Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2013 Sep;121(9):1047-53.
doi: 10.1289/ehp.1306607. Epub 2013 Jun 7.

Associations of urinary cadmium with age and urinary proteins: further evidence of physiological variations unrelated to metal accumulation and toxicity

Affiliations

Associations of urinary cadmium with age and urinary proteins: further evidence of physiological variations unrelated to metal accumulation and toxicity

Agnes Chaumont et al. Environ Health Perspect. 2013 Sep.

Abstract

Background: The current risk assessment for environmental cadmium (Cd) largely relies on the assumption that urinary Cd (U-Cd) is a reliable biomarker of the Cd body burden. Recent studies have questioned the validity of this assumption.

Objectives: We studied the lifetime trend of U-Cd as a function of diuresis, gender, smoking status, and protein tubular reabsorption. We also analyzed the associations between U-Cd and urinary proteins.

Methods: Cd, retinol-binding protein, and albumin were measured in the urine of six cohorts of the general population of Belgium, with a mean age ranging from 5.7 to 88.1 years (n = 1,567). Variations of U-Cd with age were modeled using natural cubic splines.

Results: In both genders, U-Cd decreased to a minimum (~ 0.20 μg/L) at the end of adolescence, then increased until 60-70 years of age (~ 0.60 μg/L in never-smokers) before leveling off or decreasing. When U-Cd was expressed in micrograms per gram of creatinine, these variations were amplified (minimum, 0.15 µg/g creatinine; maximum, 0.70 µg/g creatinine) and much higher U-Cd values were observed in women. We observed no difference in U-Cd levels between never-smokers and former smokers, and the difference with current smokers did not increase over time. Lifetime curves of U-Cd were higher with increasing urinary retinol-binding protein or albumin, a consequence of the coexcretion of Cd with proteins.

Conclusions: At low Cd exposure levels, U-Cd and age are associated through nonlinear and nonmonotonic relationships that appear to be driven mainly by recent Cd intake and physiological variations in the excretion of creatinine and proteins.

PubMed Disclaimer

Conflict of interest statement

The authors declare they have no actual or potential competing financial interests.

Figures

Figure 1
Figure 1
Associations of U-Cd in µg/L (A) or µg/g creatinine (B) with age according to gender in healthy and non­smoking male (n = 405) and female (n = 581) participants. Data were fitted using natural cubic splines with four knots placed at the 20th, 40th, 60th, and 80th percentiles. Differences between males and females were statistically significant (p < 0.05) at ≥ 60 years of age in (A), and at ≥ 20 years of age in (B).
Figure 2
Figure 2
Associations of U-Cd in µg/L (A) or µg/g creatinine (B) with age according to smoking status. Data were fitted using natural cubic splines with three knots placed at the 25th, 50th and 75th percentiles. In adults 18–40 years of age, U-Cd of current and former smokers was significantly higher than that in never-smokers; however, after 40 years of age, the difference was statistically significant only between current and never-smokers. Never-smokers, n = 490; former smokers, n = 213; current smokers, n = 368.
Figure 3
Figure 3
Association between U-Cd and age by tertiles of U-RBP (A) and of U‑Alb (B) in the nonsmoking population (n = 840). Data were fitted using natural cubic splines with three knots placed at 25th, 50th and 75th percentiles. U-Cd values were significantly different between tertiles for U-RBP and U‑Alb from adolescence.

Comment in

References

    1. Aguilera I, Daponte A, Gil F, Hernandez AF, Godoy P, Pla A, et al. Urinary levels of arsenic and heavy metals in children and adolescents living in the industrialized area of Ria of Huelva (SW Spain). Environ Int. 2010;36:563–569. - PubMed
    1. Akerstrom M, Sallsten G, Lundh T, Barregard L.2013Associations between urinary excretion of cadmium and proteins in a nonsmoking population: renal toxicity or normal physiology? Environ Health Perspect 121187–191.;10.1289/ehp.1205418. - DOI - PMC - PubMed
    1. Amzal B, Julin B, Vahter M, Wolk A, Johanson G, Åkesson A.2009Population toxicokinetic modeling of cadmium for health risk assessment. Environ Health Perspect 1171293–1301.;10.1289/ehp.0800317. - DOI - PMC - PubMed
    1. Barr DB, Wilder LC, Caudill SP, Gonzalez AJ, Needham LL, Pirkle JL.2005Urinary creatinine concentrations in the U.S. population: implications for urinary biologic monitoring measurements. Environ Health Perspect 113192–200.;10.1289/ehp.7337. - DOI - PMC - PubMed
    1. Benedetti JL, Samuel O, Dewailly E, Gingras S, Lefebvre MA. Levels of cadmium in kidney and liver tissues among a Canadian population (province of Quebec). J Toxicol Environ Health A. 1999;56:145–163. - PubMed

Publication types

LinkOut - more resources