Literature DB >> 14605428

Uptake of cadmium in meals from the digestive tract of young non-smoking Japanese female volunteers.

Yuriko Kikuchi1, Tetsuo Nomiyama, Nami Kumagai, Fumiko Dekio, Takamoto Uemura, Toru Takebayashi, Yuji Nishiwaki, Yukio Matsumoto, Yuri Sano, Kanae Hosoda, Shaw Watanabe, Haruhiko Sakurai, Kazuyuki Omae.   

Abstract

OBJECTIVES: To estimate rates of cadmium (Cd) uptake from the digestive tract and changes in Cd in biological specimens after intake of Cd mainly in rice.
METHODS: Twenty-five young non-smoking Japanese female volunteers (20-23 in age) were recruited and a 20-d experimental study was conducted. With polished rice containing 0.004 ppm and 0.340 ppm of Cd, Meal L and Meal H were prepared. Approximately 12% of total Cd in Meal L and 92% of total Cd in Meal H originated in rice. The volunteers ate Meal L for 11 d to achieve a stable intake-output balance of Cd. Fifteen of the 25 volunteers ate Meal H on the 12(th) day (Group D1), and the remaining 10 ate Meal H on the 12(th), 13(th) and 14(th) day (Group D3). All 25 subjects then resumed the consumption of Meal L to the end of the study (20(th) day). All meals, feces and urine were collected during the study, and Cd intake from the daily meals (Cd-I), Cd in feces (Cd-F) and Cd in urine (Cd-U) were determined. For measurement of Cd in blood (Cd-B), venous blood was collected from all volunteers on the day before the study and again on the 12(th) and 20(th) day; venous blood was also collected from 4-8 volunteers at additional time points.
RESULTS: Mean Cd-I was 4.51 microg/d (range: 1.85-6.93) or 48.48 microg/d (range: 27.98-56.27) when they ate Meal L or Meal H. Cd-F and Cd-B exhibited faster responses to the change in Cd-I than did Cd-U. The Cd(uptake) rate, defined as (1-Cd-F(excess) /Cd-I(excess)) (Fig. 1), was 47.2% (range: -9.4-83.3%) in Group D1 and 36.6% (range: -9.2-73.5%) in Group D3, and the Cd(balance) rate, defined as (1-Cd-F(output) /Cd-I(intake)), was 23.9% (range: -4.0-37.7%) in Group D1 and 23.7% (range: -8.2-56.9%) in Group D3.
CONCLUSIONS: Cd-F and Cd-B are better biological monitoring parameters for assessing change in Cd-I than Cd-U. The Cd(uptake) and Cd(balance) rates appeared to be higher than those in previous papers when ingested Cd mainly originated in rice.

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Year:  2003        PMID: 14605428     DOI: 10.1539/joh.45.43

Source DB:  PubMed          Journal:  J Occup Health        ISSN: 1341-9145            Impact factor:   2.708


  5 in total

1.  Cadmium, environmental exposure, and health outcomes.

Authors:  Soisungwan Satarug; Scott H Garrett; Mary Ann Sens; Donald A Sens
Journal:  Cien Saude Colet       Date:  2011-05

Review 2.  Cadmium, environmental exposure, and health outcomes.

Authors:  Soisungwan Satarug; Scott H Garrett; Mary Ann Sens; Donald A Sens
Journal:  Environ Health Perspect       Date:  2010-02       Impact factor: 9.031

3.  Determination of Trace Metal Levels in the General Population of Korea.

Authors:  Hyun-Jun Kim; Hwan-Sub Lim; Kyoung-Ryul Lee; Mi-Hyun Choi; Nam Mi Kang; Chang Hoon Lee; Eun-Jung Oh; Hyun-Kyung Park
Journal:  Int J Environ Res Public Health       Date:  2017-06-29       Impact factor: 3.390

4.  Plant food intake is associated with lower cadmium body burden in middle-aged adults.

Authors:  Kristine K Dennis; Suzanne E Judd; Jessica A Alvarez; Ka Kahe; Dean P Jones; Terryl J Hartman
Journal:  Eur J Nutr       Date:  2021-02-22       Impact factor: 5.614

Review 5.  Adverse health effects of chronic exposure to low-level cadmium in foodstuffs and cigarette smoke.

Authors:  Soisungwan Satarug; Michael R Moore
Journal:  Environ Health Perspect       Date:  2004-07       Impact factor: 9.031

  5 in total

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