Acute inhalation study in the rat of comparative uptake, distribution and excretion for different cadmium containing materials

Characterization of basolateral-to-apical transepithelial transport of cadmium in intestinal TC7 cell monolayers

Cadmium (Cd) is a toxic metal with an extremely long half-life in humans. The intestinal absorption of Cd has been extensively studied but the role the intestinal epithelium may play in metal excretion has never been considered. The basolateral (BL)-to-apical (AP) transepithelial transport of Cd was characterized in TC7 human intestinal cells. Both AP and BL uptakes varied with days in culture, and BL uptake was twofold higher compared to AP in differentiated cultures. A 50% increase in the BL uptake of 0.5 μM (109)Cd was observed at pH 8.5 in a chloride but not nitrate medium, suggesting the involvement of a pH-sensitive mechanism of transport for chloro-complexes. Fe and Zn inhibited the BL uptake of Cd whereas complexation by albumin had no effect, but the stimulatory effect of pH 8.5 was lost in the presence of albumin. The BL uptake of [(3)H]-MPP(+) and (109)Cd were both inhibited by decynium22 without reciprocal inhibition. MRP2 and MDR1 mRNA levels increased as a function of days in culture. A 25 and 20% decrease in the cellular AP efflux of Cd was observed in the presence of verapamil and probenecid, respectively. In cells treated with BSO, which lowered by 26% the total cellular thiol content, the inhibitory effect of verapamil increased, whereas that of probenecid decreased. These results reveal the existence of a decynium22-sensitive mechanism of transport for Cd at the BL membrane, and suggest the involvement of MDR1 and MRP2 in cellular Cd efflux at the AP membrane. It is conceivable that the intestinal epithelium may contribute to Cd blood excretion.

Genotoxicity of soluble and particulate cadmium compounds: impact on oxidative DNA damage and nucleotide excision repair

Water-soluble and particulate cadmium compounds are carcinogenic to humans. While direct interactions with DNA are unlikely to account for carcinogenicity, induction of oxidative DNA damage and interference with DNA repair processes might be more relevant underlying modes of action (recently summarized, for example, in Joseph , P. (2009) Tox. Appl. Pharmacol. 238 , 271 - 279). The present study aimed to compare genotoxic effects of particulate CdO and soluble CdCl(2) in cultured human cells (A549, VH10hTert). Both cadmium compounds increased the baseline level of oxidative DNA damage. Even more pronounced, both cadmium compounds inhibited the nucleotide excision repair (NER) of BPDE-induced bulky DNA adducts and UVC-induced photolesions in a dose-dependent manner at noncytotoxic concentrations. Thereby, the uptake of cadmium in the nuclei strongly correlated with the repair inhibition of bulky DNA adducts, indicating that independent of the cadmium compound applied Cd(2+) is the common species responsible for the observed repair inhibition. Regarding the underlying molecular mechanisms in human cells, CdCl(2) (as shown before by Meplan, C., Mann, K. and Hainaut, P. (1999) J. Biol. Chem. 274 , 31663 - 31670 ) and CdO altered the conformation of the zinc binding domain of the tumor suppressor protein p53. In further studies applying only CdCl(2), cadmium decreased the total nuclear protein level of XPC, which is believed to be the principle initiator of global genome NER. This led to diminished association of XPC to sites of local UVC damage, resulting in decreased recruitment of further NER proteins. Additionally, CdCl(2) strongly disturbed the disassembly of XPC and XPA. In summary, our data indicate a general nucleotide excision repair inhibition by cadmium compounds, which is most likely caused by a diminished assembly and disassembly of the NER machinery. These data reveal new insights into the mechanisms involved in cadmium carcinogenesis and provide further evidence that DNA repair inhibition may be one predominant mechanism in cadmium induced carcinogenicity.

