RESUMEN
This study concerns the metabolism of inorganic arsenic (As) in children in three villages in northern Argentina: San Antonio de los Cobres and Taco Pozo, each with about 200 microg As/l in the drinking water, and Rosario de Lerma, with 0.65 microg As/l. Findings show that the concentrations of As in the blood and urine of the children in the two As-rich villages were on average 9 and 380 microg/l, respectively, the highest ever recorded for children. The concentrations were about 10 and 30 times higher for blood and urine, respectively, than in Rosario de Lerma. Total As in urine was only slightly higher than the sum of metabolites of inorganic As (U-Asmet), i.e., inorganic As, methylarsonic acid (MMA), and dimethylarsinic acid (DMA); this shows that inorganic As was the main form of As ingested. In contrast to previous studies on urinary metabolites of inorganic As in various population groups, the children and women in the present study excreted very little MMA. Thus, there seems to be a polymorphism for the enzymes (methyltransferases) involved in the methylation of As. Interestingly, the children had a significantly higher percentage of inorganic As in urine than the women, about 50% versus 32%. Also, the percentage of inorganic As in the children is considerably higher than in previous studies on children (about 13% in the two studies available) and adults (about 15-25%) in other population groups. This may indicate that children are more sensitive to As-induced toxicity than adults, as the methylated metabolites bind less to tissue constituents than inorganic As. In the children, the percentage inorganic arsenic in urine decreased, and the percentage of DMA increased with increasing U-Asmet, indicating an induction of As methylation with increasing exposure.
Asunto(s)
Arsénico/metabolismo , Protección a la Infancia , Exposición a Riesgos Ambientales , Contaminantes Químicos del Agua/metabolismo , Abastecimiento de Agua , Adulto , Argentina , Arsénico/efectos adversos , Arsénico/sangre , Niño , Femenino , Humanos , Masculino , Contaminantes Químicos del Agua/efectos adversosRESUMEN
OBJECTIVE: To investigate the excretion of arsenic in breast milk of lactating native Andean women living in a village in northwestern Argentina with high concentrations of arsenic in the drinking water (about 200 micrograms/l) and to assess the exposure of children to arsenic during the very first period of life. METHODS: The study included ten lactating women and two nursing babies. Hydride-generation atomic absorption spectrometry (HG-AAS) was used to determine the concentration of arsenic in samples of human milk, drinking water, blood, and urine. RESULTS: The concentrations of arsenic detected in maternal blood (total arsenic) and urine (metabolites of inorganic arsenic) were high, averaging 10 and 320 micrograms/l, respectively. In subjects without known exposure to arsenic the average concentrations found in blood and urine are 1-2 and about 10 micrograms/l, respectively. The metabolites of inorganic arsenic constituted more than 80% of the total arsenic in the urine, which shows that inorganic arsenic was the main form of arsenic ingested. The average concentration of arsenic detected in human milk was 2.3 micrograms/kg fresh weight (range 0.83-7.6 micrograms/kg). Although data on background levels of arsenic in human breast milk are scarce, the present concentrations seem to be slightly elevated. However, considering the high levels of arsenic exposure in the mothers, the total arsenic concentrations measured in human milk were low. In concordance with the low concentrations of arsenic found in the milk, the concentrations of arsenic metabolites measured in the urine of two of the nursing babies were low: 17 and 47 micrograms/l, respectively. CONCLUSIONS: The low concentrations of arsenic detected in the breast milk and urine of the two nursing babies in relation to the high level of maternal exposure to arsenic indicate that inorganic arsenic is not excreted in breast milk to any significant extent. This is a very important reason for long breast-feeding periods.
