Possible effects of environmental cadmium exposure on kidney function in the Japanese general population

Objectives: To examine whether the current level of environmental exposure to cadmium (Cd) is associated with kidney dysfunction among general populations in Japan. Methods: A nationwide survey was conducted in Japan from 1991 to 1997 at 30 survey sites (with no known environmental heavy metal pollution), by the collection of 24-h food-duplicate samples, peripheral blood specimens and morning spot urine samples. In practice, 607 non-smoking adult women provided these samples. After being wet-ashed, the samples were analyzed for Cd in food duplicates (Cd-F), in blood (Cd-B) and urine (Cd-U) by inductively-coupled plasma mass spectrometry (ICP-MS). Urine samples were also analyzed for α1-microglobulin (α1-MG), β2-microglobulin (β2-MG) and retinol-binding protein (RBP), creatinine (cr) and specific gravity. Possible tubular dysfunction in association with Cd exposure was examined by simple, multiple and logistic regression analyses, and comparison among three different Cd-dose groups. To minimize the confounding effects of aging, 367 women from 41 to 60 years old were selected and subjected to the same statistical analyses. Results: The analysis of a whole population of 607 women showed that α1-MG and possibly β2-MG increased as a function of Cd-F, Cd-B and Cd-U. When the analysis was repeated with the selected population of 367 women aged 41–60, the Cd dose-dependent changes in α1-MG and β2-MG became less evident. The distribution of the selected population with α1-MG above two low cut-off values of >4.9 and >8.4 mg/g cr or with β2-MG above the lowest cut-off value of >400 μg/g cr, was biased toward the group with higher Cd-Ucr, but such bias was not significant for both α1-MG and β2-MG when higher cut-off values were employed. No bias was detected with RBP. Logistic regression analysis with α1-MG, β2-MG and RBP (with cut-off values given above) in combination with age, Cd-F, Cd-B and Cd-Ucr gave essentially the same results. Conclusions: The evidence for kidney dysfunction was of borderline significance in the present study population for which geometric mean Cd-F, Cd-B and Cd-U were 24.7 μg/day, 1.76 μg/l, and 3.94 μg/g cr, respectively. The findings might suggest at the same time that the safety margin is small for the Japanese general population regarding environmental Cd exposure.

[1]  Dose-response relationship between total cadmium intake and β2-microglobulinuria using logistic regression analysis , 1993 .

[2]  M. Ikeda,et al.  Cadmium levels in the urine of female farmers in nonpolluted areas in Japan. , 1986, Journal of toxicology and environmental health.

[3]  T. Kido,et al.  Dose-Response Relationship between Urinary Cadmium Concentration and β2–Microglobulinuria Using Logistic Regression Analysis , 1996 .

[4]  M J Stock,et al.  The measurement of food and energy intake in man-an evaluation of some techniques. , 1980, The American journal of clinical nutrition.

[5]  M. Ikeda,et al.  Background exposure of urban populations to lead and cadmium: comparison between China and Japan , 1997, International archives of occupational and environmental health.

[6]  M. Moriyama,et al.  Renal tubular function after reduction of environmental cadmium exposure: a ten-year follow-up. , 1993, Archives of environmental health.

[7]  H. Nakagawa,et al.  Significance of elevated urinary human intestinal alkaline phosphatase in Japanese people exposed to environmental cadmium. , 1995, Toxicology letters.

[8]  M. Ikeda,et al.  Cadmium levels in the blood of inhabitants in nonpolluted areas in Japan with special references to aging and smoking. , 1983, Environmental research.

[9]  K. Jung,et al.  Urinary proteins and enzymes as early indicators of renal dysfunction in chronic exposure to cadmium. , 1993, Clinical chemistry.

[10]  H. Nakagawa,et al.  Prognostic factors of renal dysfunction induced by environmental cadmium pollution. , 1994, Environmental research.

[11]  L. Järup,et al.  Renal function impairment in workers previously exposed to cadmium. , 1993, Nephron.

[12]  M. Ikeda,et al.  Chronological changes and inter-regional differences in dietary fiber intakes among middle-aged Japanese women. , 1996, The Tohoku journal of experimental medicine.

[13]  T. A. Davies,et al.  URINARY EXCRETION OF PHENOL BY MEN EXPOSED TO VAPOUR OF BENZENE: A SCREENING TEST , 1965, British journal of industrial medicine.

[14]  C. Tohyama,et al.  Urinary α1‐microglobulin as an indicator protein of renal tubular dysfunction caused by environmental cadmium exposure , 1986, Journal of applied toxicology : JAT.

[15]  M. Ikeda,et al.  The integrity of the liver among people environmentally exposed to cadmium at various levels , 1997, International archives of occupational and environmental health.

[16]  A. Mutti,et al.  Markers of early renal changes induced by industrial pollutants. III. Application to workers exposed to cadmium. , 1993, British Journal of Industrial Medicine.

[17]  T. Kido,et al.  Biological monitoring of cadmium exposure in itai-itai disease epidemiology , 1993, International archives of occupational and environmental health.

[18]  M. Moriyama,et al.  Association between renal tubular dysfunction and mortality among residents in a cadmium-polluted area, Nagasaki, Japan. , 1991, The Tohoku journal of experimental medicine.

[19]  Watanabe Takao,et al.  A semiautomated system for analysis of metals in biological materials and its application to mass determination of cadmium in blood. , 1982 .

[20]  T. Kido,et al.  Dose‐response relationship between total cadmium intake and prevalence of renal dysfunction using general linear models , 1995, Journal of applied toxicology : JAT.

[21]  M. Ishizaki,et al.  Progress of renal dysfunction in inhabitants environmentally exposed to cadmium. , 1988, Archives of environmental health.

[22]  L. Järup,et al.  Dose-response relations between urinary cadmium and tubular proteinuria in cadmium-exposed workers. , 1994, American journal of industrial medicine.

[23]  M. Ikeda,et al.  Determination of lead and cadmium in food and blood by inductively coupled plasma mass spectrometry: a comparison with graphite furnace atomic absorption spectrometry. , 1997, The Science of the total environment.

[24]  J. Angerer,et al.  The determination of metals (antimony, bismuth, lead, cadmium, mercury, palladium, platinum, tellurium, thallium, tin and tungsten) in urine samples by inductively coupled plasma-mass spectrometry , 1997, International archives of occupational and environmental health.

[25]  G. Nordberg,et al.  Biological monitoring of cadmium exposure and renal effects in a population group residing in a polluted area in China. , 1997, The Science of the total environment.

[26]  S. Jackson Creatinine in urine as an index of urinary excretion rate. , 1966, Health physics.