Female mice were exposed to a single dose of 0.005 to 5 microg Cd/kg body wt., in order to test the hypothesis that once the Cd-binding capacity of intestinal metallothionein is saturated. Cd becomes more readily available for transfer from the mucosa to the circulatory system, causing an increase in Cd absorption. In this case the binding of Cd to MT would act as a barrier against Cd absorption, thus protecting the organism from accumulation and toxic effects of Cd in target organs such as the kidney. In mice the fractional Cd uptake (% of dose) in the duodenum, which was the main site of Cd uptake in the intestine, was not influenced by the Cd dose 6 h after dosage. However, the percentage of cytosolic Cd associated to MT in the duodenum decreased when the Cd dosage increased from 0.005 or 0.025 microg/kg to 5 microg/kg. Concomitantly, the percentage bound to low-molecular-weight (LMW) ligands increased, indicating saturation of the Cd-binding capacity of MT. Nevertheless, the fractional absorption was not dosage dependent in the dosage interval studied. Moreover, there was no statistically significant correlation between the percentage of cytosolic Cd bound to MT and the percentage of Cd absorbed. Thus, our results do not support the hypothesis that the intestinal Cd absorption is increased when the Cd-binding capacity of intestinal MT is saturated.
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http://dx.doi.org/10.1016/s0378-4274(97)03886-1 | DOI Listing |
Sci Total Environ
January 2025
State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 100049, China; School of Environment, Hangzhou Institute for Advanced Study, University of Chinese Academy of Sciences, Hangzhou 310024, China.
Half-life of cadmium (Cd) in blood is around 3-4 months, which is much shorter than its half-life in human organs (30 years). Promoting the elimination of Cd from the blood is a crucial step in reducing the body's Cd burden. However, there is currently no effective method available to facilitate this process.
View Article and Find Full Text PDFPlant Physiol Biochem
November 2024
College of Environmental and Chemical Engineering, Shanghai University, 99 Shangda Road, Shanghai, 200444, China.
Bioinform Biol Insights
August 2024
Postdoctoral Fellow, Department of Animal Science, Manonmaniam Sundaranar University, Tirunelveli, India.
The mitigation of cadmium (Cd) pollution, a significant ecological threat, is of paramount importance. harbors 2 Cd resistance genes, namely, and . Presently, our focus is on the identification and characterization of the cation-transporting P-type ATPase (cadA) in BC15 through methods.
View Article and Find Full Text PDFBiol Trace Elem Res
January 2025
College of Resources and Environmental Engineering, Guizhou University, Guiyang, 550025, China.
Cadmium (Cd) is one of the most well-known toxic metals capable of entering the human body via the food chain, leading to serious health problems. Human gut microbes play a pivotal role in controlling Cd bioavailability and toxicity within the human gastrointestinal tract, primarily due to their capacity for Cd adsorption and metabolism. In this work, a Cd-resistant bacterial strain, Enterococcus faecalis strain ATCC19433 was isolated from human gut microbiota.
View Article and Find Full Text PDFEnviron Pollut
March 2024
College of Landscape Architecture, Sichuan Agricultural University, Chengdu, 611130, China.
Methyl jasmonate (MeJA), a crucial phytohormone, which plays an important role in resistance to Cadmium (Cd) stress. The cell wall (CW) of root system is the main location of Cd and plays a key role in resistance to Cd toxicity. However, the mechanism effect of MeJA on the CW composition and Cd accumulation remain unclear.
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