Felix Ayala-Fierro

Effects of micronutrients on metal toxicity.

There is growing evidence that micronutrient intake has a significant effect on the toxicity and carcinogenesis caused by various chemicals. This paper examines the effect of micronutrient status on the toxicity of four nonessential metals: cadmium, lead, mercury, and arsenic. Unfortunately, few studies have directly examined the effect of dietary deficiency or supplementation on metal toxicity. More commonly, the effect of dietary alteration must be deduced from the results of mechanistic studies. We have chosen to separate the effect of micronutrients on toxic metals into three classes: interaction between essential micronutrients and toxic metals during uptake, binding, and excretion; influence of micronutrients on the metabolism of toxic metals; and effect of micronutrients on secondary toxic effects of metals. Based on data from mechanistic studies, the ability of micronutrients to modulate the toxicity of metals is indisputable. Micronutrients interact with toxic metals at several points in the body: absorption and excretion of toxic metals; transport of metals in the body; binding to target proteins; metabolism and sequestration of toxic metals; and finally, in secondary mechanisms of toxicity such as oxidative stress. Therefore, people eating a diet deficient in micronutrients will be predisposed to toxicity from nonessential metals.

Glutathione, albumin, cysteine, and cys-gly effects on toxicity and accumulation of mercuric chloride in LLC-PK1 cells.

Speciation plays a profound if not dominant role in both transport and toxicity of Hg(II). Hg(II) has a high affinity for sulfhydryl groups. The formation constant for Hg2+ and the anionic form of a sulfhydryl group R-S- is > or =10(10) higher than that for the carboxyl or amino groups. The kidneys are the target organ for Hg(II) toxicity and the primary site of Hg(II) accumulation. Sulfhydryl groups have been implicated in both transport and nephrotoxicity; however, the role endogenous thiol compounds play in these parameters is not clear. The roles that albumin, glutathione, and the glutathione-derived complexes cysteinylglycine and L-cysteine play in toxicity and accumulation of HgCl2 were studied in LLC-PK1 cells incubated with different Hg(II):thiol ratios. In cysteine-containing medium, almost all 1:2 Hg(II):thiol complexes protected against Hg(II) toxicity up to 120 microM Hg, increased membrane-bound Hg(II), and decreased intracellular Hg(II) accumulation. In cysteine-free medium, all 1:1 Hg(II):thiol complexes were as toxic as uncomplexed Hg(II), and almost all 1:2 Hg(II):thiol complexes protected at > or =20 microM Hg, except albumin, which protected at < or =20 microM Hg. In cysteine-free but cystine-containing medium, two 1:1 Hg(II):thiol complexes were toxic at > or =80 microM Hg and two provided complete protection. All 1:2 complexes provided protection at 80-160 microM Hg. This investigation used defined media to demonstrate that mercury cytotoxicity in LLC-PK1 cells was dependent on Hg(II) concentration, the ligand, and the presence of a cysteine source for the cells. These effects were only partially explained by intracellular Hg(II) levels.

Disposition, toxicity, and intestinal absorption of cobaltous chloride in male Fischer 344 rats.

The absorption and disposition of inorganic cobalt salts after oral administration have not been well characterized. The objectives of this study were to compare in vivo results with cobalt transport through the in vitro everted small intestine and to relate the disposition results to a biochemical indicator of cobalt toxicity. Cobalt chloride was given to male Fischer 344 rats orally at 33.3 mg Co(II)/kg or intravenously at 4.16 mg Co(II)/kg. By 36 h, 74.5% of the oral dose was eliminated in the feces. The liver, kidney, and heart accumulated cobalt to the greatest extent. Following the single oral dose, the blood cobalt concentration-time curve was triphasic, peaked at 3.2 h, and had an absorptive half-life of 0.9 h, an elimination phase half-life of 3.9 h, and a terminal elimination half-life of 22.9 h. Following intravenous administration, 10.1% of the dose was excreted in the feces, indicating that cobalt can be secreted in the bile. Following a single intravenous injection, the concentration-time curve displayed three segments. The first segment, which occurred during the first 4 h, had a rapid half-life of 1.3 h. The second phase, from 4 to 12 h, demonstrated a slower clearance rate with a half-life of 4.3 h. The final and slowest phase, from 12 to 36 h, had a half-life of 19 h. Intestinal jejunal ring experiments indicated that cobalt transport has both active and passive components; however, cobalt transport through the in vitro rat everted duodenum indicated that cobalt transport had almost exclusively passive components with facilitated diffusion. The finding that uptake was saturable may explain the small extent of absorption following oral dosing. Heme oxygenase studies following subcutaneous and intravenous administration resulted in an increase in activity (twofold) over controls, while oral administration did not. We concluded that the extent of cobalt absorption across the gastrointestinal tract is incomplete, and that the concentration administered and the route of exposure may determine its systemic toxicity.

