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PNNL-13501 - Pacific Northwest National Laboratory

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Figure 2. Argonne human radium data for bone cancer, rolling 50-person average, showing observed fractions of bone sarcomas<br />

plotted on both a. logarithmic and b. linear dose scales. Dose threshold is about 8 Gy as inferred from nonlinear least-squares<br />

fitting.<br />

significantly exposed to an alpha-emitting heavy metal<br />

(Stannard 1988) and have been studied internationally.<br />

Research was conducted by others to verify the Advisory<br />

Committee statement using the latest available data from<br />

Danish (Andersson and Storm 1992; Andersson et al.<br />

1994; Advisory Committee on Radiological Protection<br />

1996), German (van Kaick et al. 1984; van Kaick et al.<br />

1999), Japanese (Kido et al. 1999; Mori et al. 1999a; Mori<br />

et al. 1999b), Portuguese (dos Santos-Silva et al. 1999),<br />

and Swedish (Martling et al. 1999) studies. We conclude<br />

that the apparent threshold may be an artifact of the<br />

assumed 15-year latency period for Thorotrast-initiated<br />

liver cancer, and that the significant, possibly causal, dose<br />

accumulates over a latency period (even for minimal<br />

Thorotrast administrations). However, even at the lowest<br />

dosages of Thorotrast administered, the radiation dose to<br />

liver was great, admitting the possibility of a threshold.<br />

Another trend we noticed in the Thorotrast data was that<br />

the latency period between the time of injection and death<br />

by liver cancer increased with decreasing amount<br />

injected. In the Danish studies (Andersson et al. 1994),<br />

the Kaplan-Meier curves are shifted to the right about<br />

6 years between the high and medium dosage groups, and<br />

are shifted again about 6 years between the medium and<br />

low dosage groups. This trend implies that the dose rate<br />

is inversely related to the latency. Since the latency for<br />

liver cancer from Thorotrast is already significant (48<br />

years to reach 50% cumulative frequency in this study), it<br />

is very possible that a dose rate exists at which the latency<br />

is so long that there is no risk of dying of liver cancer.<br />

There was inadequate data, at present, for us to estimate<br />

this “effective threshold” for Thorotrast dose rate.<br />

280 FY 2000 <strong>Laboratory</strong> Directed Research and Development Annual Report<br />

Human Plutonium Exposure Related to Bone and Liver<br />

Cancer<br />

Two papers (Gilbert et al. 2000, Koshurnikova et al.<br />

2000) shed light directly on the human bone and liver<br />

cancer associated with very high exposures to plutonium.<br />

These authors analyzed dosimetry and medical records for<br />

11,000 workers who began working at Mayak in 1948 to<br />

1958, among whom were 23 cases that had bone cancer<br />

and 60 cases that had liver cancer at death. Of the 5,500<br />

who were monitored for plutonium in urine (beginning in<br />

1970), 10 had bone cancer and 36 had liver cancer.<br />

Stratifying by age and sex and accounting for external<br />

dose on a linear basis, the authors computed relative risk<br />

for the two upper ranges of body burdens compared with<br />

the lowest range (Figure 3). For both bone cancer and<br />

liver cancer the relative risk for cancer in the intermediate<br />

body burden range (1.48 to 7.4 kBq) was not statistically<br />

different from the lowest group. It was only in the highest<br />

group (of 251 individuals) that an increased relative risk<br />

can be seen. The authors did not give skeletal dose values<br />

for all cases, but sufficient information was available to<br />

infer that individuals in the middle group had skeletal<br />

doses on the order of 1 to 7 Gy. Thus, these data suggest<br />

a threshold for osteosarcoma above 7 Gy of alpha dose to<br />

the skeleton.<br />

Impact on Cleanup Standards<br />

If there are thresholds for bone and liver cancer in humans<br />

from relatively high doses of alpha irradiation, as our<br />

investigation shows, then DOE’s cleanup standards and<br />

occupational dose limits for plutonium are too restrictive

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