HUMAN HEALTH RISK ASSESSMENT OF CADMIUM
Summary of the 61st JECFA Meeting
A.M. Tritscher
International Programme on Chemical Safety, World Health Organization,
Geneva,
The Joint FAO/WHO
Expert Committee on Food Additives (JECFA) evaluated cadmium at three
of its previous meetings. At the fifty-fifth meeting in 2000 the Committee
retained the Provisional Tolerable Weekly Intake (PTWI) of 7 µg
per kg of body weight, and concluded that the prevalence of renal tubular
dysfunction at various dietary intakes of cadmium serves as a reasonable
basis for risk assessment. The Committee acknowledged that new information
indicates that a portion of the general population may be at risk of
exceeding the current PTWI, but the value was maintained due to lack
of precision in the risk estimates. Additional information that would
help to improve the current risk assessment include human toxicokinetic
data; improved dietary consumption data; studies on the relationship
between biomarkers of renal tubular dysfunction and clinical disease
and mortality; influence of cadmium on calcium metabolism and osteoporosis.
A number of studies have addressed these knowledge gaps and at its recent
61st meeting (2003) the JECFA reviewed this information in
order to re-evaluate cadmium, key conclusions from this meeting are
summarized.
The kidney is the main target organ for chronic cadmium toxicity. In
test species, chronic oral exposure to cadmium results in progressive
histopathological changes in the kidney, including tubular epithelial
cell damage. Renal damage can be measured by increased urinary excretion
of low molecular weight proteins, glucose and amino acids, as well as
by increased urinary cadmium excretion. Decreases in bone calcium and
increased urinary calcium excretion have also been associated with exposure
to cadmium.
In humans, a number of new epidemiological studies investigated the
relationship between (mainly environmental) cadmium exposure and health
effects, such as renal dysfunction, mortality, calcium/bone metabolism.
A number of studies attempted to refine the dose-effect/dose-response
relationship between environmental cadmium exposure and renal dysfunction,
as measured via biomarkers such as urinary cadmium, urinary ß2-microglobulin
and N-acetyl-ß-D-glucosaminidase (NAG). Despite inconsistencies
between studies, it can be concluded that low-level environmental exposure
to cadmium is associated with an increased prevalence of proximal renal
tubular dysfunction. However, several issues regarding biomarkers and
appropriate adjustments were identified, which still render dose-response
evaluations difficult. Environmental cadmium exposure is suggested to
alter calcium metabolism in bone tissue and may increase the risk of
osteoporosis. However, this is difficult to evaluate becausebone metabolism
is influenced by many factors, such as age, nutritional and hormonal
status. The presented studies were hence considered preliminary.
New data on dietary intake, based on national studies, resulted in estimates
of mean cadmium intake ranging from 0.7 to 6.3 µg/kg body weight
per week. Mean dietary intakes based on WHO GEMS/Food regional diets
ranges from 2.8 to 4.2 µg/kg body weight per week. These mean
intake estimates constitute appr. 40 to 60% of the PTWI, indicating
that high consumers may exceed the PTWI. The foods contributing most
to intake include rice, wheat, starchy roots/tubers and molluscs.
Overall the Committee reaffirmed that renal tubular dysfunction is the
critical health outcome and that an excess prevalence of tubular dysfunction
is not expected to occur at urinary cadmium levels below 2.5 µg/g
creatinine. Although some studies, using sensitive biomarkers, indicate
a changes in renal functions at levels below that, there remains appreciable
uncertainty about the long-term health significance of these changes.
Therefore, the PTWI was maintained at 7 µg per kg of body weight.