no major acersiation of radioactive materials in the botteon
material which is basing picked un by the individual ovrganisns

Sampiing for quantitative determinations -- we have
the laboratory progran goirg on in terms of toxicity studics,
but we are also aware that the salmon fry may not be tho most
sensitive organism that we have te ceal with in the river, so
we are interested in knowins whether any of the population
in 4the river are koing aifected.

This cets back to some quanti-

tative type of samplinsts of river organisns,
Ve started out taking cuantitative samples in a number
of different stations which, as I nmentionod earlicr, were selected
because we thought they were as near the hydrosraphic conditions
as w2 could find thon, This gets to waat Dr, Patrick pointod out
yesterday.

Comparing one station to another, it requires a

terificaliy large nunber of samples in order to try to make
quantitative differences,

These stations we looked at in terns

of both numbers of species and also the quantity of individual
species Which were involved.

The species number compare quite

favorably up and down, but we still get wide fluctuations in
nuubers of organisms betveen different stations, This probably
.

-

points out the kinds of differences that occur even in
.

-*

\
\

Stations which are selected for similarity initially.

‘A

* We have arranzed these things in terus of the activity
¥

.

°

‘density which wo find in the river water which is asseciated
with those, so wa find that the stations clese to the Hanford

1

$

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