02.06.2013 Views

Health Risks of Ionizing Radiation: - Clark University

Health Risks of Ionizing Radiation: - Clark University

Health Risks of Ionizing Radiation: - Clark University

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

When we look at an analysis <strong>of</strong> SMRs, for example,<br />

we should consider each estimate in the context<br />

<strong>of</strong> the overall SMR for the cohort. If workers at a<br />

facility have an SMR <strong>of</strong> 0.8 overall then they are a<br />

healthy cohort with mortality rate 20% lower than<br />

average. Judging SMRs for specific diseases by<br />

whether or not they are significantly greater than 1 is<br />

misleading in this case, because they should in fact<br />

be lower than 1 in a healthy cohort. Any SMRs that<br />

are significantly greater than 1 become very strong<br />

evidence <strong>of</strong> an effect.<br />

Another common factor involves time;<br />

researchers <strong>of</strong>ten represent workplace exposure with<br />

a proxy variable like years <strong>of</strong> employment. This is<br />

affected by the fact that sick people are weeded out<br />

<strong>of</strong> employment over the years. A person with lung<br />

cancer, for example, is unlikely to remain working<br />

for very long. This results in a situation where the<br />

people who have been working the longest can be<br />

expected to be unusually healthy. This is known<br />

as the healthy survivor effect. Baillargeon and<br />

Wilkinson (1999) studied the healthy survivor effect<br />

among workers at Hanford; they found that there<br />

was a stepwise decline in the standardized mortality<br />

ratios <strong>of</strong> workers with increasing employment length<br />

and that workers in the highest employment duration<br />

category showed a significant survival advantage<br />

over other workers.<br />

Other methodological limitations associated<br />

with occupational exposure studies include:<br />

• relatively low numbers <strong>of</strong> excess deaths, reducing<br />

precision in risk estimation<br />

• missing or incomplete workplace employment<br />

and exposure records (this is especially true for<br />

older data)<br />

• confounding variables such as smoking that are<br />

difficult to control<br />

• poor records <strong>of</strong> disease incidence leading to a<br />

reliance on mortality data<br />

Despite these limitations, many researchers<br />

look to studies <strong>of</strong> occupational exposure as a key<br />

resource for data on health effects <strong>of</strong> chronic, lowlevel<br />

radiation exposure. These workers constitute<br />

a large population for whom exposure monitoring,<br />

although far from ideal, is relatively thorough.<br />

Furthermore, the majority <strong>of</strong> doses received by<br />

these workers are relatively low. The mean dose<br />

<strong>Radiation</strong> Workers 73<br />

in a study <strong>of</strong> workers from three countries was 40<br />

mSv and 80% <strong>of</strong> workers had doses below 0.05<br />

Sv (Cardis et al. 1995). In a large Canadian study<br />

the mean dose was even lower (6.6 mSv) because<br />

it included exposure in medical pr<strong>of</strong>essions; in this<br />

case 97% <strong>of</strong> workers had doses below 0.05 Sv (Sont<br />

et al. 2001).<br />

Sections 6.2 and 6.3 discuss studies <strong>of</strong> worker<br />

health by facility. Examining facilities individually<br />

can reveal information and risks that “a common<br />

estimator” from a multi-site study may obscure (Ritz<br />

1999). On the other hand, many facility-specific<br />

studies have been inconclusive because the cohorts<br />

are small and because the healthy worker effect<br />

limits meaningful comparisons to analyses within<br />

the cohort. Because <strong>of</strong> this, a number <strong>of</strong> large pooled<br />

analyses have been undertaken, some general and<br />

some focused on specific disease endpoints. These<br />

are addressed in Section 6.4. Section 6.5 presents a<br />

summary and discussion <strong>of</strong> health effects in nuclear<br />

workers.<br />

6.2 US facilities<br />

Hanford. Hanford, managed by the DOE, is<br />

located in Richland, Washington and covers 560<br />

square miles. From 1944 to the late 1980s, Hanford<br />

operated as a plutonium production facility for<br />

the nuclear weapons complex. More than 100,000<br />

people have worked at Hanford over the years. In<br />

our literature review for Hanford it became clear that<br />

there had been something <strong>of</strong> an academic battle over<br />

interpretation <strong>of</strong> the occupational exposure research<br />

for this facility. Stewart and Kneale (1991) provide<br />

some background as follows: In the early years <strong>of</strong><br />

standard setting for occupational radiation exposure<br />

there was a lot <strong>of</strong> fluctuation and disagreement.<br />

The Atomic Energy Commission (AEC) lowered<br />

its exposure limits as risk awareness increased.<br />

However, after hearing that significant risk was<br />

difficult to detect in low-dose survivors <strong>of</strong> the<br />

atomic bomb, the AEC wished to relax its standards.<br />

In 1964 the AEC agreed to sponsor a lifetime health<br />

mortality study <strong>of</strong> all <strong>of</strong> its employees in order to<br />

gather more definitive information by which to set<br />

standards. They hired Thomas Mancuso, <strong>of</strong> the<br />

<strong>University</strong> <strong>of</strong> Pittsburgh School <strong>of</strong> Public <strong>Health</strong>,<br />

to lead the study and Mancuso decided to focus on<br />

data from Hanford. Shortly after Mancuso began his

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!