MINERAL CYCLING IN .4 DOUGLAS FIR FOREST STAND

Phosphorus was selected in addition to the
monovalent potassium and divalent calcium
cations, These three elements can easily be
tagged with #P, §&Rband “Cafor tracer studies.

This paper will report only the radiological
aspects of movementofthe tracers through the
forest floor and surfacesoil, and upinto thetrees,
STUDY AREA

The studyis conducted in close cooperation

with the Fern Lake Program of the Radiation

Biology Laboratory, University of Washington,
Seattle, Washington.” Fern Lake is located

about 50 miles southwest of Seattle, Washing-

ton. The climate is moderate with a mean
annual temperature of 50°F and an average
annual precipitation of 45 in. The study plots
are located close to the lake in a dense stand of
40-y old Douglas fir trees (Pseudotsuga menziesii
(Mirb.) Franco) about 50 ft high. The fairly
level soil is an Alderwood-like gravelly sandy

lcam originated on glacialtill, The forest floor
is about | in. thick and has a 50 per cent moss
cover. The A, horizon is 4—5 in. deep. The pH
throughout the profile is about 5.3, and the
cation exchange capacity decreases from 12 meq/
100 g at the surface to 5 meq/100 g at a depth of

2 ft.)

METHODS

Each plot consists of a central dominant tree
without close competition from other dominants
(See Fig. 1). The forest floor and/or surface
soil of 225 in.? areas arranged aroundthe central
tree were sprayed with tracer solutions of known
specific activities. Tension lysimeters, installed
under the forest floor and 6-8 in. in the surface
soil, collected soil solutions. The tension lysimeter

consists of a porous plate that can be readily
inserted within a forest soil with a minimumof
disturbance to the overlying system. A tension

placed against the porous plate by a controlled

vacuum system eliminates the soil solution and

air interface problem inherent in the drainage of
most lysimeter designs.'§)
Uptake patterns of the tracers by the central
tree were obtained by periodically sampling
young foliage of midcrown positions. A steel
tower erected alongside the tree facilitated
access to the crown. The return movement of
mineral elements was sampled with litterfall

troughs placed radially from the tree, and a

rubber

channel

sealed

around

the «-4

Rainwash solutions from the troughs and -~ §

were led through mixed bed ion exchanger ;

columns which contained porous plastic 1
to prevent clogging of the resins.

Con, $

siphontube flowmeters were used to mit ;
the flow of solutionsat several samplingpo::
Thedischarge of the flowmeter by siphon ac:
cools a positive temperature coefficientre...
which then causes a relay to activate ane.c |
recorder. Incoming precipitation was meas...
by rain gauges placed on two of the ton-Forest floor and surface soil temperatures w4

1364

recorded continuously at one location in

forest stand. The radioactivity ofa few lysin-

solutions was recorded continuously with the +

of throughflow GM-tubes. A control plu:
monitor background activity due to radioa.fallout products in the samples was maint.
throughout the study.
During 1964, 12.5 per cent of thetotal rai.
activity per plot was applied on the forest 3.,
and 87.5 per cent directly on the surface of ++ |
mineral soil. The forest floor was separated a.

lifted off the application area with a board a:
replaced after treatment of the exposed .,
surface.

Thesolutions, exchangeresins and tree crows

were sampledperiodically. The solution volum,
were determined by weighing to prevent cr».
contaminations. Excess radioactive leachs +
were evaporated in the field in a barrel wit ,
floating heating element.!® A mercury sw:::
disconnected the heating element when =.
solution dropped below givenlevel.
One-liter samples were evaporated and wv.

dized in the laboratory and assayed for ra.
activity. The exchange resins were eluted ».

2--3 volumes of 10 per cent HNO. The ehuswere

evaporated

to

dryness,

oxidized a:

assayed for radioactivity. The foliage samiun

were slowly ashed at 450°C, taken up in \
HNO,, filtered and assayed. Calcium in:
foliage samples of 1964 wasprecipitated ou :
the oxalate method!to reduce the radioac:.
ity due to fallout products.
All samples of 1963 were assayed for i,
activity by the Radiation Biology Labora: -

During 1964 the gammaradiation of Rb 4. &
measured using a 4-in. scintillation crystal 2-. |
multichannel analyzer. Data on recovery

Select target paragraph3