Characterization of zinc, lead, and cadmium in mine waste: implications for transport, exposure, and bioavailability

We characterized the lability and bioaccessibility of Zn, Pb, and Cd in size-fractionated mine waste at the Tar Creek Superfund Site (Oklahoma) to assess the potential for metal transport, exposure, and subsequent bioavailability. Bulk mine waste samples contained elevated Zn (9100 +/- 2500 ppm), Pb (650 +/- 360 ppm), and Cd (42 +/- 10 ppm), while particles with the greatest potential for windborne transport and inhalation (< 10 microm) contained substantially higher concentrations, up to 220 000 ppm Zn, 16 000 ppm Pb, and 530 ppm Cd in particles < 1 microm. Although the mined ore at Tar Creek primarily consisted of refractory metal sulfides with low bioavailability, sequential extractions and physiologically based extractions indicate that physical and chemical weathering have shifted metals into relatively labile and bioaccessible mineral phases. In < 37 microm mine waste particles, 50-65% of Zn, Pb, and Cd were present in the "exchangeable" and "carbonate" sequential extraction fractions, and 60-80% of Zn, Pb, and Cd were mobilized in synthetic gastric fluid, while ZnS and PbS exhibited minimal solubility in these solutions. Our results demonstrate the importance of site-specific characterization of size-fractionated contemporary mine waste when assessing the lability and bioavailability of metals at mine-waste impacted sites.

The speciation of metals in mammals influences their toxicokinetics and toxicodynamics and therefore human health risk assessment

Chemical form (i.e., species) can influence metal toxicokinetics and toxicodynamics and should be considered to improve human health risk assessment. Factors that influence metal speciation (and examples) include: (1) carrier-mediated processes for specific metal species (arsenic, chromium, lead and manganese), (2) valence state (arsenic, chromium, manganese and mercury), (3) particle size (lead and manganese), (4) the nature of metal binding ligands (aluminum, arsenic, chromium, lead, and manganese), (5) whether the metal is an organic versus inorganic species (arsenic, lead, and mercury), and (6) biotransformation of metal species (aluminum, arsenic, chromium, lead, manganese and mercury). The influence of speciation on metal toxicokinetics and toxicodynamics in mammals, and therefore the adverse effects of metals, is reviewed to illustrate how the physicochemical characteristics of metals and their handling in the body (toxicokinetics) can influence toxicity (toxicodynamics). Generalizing from mercury, arsenic, lead, aluminum, chromium, and manganese, it is clear that metal speciation influences mammalian toxicity. Methods used in aquatic toxicology to predict the interaction among metal speciation, uptake, and toxicity are evaluated. A classification system is presented to show that the chemical nature of the metal can predict metal ion toxicokinetics and toxicodynamics. Essential metals, such as iron, are considered. These metals produce low oral toxicity under most exposure conditions but become toxic when biological processes that utilize or transport them are overwhelmed, or bypassed. Risk assessments for essential and nonessential metals should consider toxicokinetic and toxicodynamic factors in setting exposure standards. Because speciation can influence a metal's fate and toxicity, different exposure standards should be established for different metal species. Many examples are provided which consider metal essentiality and toxicity and that illustrate how consideration of metal speciation can improve the risk assessment process. More examples are available at a website established as a repository for summaries of the literature on how the speciation of metals affects their toxicokinetics.

The risk to the United Kingdom population of zinc cadmium sulfide dispersion by the Ministry of Defence during the "cold war"

OBJECTIVES

To estimate exposures to cadmium (Cd) received by the United Kingdom population as a result of the dispersion of zinc Cd sulfide (ZnCdS) by the Ministry of Defence between 1953 and 1964, as a simulator of biological warfare agents.

METHODS

A retrospective risk assessment study was carried out on the United Kingdom population during the period 1953-64. This determined land and air dispersion of ZnCdS over most of the United Kingdom, inhalation exposure of the United Kingdom population, soil contamination, and risks to personnel operating equipment that dispersed ZnCdS.

