A1447 Relation of tubular dysfunction marker levels with cadmium in urine in non-polluted areas In Japan

Wednesday, March 21, 2012: 16:20
Cozumel 1 (Cancun Center)
Masayuki Ikeda, Research section, Kyoto Industrial Health Association, Kyoto, Japan
Jiro Moriguchi, Clinic, Kyoto Industrial Health Association, Kyoto, Japan
Sonoko Sakuragi, Mibu Office, Kyoto Industrial Health Association, Kyoto, Japan
Fumiko Ohashi, Research section, Kyoto Industrial Health Association, Kyoto, Japan
Handouts
  • ICOH_S~1.pdf (276.9 kB)
  • Introduction
    Previous findings suggest that the dose (in terms of cadmium in urine) -response (tubular dysfunction markers in urine) relationship after environmental exposure to cadmium (Cd) is bi-phasic in a shape of a hockey stick with a very steep slope when Cd exposure exceeds a critical level. The present study was initiated to examine if the dose-response is linear below the critical level of Cd among non-exposed populations.

    Methods
    Data were cited from previous publications on Cd (as an exposure marker), α1-MG, β2-MG, NAG (as three tubular dysfunction markers), creatinine (CR) and specific gravity (SG) in urine obtained from more than 17000 adult Japanese women. The cases were selected for age (50-59 years), CR (0.3-3.0 g/l), and SG (1.010-1.030) so that 5306 cases were available after selection. In ananlyses, observed (non-corrected) values were employed.

    Results
    The relationship of the effect markers with Cd was not linear. In case of β2-MG, the slope of the regression line between Cd (µg/l) (as X) and β2-MG (µg/l) (as Y), 17.6, when Cd was less than 2.5 µg/l, was significantly (p<0.01) steeper than the slope, 6.06 when Cd was >2.5 µg/l. The two regression line crossed at Cd=2.4 µg/l. A steeper slope at lower Cd and shallower one at higher Cd was also the case for α1-MG and NAG, with crossing points at Cd=2.3 and 1.3 µg/l, respectively.

    Discussion
    The relationship between Cd exposure and tubular dysfunction is not bi-phasic but tri-phasic. The dysfunction markers were elevated rather steeply at a low Cd range (<2-3 µg/), rather shallowly in the middle range (up to 5-10 µg/), whereas very steeply when Cd exposure is high (e.g., >10 µg/l) as observed in Cd-polluted areas. Bio-toxicological significance of the tri-phasic relationship deserves further study.