Lilia Batres

Overview of human health and chemical mixtures: problems facing developing countries.

In developing countries, chemical mixtures within the vicinity of small-scale enterprises, smelters, mines, agricultural areas, toxic waste disposal sites, etc., often present a health hazard to the populations within those vicinities. Therefore, in these countries, there is a need to study the toxicological effects of mixtures of metals, pesticides, and organic compounds. However, the study of mixtures containing substances such as DDT (dichlorodiphenyltrichloroethane, an insecticide banned in developed nations), and mixtures containing contaminants such as fluoride (of concern only in developing countries) merit special attention. Although the studies may have to take into account simultaneous exposures to metals and organic compounds, there is also a need to consider the interaction between chemicals and other specific factors such as nutritional conditions, alcoholism, smoking, infectious diseases, and ethnicity.

Arsenic-cadmium interaction in rats: toxic effects in the heart and tissue metal shifts

Previously, we had shown that arsenic interacts with cadmium in rats; our results showed that the toxicity of a mixture of arsenic + cadmium cannot be predicted by the toxic mechanisms of the individual components. In this paper, we present further evidence about the interaction of arsenic and cadmium in rats. The results were: arsenic modified the 24 h-LD50 value of cadmium more clearly than cadmium did with the one of arsenic; based on the LD50 values, the mixtures we studied were more toxic than either metal alone. With single doses (As 10 mg/kg, Cd 2.6 mg/kg, and As 10 mg/kg + Cd 2.6 mg/kg) the mixture As + Cd was more toxic than each metal. At these doses, cadmium significantly induces the levels of glutathione, metallothionein, and lipid peroxidation in heart tissue, as compared to a saline group of rats. Arsenic incremented glutathione and lipid peroxidation at higher values than those obtained with cadmium. The mixture of As + Cd behaved as arsenic in the induction of lipid peroxidation and glutathione and like cadmium in metallothionein induction. Finally, rats treated with As + Cd had less Cd in liver than animals treated only with cadmium, and more As in heart tissue than rats treated only with arsenic. Our results give further evidence about the arsenic-cadmium interaction in rats, demonstrate the utility of employing different biomarkers in the study of chemical mixtures and indicate that heart tissue is affected not only by the mixture of As + Cd, but also by either metal alone.

Environmental Health Assessment of Deltamethrin in a Malarious Area of Mexico: Environmental Persistence, Toxicokinetics, and Genotoxicity in Exposed Children

We reported previously that children are exposed to deltamethrin in malarious areas. In the present work we explored the levels of this insecticide in soil samples and also obtained relevant toxico-kinetic data of deltamethrin in exposed children. Results show that, after spraying, indoor levels of deltamethrin in soil samples were higher than outdoor levels. The mean half-life estimated with these data was 15.5 days for outdoor samples and 15.4 days for indoor samples. Children’s exposure to deltamethrin was assessed using as biomarkers the urinary concentrations of the metabolites 3-phenoxybenzoic acid (3-PBA) and cis-3-(2,2-dibromovinyl)-2,2-dimethylcyclopropane-1-carboxylic acid (Br2CA). The mean level of both biomarkers reached a peak within the first 24 hr postexposure; 6 months after the initial exposure, urinary levels of 3-PBA and Br2CA were found at levels observed before exposure. Approximately 91% of the total 3-PBA or Br2CA was excreted during the first 3 days after exposure. Therefore, we estimated a half-life for this period, the values for 3-PBA and Br2CA being almost identical (13.5 vs. 14.5 hr). Finally, considering reports about the genotoxicity of deltamethrin, we assessed DNA damage in children before and 24 hr after indoor spraying of deltamethrin; we found no differences in the comet assay end points. In conclusion, we observed exposure to deltamethrin in children, but we did not find any relationship between soil concentrations of deltamethrin and urinary levels of the metabolites. At least for genotoxicity, the exposed children appeared not to be at risk.

Toxicological assessment of azarcon, a lead salt used as a folk remedy in Mexico. I: Oral toxicity in rats

Azarcon, a lead tetroxide salt, is used among Mexican and Mexican-American populations for the treatment of digestive illness. Chemical analysis of the azarcon sample used in this study showed it to be 96% lead, 1% calcium, 1% other minor metals, and 2% unidentified material. Taking into account the fact that Pb absorption was estimated at 2% following a single oral administration of 100 mg/kg (Aungst et al., 1981), it is possible to propose a chemical interaction between the components of azarcon, and as a result, the toxicity of Pb tetroxide would be different when given as azarcon than when given as a pure compound. The present work studied this possibility, with the following results. When the treatments of equal doses of pure Pb tetroxide and azarcon were compared (158 mg/kg/day p.o. for 96 h), five of nine tissues studied had similar Pb concentrations. However, with the pure compound the Pb levels were higher in bone and intestines; while with azarcon the Pb levels were higher in heart and brain. The pure Pb tetroxide treatment affects lipid peroxidation only in liver, but a low induction of peroxidation was found also in kidney and heart in rats which received the azarcon treatment. Liver and kidney damage were evident in rats treated with a high dose of azarcon (1.1 g/kg/day p.o. for 96 h), while the effects with the pure compound were similar in type but lower in magnitude. Pb tetroxide as a pure compound inhibits ALA-D by 26% while an inhibition of 42% was found with azarcon.(ABSTRACT TRUNCATED AT 250 WORDS)