Predictors of erythrocyte cadmium levels in 454 adults in Florence, Italy
Graphical abstract
Introduction
Cadmium (Cd) is associated with a broad spectrum of adverse health effects on humans. Cadmium accumulation in the kidney and bone is known to cause tubular damage, renal dysfunction, osteomalacia, and osteoporosis (Jin et al., 2004; Järup and Akesson, 2009). In addition, cadmium and its compounds are classified as human group 1 carcinogens by the International Agency for Research on Cancer (IARC) as they are implicated in the pathogenesis of cancer of the lung, prostate and kidney (International Agency for Research on Cancer (IARC), 2012). Overall, cadmium represents a very serious threat to human health, and the implementation of measures aiming at reducing exposure to it should be regarded as an important public health priority.
Cadmium occurs naturally in the earth's crust and its environmental availability may increase temporarily due to volcanic activity; however, the most important sources of exposure to cadmium are usually anthropogenic. In fact, cadmium is widely used in industrial processes: it is a component of rechargeable nickel-cadmium batteries, televisions screens and pigments, and it is also used in electroplating in the aircraft industry, in galvanizing steel, and as a thermal neutron absorber in nuclear plants (Godt et al., 2006; Bernhoft, 2013). Humans are exposed to cadmium mostly via inhalation or ingestion. Cigarette smoking is considered as the main source of inhaled cadmium among non-occupationally exposed individuals; inhalation of cadmium fumes may occur in occupational settings as well, for instance during welding or soldering. An additional important anthropogenic source of cadmium emission into the environment is the incineration of cadmium-containing products (Ono, 2013). Cadmium can enter the human body also through diet: the foods highest in cadmium are leafy vegetables, rice, crustaceans and shellfish, offal, and edible mushrooms, and its uptake can be enhanced in case of deficiency of micronutrients such as iron, manganese and zinc (Godt et al., 2006; Bernhoft, 2013; Hajeb et al., 2014; Kippler et al., 2009). After absorption, cadmium is transported in the blood bound to proteins (like albumin and metallothionein), and is deposited mostly in the kidney and liver.
The multiplicity of sources and routes of exposure entails that the biological levels of cadmium may differ substantially between populations, and that a thorough investigation of its main determinants is necessary in order to maximize the effectiveness of any preventive intervention. This task is made even more urgent by the observation that, unlike other pollutants (e.g. lead and mercury), cadmium exposure in the general population does not appear to have decreased in recent decades in Europe (Lundh et al., 2016; Wennberg et al., 2017). Here, we aimed at identifying the main determinants of individual cadmium levels in a series of 454 adults residing in Tuscany, central Italy.
Section snippets
Studied population
This study was conducted within the Florence sub-cohort of the European Prospective Investigation into Cancer and Nutrition (EPIC), a multicentre prospective study that aims to investigate the role of dietary, lifestyle and environmental factors in the aetiology of cancer (Riboli and Kaaks, 1997; Riboli et al., 2002). The Florence-EPIC cohort includes 13,597 healthy volunteers (of which 10,083 women, 74.2%) who were aged 35–65 years at enrolment (1992–198) (Palli et al., 2003). The volunteers
Results
Erythrocyte cadmium levels were above the limit of quantification for all of the 454 study subjects. The distributions were skewed to the right (Fig. 1), and the median concentration was 0.66 μg/L (range 0.18–6.77 μg/L, inter-quartile range 0.43–1.07 μg/L).
Discussion
We studied the determinants of erythrocyte cadmium levels in a population-based sample of 454 adults (94.3% women, mean age 52.2 years) residing in Tuscany, central Italy, who provided a blood sample at the moment of their enrolment in the EPIC-Florence cohort study during 1992–1998. Erythrocyte cadmium levels in our study were fairly in line with those reported in studies conducted in other countries, also outside Europe (Kellen et al., 2007; Rentschler et al., 2014; Borné et al., 2016).
Competing interests
All authors declare they have no conflicts of interest to disclose.
Funding
This work was supported by the Italian Ministry of Health under the call for projects “Finalized Research and Young Researchers, 2011–12”, [grant number GR-2011-02349628]. Laboratory analyses were conducted within the Envirogenomarkers project, which was supported by the European Commission, FP7 programme [grant number 226756]. The funding sources had no role in study design; collection, analysis and interpretation of data; writing of the paper; and decision to submit the article for
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