two kinds of experimental results. The
first were the results of Met Lab toxici-
ty experiments with animals in which
the ability of plutonium and radium to
create recognizable and measurable in-
jury, such as death in a certain number
of days, was compared. The results of
these studies did not agree with the as-
sumption, based on alpha energy de-
posited in tissue, that plutonium should
be about 50 times less toxic than radi-
um. When radium or plutonium were
injected in amounts capable of causing
death in 30 days, they were essentially
equal in toxicity. As the dose was low-
ered so that the number of days to
death increased, plutonium did become
less toxic than radium, but the ratio was
typically more like 4 than 50.
The second type of experimental result
that lead to the reduction in the toler-
ance limit were autoradiographic stud-
ies of bone samples that showed how
plutonium and radium were deposited.
Much of both ended up in the bone, but
radium appeared to be distributed
throughout the volume of calcified
bone, whereas plutonium concentrated
on bone surfaces, especially those sur-
faces throughout the more biologically
active portions of the bone, such as the
bone surfaces where the marrow is lo-
cated (Figure 3).
In a report on the May 14 and 15 con-
ference on plutonium, issued July 23 by
the Met Lab, it was postulated that plu-
tonium had a higher level of acute toxi-
city than expected in relation to radium
because of the differences in deposi-
tion. A large proportion of the radium
buried itself “deep in bony structures
where it is relatively innocuous from
the standpoint of acute toxicity.” On
the other hand, plutonium concentrated
“in the endosteal layers of bone close to
the marrow and (at least to a greater
extent than radium) in soft tissues.” In
fact, these same studies found that an-
other heavy-metal radioisotope, poloni-
um-210, was about 2 to 10 times “as
toxic as plutonium per unit of alpha-ray
energy dissipated in the body,” most
likely a result of the fact that polonium
concentrated in “highly radio-sensitive
soft tissues, such as the hematopoietic
and lymphatic tissues themselves.”
The Los Alamos Health Handbook.
On August 17, 1945, Los Alamos is-
sued the Chemistry and Metallurgy
Health Handbook of Radioactive Mate-
rials, outlining the hazards and safety
procedures for radioactive materials.
This handbook put into practice for plu-
tonium what had been learned from the
recent animal and human injection stud-
ies. The introduction stated:
It was deemed essential to indicate
to the reader the intensive effort
being made to eliminate radiation
health hazards: hence, the detailed
description of monitoring instru-
ments and, as an example, the
chemical assay for 49 [plutonium]
and polonium in the urine. . . . The
worker exposed to nuclear radia-
tions is emphatically urged to fol-
low the two basic rules: (1) know
all the possible radiation hazards
in a given job, and, (2) see that
proper protective procedures are
followed in the job.
The handbook included a discussion of
“tolerance” dose, stating that this
“means an upper limit to the radiation
energy absorbed per day indefinitely
which will be ‘absolutely safe,’ i.e.
which will produce no observable im-
pairment of any function of a large
number of healthy humans.” The hand-
book went on to discuss the fact that a
“safety factor” was built into the toler-
ance limit, but that this factor could
vary from individual to individual.
If the average individual stays
within the tolerance limits he can
be practically certain of suffering
no impairment of any of his func-
tions. If he exceeds the tolerance
limits one cannot always predict
what the results will be. In gener-
al, however if the tolerance limits
are not greatly exceeded, the indi-
vidual need not be considered a
“dead duck,” for in all probability
only minor disability may result.
The level established for plutonium was
The Human Plutonium Injection Experiments
200
Los Alamos Science Number 23 1995
Figure 3. Deposition of Plutonium in the Bone
A neutron-induced autoradiograph (magnified 190 times) of portions of trabecular bone
(B) in dog, showing fission tracks from particles of plutonium deposited on the bone
surface (S). Radium, in contrast, deposits throughout the bone volume (B). (In
Radio-
biology of Plutonium. 1972. Betsy J. Stover and Webster S. S. Jee, editors. (Universi-
ty of Utah/Salt Lake City: J.W. Press).)
a body burden of one microgram. If a
level of more than one microgram was
indicated by urine tests, the worker was
to be “removed from further contact
with the material.” This level was es-
tablished by “a persistent excretion of 7
or more counts per minute per 24 hour
sample” (which corresponds to a 1-mi-
crogram body burden at an 0.01-per-
cent daily excretion rate and a 50-per-
cent counting efficiency).