Systemic indicators of inorganic arsenic toxicity in four animal species.

The effect of arsenic compounds depends on the chemical form and is specific for certain organs. The lack of specific biological indicators for the effects of each arsenic species makes it difficult to differentiate their toxicity. Five prospective biological indicators of systemic toxicity were examined at time points ranging from 15 min to 24 h using male Sprague-Dawley rats, B6C3F1 mice, Golden-Syrian hamsters, and Hartley guinea pigs, following intraperitoneal dosing with 0.1 and 1 mg/kg sodium arsenite. Rats and mice were also dosed with 1 mg/kg sodium arsenate. Total blood arsenic levels were determined in all animal species to show that exposure occurred and as an index of the severity of the change is an indicator of toxicity. Total blood arsenic levels were increased in all animal species. This increase was dose, arsenic species, and animal dependent. Renal pyruvate dehydrogenase activity was significantly decreased at early time points in mice, hamsters, and guinea pigs, and at later time points in rats dosed with arsenite. Rats and mice dosed with arsenate also exhibited PDH decrease at early time points. Blood hematocrit and glucose were increased in the rat and guinea pig, respectively, after arsenite administration. Creatinine and urea nitrogen were found to be unresponsive to arsenic in most animal species. Data suggested that the mouse and secondly the hamster appear to be the most appropriate animal models for the study of acute arsenic toxicity.The effect of arsenic compounds depends on the chemical form and is specific for certain organs. The lack of specific biological indicators for the effects of each arsenic species makes it difficult to differentiate their toxicity. Five prospective biological indicators of system ic toxicity were examined at time points ranging from 15 m in to 24 h using male Sprague-Dawley rats, B6C3F1 mice, Golden-Syrian hamsters, and Hartley guinea pigs, following intraperitoneal dosing with 0.1 and 1 mg/kg sodium arsenite. Rats and mice were also dosed with 1 mg/kg sodium arsenate. Total blood arsenic levels were determined in all animal species to show that exposure occurred and as an index of the severity of the change is an indicator of toxicity. Total blood arsenic levels were increased in all animal species. This increase was dose, arsenic species, and animal dependent. Renal pyruvate dehydrogenase activity was significantly decreased at early time points in mice, hamsters, and guinea pigs, and at later time points in rats dosed with arsenite. Rats and mice dosed with arsenate also exhibited PDH decrease at early time points. Blood hematocrit and glucose were increased in the rat and guinea pig, respectively, after arsenite administration. Creatinine and urea nitrogen were found to be unresponsive to arsenic in most animal species. Data suggested that the mouse and secondly the hamster appear to be the most appropriate animal models for the study of acute arsenic toxicity. the acute toxicity of DMA is lower than that of the inorganic (Marafante et al., 1985). Each of these arsenic species has commercially and each has its own toxicity. Assigning toxic a particular species has been complicated by the finding that can, in some cases, metabolize one arsenic species to other et al., 1999). Environmental inorganic arsenic compounds metabolized, sometimes to other toxic intermediates (Cullen et Exposure to gallium arsenide (Webb et al., 1986) and exposure (Fowler & Weissberg, 1974) lead to pulmonary and blood toxicity, The arsenic species that induce toxicity in either case are not known. The development of biological indicators that differentiate As(III), As(V), and AsH3 toxicity could make it possible to the mechanisms of toxicity of some arsenic compounds. An indicator of arsenic exposure would show significant upon very-low-dose exposure and would respond quantitatively manner to each different chemical species of arsenic.

Cytotoxic effect of three arsenic compounds in HeLa human tumor and bacterial cells.

