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