Gender differences in the disposition and toxicity of metals
Introduction
Gender differences in exposure to toxic metals have been reported, and there is increasing evidence that health effects of certain toxic metals are also manifested differently in males and females, due to differences in kinetics, mode of action, or susceptibility. However, the database is small and, with a few exceptions, gender differences in exposure and susceptibility has not been considered in the environmental health risk assessment. As for most other chemicals and environmental pollutants, the health risk assessment on toxic metals have largely been based on data on occupationally exposed men, with the obvious exception of reproductive and developmental effects. Still, the results have been used as if they were representative of the general population, including women, children and the elderly. Even though many epidemiological studies of mixed gender population groups reported data separately for men and women, gender differences were seldom evaluated. In addition, experimental toxicological studies have almost exclusively used male animals. Thus, possible mechanisms, e.g., related to certain hormone interactions, were not detected. A review of recent publications in occupational health epidemiology showed that women are still less often studied than men, and that gender factors are seldom investigated in many mixed studies (Niedhammer et al., 2000).
Based on the more extensive literature on the action and side-effects of therapeutic drugs (Christian, 2001; Gandhi et al., 2004; Miller, 2001), gender-differences in the toxic effect of chemicals that people are exposed to in the working and general environment are to be expected. A meeting under the auspice of the Society for Women's Health Research recently concluded that a greater focus on interdisciplinary, hypothesis-driven research is essential in order to understand potential interactions between sex and environmental exposures on health (Keitt et al., 2004). Research needs to explore sex differences from the molecular and cellular levels to behavioral responses, and should track these effects across multiple generations. Such information is essential for evaluation of mechanisms of action and susceptible groups, and to determine the most effective mitigation measures.
This review focuses on gender differences in health effects of nickel, mercury, lead, cadmium, and arsenic. It serves to provide examples showing the necessity of assessing gender differences in exposures, kinetics and toxicity of chemicals and pollutants.
Section snippets
Nickel
Nickel allergy is an example of gender-specific effects caused by differences in exposure. A number of metals and metal compounds may cause adverse reactions upon contact with the skin (Lidén et al., 2006). Although some are toxic, causing irritant contact dermatitis, ulceration or granuloma, the most common effect is contact allergy. Nickel is the most common cause of contact allergy of all skin sensitizers, and it is also an important cause of hand eczema.
Sensitization to nickel is generally
Cadmium
There are indications that cadmium-related health effects are more common among women than among men. Whether this is due to differences in sensitivity to toxic effects or merely reflects the frequently observed higher body burden of cadmium in women is not clear (Vahter et al., 2002). Besides tobacco smoking, the diet is the main source of environmental cadmium exposure. Cadmium concentrations in food vary considerably, but generally fiber rich foods like cereals, vegetables and shellfish
Lead
Although, environmental exposure to lead has decreased considerably in countries that have banned leaded gasoline, it is still a major environmental health problem in countries that continue to use leaded gasoline, or where people are exposed to deteriorated residential lead-based paint or lead glazed ceramics used for storage and preparation of food (WHO, 1995). Occasionally, family-based workshops processing car accumulators and lead-containing scraps are sources of considerable exposure of
Mercury
The health effects of mercury are highly dependent on the chemical form. The major source of mercury vapor (Hg0) exposure in the general population is dental amalgam and an association between the number of amalgam fillings and the concentrations of inorganic mercury (I–Hg) in blood and urine has been reported (Vahter et al., 2000; WHO, 1991). I–Hg is present in the diet at low concentrations, mainly as Hg2+, and the absorption of ingested I–Hg is also low. Occupational exposure to mercury
Arsenic
Inorganic arsenic is a potent carcinogen, which is ubiquitous in the environment, implying that all people are exposed to some extent, often life-long. Exposure to elevated arsenic concentrations in drinking water is common in many areas world-wide, and probably more than 100 million people are exposed to arsenic above 10 μg/L, which is the drinking water standard in most countries (IARC, 2004). Food, in particular vegetables and rice, may be an additional source of exposure to inorganic arsenic
Conclusions
Gender differences in exposure to toxic metals have been well documented. Less is known about gender difference in susceptibility. An increasing number of studies also point towards differences between men and women in uptake and distribution of cadmium and lead. Obviously, such differences may result in diversities in the prevalence of health effects. Taken together, the database regarding gender differences in metabolism and toxic effects of mercury is still too small to draw any firm
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