Numerous epidemiological studies suggest that arsenic (As) compounds are carcinogens, however, recent data have renewed the interest in their anticarcinogenic properties. The cytotoxic effects of three arsenic compounds were assessed: sodium arsenite, sodium arsenate and sodium cacodylate, representing the trivalent and pentavalent species of arsenic, along with a dimethylated pentavalent arsenic species. HeLa cells and Salmonella typhimurium (strains TA98 and TA100) were exposed to As compounds and the cytotoxic effects were evaluated. Alterations on RNA and DNA synthesis in HeLa cells were also examined. All arsenic compounds produced a dose-dependent inhibition on colony formation and DNA synthesis in HeLa cells, yet any of them significantly influenced RNA synthesis in these cells. No evidence of arsenic-induced mutagenicity or antimutagenicity was observed using the Ames assay. In bacterial cells, only sodium arsenite caused a dose-dependent inhibition of colony formation.Collectively, these results indicate that in both, HeLa and S. typhimurium cell systems, only trivalent sodium arsenite can act as an effective inhibitor of cell growth. The possible mechanism(s) of the cytotoxic effect of arsenite in these two different cell systems might be due to its reactivity with intracellular sulfhydryl groups.

Structural alterations in the rat kidney after acute arsine exposure.

The mechanism of arsine (AsH3) toxicity is not completely understood. In this investigation, the toxicity of AsH3 and AsH3-produced hemolytic products was determined in primary culture of renal cortical epithelial cells and in the in situ isolated rat kidney. The objective of this study was to model kidney dysfunction caused by AsH3 exposure. The hypothesis was that unchanged AsH3 and AsH3-produced hemolysate that may contain arsenite (As(III)) as metabolite are both responsible for renal toxicity. Toxicity in isolated cells was determined by 2, 3-bis[2-methoxy-4-nitro-5-sulfophenyl]-2H-tetrazolium-5-carboxanilide inner salt (XTT) bioreduction, intracellular potassium (K+), and lactate dehydrogenase (LDH) leakage. Data from XTT bioreduction showed that most toxicity occurred at 1 hour and was independent of the arsenic species. At 4 hours, the observed toxicity depended on the arsenic species and was generated by As(III). In the isolated cells, the As(III)-spiked hemolysate produced similar toxicities with regard to intracellular K+ and LDH. The AsH3-hemolysate only affected LDH at 1 hour. Unchanged AsH3 was very toxic to the isolated rat kidney. In this system, after 10 minutes exposure to AsH3, the effects of toxicity were observed mainly in the glomerular and peritubular endothelial cells. Tubular epithelial cells also presented early signs of toxicity. The AsH3-hemolysate was not toxic after a 10-minute exposure. These data suggested that early cytotoxicity caused by unchanged AsH3 results in kidney dysfunction, produced by AsH3, and later by the formation of a hemolysate that may contain As(III). These data may be important in understanding the renal toxic effects after AsH3 intoxication.

