygen decrease wa s<br />

quite abrupt. Temperatures at this tim e<br />

ranged from 1 0 C at the surface to 3° C a t<br />

25 m .<br />

Limnological surveys were performed b y<br />

Welch (see footnote 1) on a monthly interval<br />

during the open summer period . Findley Lake<br />

is extremely clear with visibility extending to<br />

depths of 15 m . Since the lake is relativel y<br />

deep (about 28 m) and unproductive, th e<br />

hypolimnion during the summer period remained<br />

well oxygenated . Maximum water<br />

temperature noted at the lake surface durin g<br />

the surveys was 18° C . The dominant zoo -<br />

plankton found was Diaptomus shoshon e<br />

with a modest population of Holopedium<br />

gibberum present early in the season. Th e<br />

Diap torn us population persisted after 3<br />

months of snow cover .<br />

The analysis of water samples b y<br />

Spyridakis (see footnote 1) is covered mor e<br />

extensively by Taub et aL(1972). Mean values<br />

16

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