RESULTS

About 4600 kg ZnCdS were dispersed from aircraft and ships, at times when the prevailing winds would allow large areas of the country to be covered. Cadmium released from 44 long range trials for which data are available, and extrapolated to a total of 76 trials to allow for trials with incomplete information, is about 1.2% of the estimated total release of Cd into the atmosphere over the same period. "Worst case" estimates are 10 microg Cd inhaled over 8 years, equivalent to Cd inhaled in an urban environment in 12100 days, or from smoking 100 cigarettes. A further 250 kg ZnCdS was dispersed from the land based sites, but significant soil contamination occurred only in limited areas, which were and have remained uninhabited. Of the four personnel involved in the dispersion procedures (who were probably exposed to much higher concentrations of Cd than people on the ground), none are suspected of having related illnesses.

CONCLUSION

Exposure to Cd from dissemination of ZnCdS during the "cold war" should not have resulted in adverse health effects in the United Kingdom population.

Agency for Toxic Substances and Disease Registry's 1997 priority list of hazardous substances. Latent effects--carcinogenesis, neurotoxicology, and developmental deficits in humans and animals

In support of Superfund re-authorization legislation, the Division of Toxicology of the Agency for Toxic Substances and Disease Registry (ATSDR) prepared a chemical-specific consultation document for Congress that identified those chemicals with carcinogenic, neurological, or developmental adverse effects having a latency period longer than 6 years. The review was limited to the top 50 substances listed on ATSDR's 1997 Priority List of Hazardous Substances (Priority List). Among the top 50 chemicals, a review of the technical literature indicated that 38 (76%) were classified as "reasonably anticipated," "possibly," or "probably" capable of causing cancer in humans, based either on human and animal data. Eight chemicals (16%) had well-established cancer latency periods in humans of 6 years or more following exposure. Three substances (6%)--arsenic, creosote, and benzidine--had data indicating latency periods longer than 6 years. The technical literature review likewise confirmed the potential for neurological and developmental effects with a latency of 6 years. Twenty-seven (54%) of the top 50 substances caused acute and/or chronic neurotoxic effects; a number of these also caused neurological effects that persisted beyond 6 years (or the equivalent in animal studies) such as: behavioral problems, neurological deficiencies, reduced psychomotor development, cognitive deficiencies, and reduced IQ. Twenty-eight substances (56%) caused adverse developmental effects in offspring of exposed individuals or animals including increased fetal and infant mortality, decreased birth weights and litter sizes, and growth delays. Latency periods for related chemicals are expected to be similar due to structural and toxicological similarities.

Lung deposition, lung clearance and renal accumulation of inhaled cadmium chloride and cadmium sulphide in rats

Rats were exposed 6 h/day over 10 days to 0.3 mg/m3 of water soluble cadmium chloride and 0.2, 1.0 and 8.0 mg/m3 of insoluble cadmium sulphide, then killed at intervals over a 3-month period for serial measurements of lung, renal and faecal cadmium. CdCl2 and high-dose CdS animals showed a transient increase in lung weight. Clearance of both compounds was biphasic. Approximately 40% of deposited material was cleared during the 10-day exposure period. For CdCl2, only 9% of the lung burden was cleared rapidly after the last exposure (half-life 1.0 days) and 47% slowly (half-life 87 days), leaving a residual lung burden of 44%. For CdS, 41% of the lung burden was cleared rapidly (half-life 1.4 days) and 40% slowly (half-life 42 days), leaving a final residue 19%. In the CdS high-dose group, the retention of CdS in the lung was greater than that in the CdS low-dose groups, indicating that clearance mechanisms may possibly have been impaired in the high-dose group by too great a lung burden. For both compounds, faecal cadmium was initially high. Renal accumulation of cadmium was substantial for CdCl2 during the exposure period and continued over the following months until it represented approximately 35% of the total cadmium cleared from the lung. For CdS, renal accumulation was only 1% of the amount cleared from the lung. The bioavailability of Cd from CdS is thus poor, the majority being cleared from the lungs and excreted in the faeces. However, the bioavailability of inhaled CdS measured as cadmium in the kidney is greater than the bioavailability of orally ingested CdS.