LLC-PK CELLS AS A MODEL FOR RENAL TOXICITY CAUSED BY ARSINE EXPOSURE

The mechanisms of arsine (AsH3) toxicity are not completely understood. Studies were undertaken to determine AsH3 and arsenite [As(III)] toxicity in a renal tubular epithelial cell line to model kidney dysfunction caused by AsH3 exposure. The hypothesis was that As(III) is the toxic metabolite responsible for the renal toxicity of AsH3. There was a concentration- and time-dependent toxic response after As(III) incubation. As(III) produced significant LDH leakage as early as 1 h and intracellular potassium loss at 5 h. AsH3 produced no changes in these parameters. AsH3 affected neither potassium nor LDH levels over 24 h and up to 1 mM AsH3 concentration. In this system, As(III) induced LDH leakage before K+ loss. Oxidative stress-like toxicity effects were also studied by determining levels of glutathione (GSH), glutathione disulfide (GSSG), and heat-shock protein 32 (Hsp32) levels. GSH levels were not markedly affected by any arsenical over a 6-h period or up to 100 microM concentration of the arsenical. However, 100 microM AsH3 significantly increased GSSG levels as early as 30 min and reached a maximum at 2.5 h. Incubation with 10 microM AsH3 was sufficient to significantly increase GSSG levels. As(III) had no marked effect on GSSG. Both arsenicals (50 microM) produced a slight increase (about threefold) in Hsp32 levels after 4-h incubation. These results showed that unchanged AsH3 produced oxidative stress-like toxic effects without producing cell death. However, similar As(III) concentrations induced the stress response and were toxic to the cells. These data indicated that AsH3 is not directly toxic to LLC-PK1 cells.The mechanisms of arsine (AsH3) toxicity are not completely understood. Studies were undertaken to determine AsH3 and arsenite [As(III)] toxicity in a renal tubular epithelial cell line to model kidney dysfunction caused by AsH3 exposure. The hypothesis was that As(III) is the toxic metabolite responsible for the renal toxicity of AsH3. There was a concentration- and time-dependent toxic response after As(III) incubation. As(III) produced significant LDH leakage as early as 1 h and intracellular potassium loss at 5 h. AsH3 produced no changes in these parameters. AsH3 affected neither potassium nor LDH levels over 24 h and up to 1 mM AsH3 concentration. In this system, As(III) induced LDH leakage before K+ loss. Oxidative stress-like toxicity effects were also studied by determining levels of glutathione (GSH), glutathione disulfide (GSSG), and heat-shock protein 32 (Hsp32) levels. GSH levels were not markedly affected by any arsenical over a 6-h period or up to 100 µM concentration of the arsenical. However, 100 µM AsH3 significantly increased GSSG levels as early as 30 min and reached a maximum at 2.5 h. Incubation with 10 µM AsH3 was sufficient to significantly increase GSSG levels. As(III) had no marked effect on GSSG. Both arsenicals (50 µM) produced a slight increase (about threefold) in Hsp32 levels after 4-h incubation. These results showed that unchanged AsH3 produced oxidative stress-like toxic effects without producing cell death. However, similar As(III) concentrations induced the stress response and were toxic to the cells. These data indicated that AsH3 is not directly toxic to LLC-PK1 cells.

Absorption and disposition of cobalt naphthenate in rats after a single oral dose.

The absorption and disposition of inorganic cobalt salts after oral administration have not been completely characterized. The objective of this project was to investigate the absorption and disposition of cobalt naphthenate in Fischer 344 rats following a single oral dose. Cobalt naphthenate was given orally at 3 doses: 0.333, 3.33, or 33.3 mg Co(II)/kg. Tissues, urine, and feces were collected over a 36-h period from the low- and high-dose groups; blood was collected from all 3 dose groups. The majority of the dose in both the low- and high-dose groups was excreted in the feces (42% and 73.1%, respectively), indicating that cobalt was incompletely absorbed from the gastrointestinal tract following oral dosing. The percent of the dose excreted in the urine was similar for low and high doses (31.8% and 26.3%, respectively). Cobalt concentrations were found to be highest in the liver and kidneys. The blood versus time cobalt concentration curves for the low-dose, intermediate-dose, and high-dose groups were elevated 4- to 5-fold, 14- to 25-fold, and 25- to 60-fold over control blood levels, respectively. The peak plasma concentrations of 0.6 and 1.7 microg Co(II)/ml occurred at approximately 4.3 h for the intermediate-dose group, and 3.3 h for the high-dose group. The terminal elimination half-lives were 24.7 and 24 h for the intermediate- and high-dose groups, respectively. Thus, although the extent of cobalt absorption as indicated by the blood concentrations and areas under the blood-time curves was not proportional to dose, the calculated pharmacokinetic values for the time to peak blood concentration and the apparent elimination rate constants were independent of dose. The amount excreted in the urine was also proportional to the dose. These apparent anomalies were not related to protein binding in blood.

Arsenic Metabolism After Pulmonary Exposure

Publisher Summary Inorganic arsenic (Asi) compounds are oxidized, reduced, methylated, and complexed with glutathione in vivo . Aposhian and coworkers showed that arsenate reduction and arsenite and MMA methylation activities were different in each organ and animal species. Arsenate reduction was found in all organs and animal species, but methylation activity appeared to be absent in some species. Where present, methylation activity was found in all organs studied except the red blood cell. Methylation of inorganic arsenicals has been associated with decreased acute toxicity, while reduction has been associated with increased toxicity. Oxidation and glutathione complexation of arsenite have not been characterized. Since each organ has some capacity to “metabolize” As, absorption from pulmonary exposure would be accompanied by a “first pass effect” from the lung.