In relation to plutonium, the handbook
added:
For materials such as 49, for
which there is not a large experi-
ence of long-period human expo-
sure, the tolerance amounts are
necessarily set with a conservative
view, thus affording the possibility
of additional safety factor. Lethal
and chronic effects of 49 and Po
are being studied extensively in
animals. The rate of elimination
and the manner of deposition of 49
and Po in tissues of humans is also
being studied. At some later time
the results of experimentation and
experience may lead to an upward
revision of the specified tolerance
amounts. At present it is safe for
the worker to proceed with the
presently accepted tolerance
values, keeping in his favor any
safety factors that may result from
conservatism in specifying the
tolerances.
One of the safety factors was the fact
that it took several weeks for the 0.01
per cent excretion rate to be reached.
For a recent exposure, 7 counts per
minute in urine would correspond to a
body burden lower than 1 microgram.
Thus, there needed to be a “persistent
excretion” at that rate before a person
was actually removed from work with
plutonium.
The handbook also discussed most of
what was known about the relative dan-
gers of plutonium and radium, the dif-
ferences in deposition in the body for
these two metals, details of the testing
process (both obtaining the urine sam-
ples and analyzing them), the various
ways plutonium might enter the body
and the relative dangers of each path-
way, and the fact that plutonium “tends
to be deposited on the surface of the
bone in close approximation to the ra-
diosensitive cells of the bone marrow.”
Hempelmann and his group obviously
wanted the people working with pluto-
nium to be as up-to-date as possible
about the material and its hazards and
to understand what was being done to
protect them.
Further Human Plutonium
Injection Experiments
By late summer 1945, there were still
serious concerns about the Health
Group’s ability to monitor the plutoni-
um workers adequately and about the
type of exposures they were receiving.
Hempelmann documented the situation
in a memo to Kennedy.
This is to confirm our telephone
conversation of 22 June 1945 dur-
ing which we discussed the recent
high exposure of personnel in the
[Plutonium] Recovery Group. At-
tached is a list of all urine counts
of the people in this group and of
high nose counts during the past
month. This indicates, I think, that
the situation seems to be getting
completely out of hand.
The main concern was the fact that, de-
spite “steps to improve their chemical
operations,” it was “a grave medical
problem.” At Kennedy’s request,
Hempelmann reported these facts to
Oppenheimer in a memo on June 26,
stating that “as soon as we have evi-
dence that the men have reached toler-
ance, I shall . . . advise [Kennedy] that
they are to be removed from their
work.”
Also troubling was the fact that the
urine assays and nose-swipe counts did
not correlate well. It was expected that
in some cases, the urine assays would
rise. But this would depend on whether
a high nose-swipe reading was due to
hand contamination or an actual inhala-
tion exposure and then, further, on
whether the form of the plutonium was
soluble or insoluble.
Likewise, there were questions about
the data from the first three studies.
The excretion data for CAL-1 appeared
consistently lower than the others; HP-
12’s data were in doubt because of his
abnormal kidney function; it was far
from certain at what value the excretion
rate leveled off, or even if it did; and
no autopsy tissue samples had been ob-
tained (CHI-1 would die early in Octo-
ber from his diagnosed cancer). More
research was needed—such as a care-
fully controlled study using about 10
patients in which excretion samples
were obtained daily for about three
weeks.
On September 5, 1945, Langham and
Warren met in Rochester with others of
the Rochester group to complete the
overall plan for such a series of plutoni-
um injection experiments in humans. A
summary of the plan written by Lang-
ham states that over three six-week pe-
riods, ten patients would be admitted to
the metabolism ward at Rochester for
the purpose of plutonium injections.
The first two weeks of each six-week
period would be a control period used
to “determine the degree of normalcy
of the metabolism of the subject, collect
blank feces, get the subject on a stan-
dard diet, and get ward attendants and
subjects in the habit of collecting all
urine and feces.” One of the purposes
of the control period would be to estab-
lish “the normal radioactivity content”
of the patient due to elements such as
uranium, thorium, and radium that are
normally ingested in food.
At the end of the control period, each
subject would “be given five micro-
grams of product in a single intra-
venous injection. For the next 24 days
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