Asunto(s)
Arsénico/análisis , Exposición a Riesgos Ambientales/análisis , Leche Humana/química , Abastecimiento de Agua/análisis , Adolescente , Adulto , Argentina , Arsénico/sangre , Arsénico/orina , Ingestión de Líquidos , Femenino , Humanos , Recién Nacido , Embarazo , Población Rural , MuestreoRESUMEN
We investigated blood lead (B-Pb) and mercury (B-Hg) levels and auditory sensory-neural function in 62 Andean school children living in a Pb-contaminated area of Ecuador and 14 children in a neighboring gold mining area with no known Pb exposure. The median B-Pb level for 62 children in the Pb-exposed group was 52.6 micrograms/dl (range 9.9-110.0 micrograms/dl) compared with 6.4 micrograms/dl (range 3.9-12.0 micrograms/dl) for the children in the non-Pb exposed group; the differences were statistically significant (p < 0.001). Auditory thresholds for the Pb-exposed group were normal at the pure tone frequencies of 0.25-8 kHz over the entire range of B-Pb levels, Auditory brain stem response tests in seven children with high B-Pb levels showed normal absolute peak and interpeak latencies. The median B-Hg levels were 0.16 micrograms/dl (range 0.04-0.58 micrograms/dl) for children in the Pb-exposed group and 0.22 micrograms/dl (range 0.1-0.44 micrograms/dl) for children in the non-Pb exposed gold mining area, and showed no significant relationship to auditory function.
Asunto(s)
Exposición a Riesgos Ambientales/efectos adversos , Pérdida Auditiva Sensorineural/inducido químicamente , Intoxicación por Plomo/complicaciones , Adolescente , Audiometría de Tonos Puros , Umbral Auditivo , Estudios de Casos y Controles , Cerámica , Niño , Preescolar , Ecuador , Potenciales Evocados Auditivos del Tronco Encefálico , Femenino , Pérdida Auditiva Sensorineural/diagnóstico , Humanos , Intoxicación por Plomo/sangre , MasculinoRESUMEN
Indium arsenide and gallium arsenide are important new materials in the semiconductor industry due to their superior electronic properties in comparison with the older silicon-based materials. Animal experiments have shown that exposure to these compounds induces marked alterations in gene expression and immune response. Toxicity to the immune system has frequently been related to T and B cell apoptosis. In the present study we show that the semiconductor elements indium (In) and arsenic (As) are able to induce apoptosis in rat thymocytes in vitro. The results show that exposure to InCl3 (1, 10, or 100 microM) or Na AsO2 (0.01, 0.1, or 1 microM) induced DNA laddering after 6 h of incubation without compromising cell viability. These results were corroborated by flow cytometry analysis of propidium iodide-loaded cells, showing a typical high hypodiploid DNA peak in apoptotic thymocytes. Higher doses of In (1 mM) or As (10-100 microM) induced cell death by necrosis. These data indicate that In and As can induce apoptosis and necrosis in T lymphocytes in a dose-dependent manner, which may be of relevance for their immunotoxicity.
Asunto(s)
Apoptosis/efectos de los fármacos , Intoxicación por Arsénico , Indio/toxicidad , Timo/efectos de los fármacos , Animales , Muerte Celular/efectos de los fármacos , Supervivencia Celular/efectos de los fármacos , Células Cultivadas , Fragmentación del ADN/efectos de los fármacos , Relación Dosis-Respuesta a Droga , Electroforesis en Gel de Agar , Citometría de Flujo , Masculino , Necrosis , Propidio/química , Ratas , Ratas Sprague-Dawley , Semiconductores , Linfocitos T/citología , Linfocitos T/efectos de los fármacos , Timo/citologíaRESUMEN
We have determined the concentrations of lead (Pb), cadmium (Cd), and mercury (Hg) in the blood of children living in two Andean villages in Ecuador with many family-owned cottage-type industries using Pb from discarded car batteries and occasionally, utility batteries containing Cd and Hg for the production of glazed tiles. The battery metals are ground together with water to a suspension, which is applied manually onto the tiles and then fused at about 1,200 degrees C in sawdust-fired kilns. Children aged 4-15 years were recruited from the schools with the assistance of the school-teachers. Children from homes with and without tile-glazing activities were to be included. Blood metal concentrations were determined by inductively coupled plasma mass spectrometry (ICP-MS). The children had extremely high blood lead concentrations (B-Pb), which ranged between 100 and 1,100 micrograms/l (median 510 micrograms/l, n = 82). Children from families engaged in tile-glazing production had significantly higher B-Pb (median 600 micrograms/l) than those living in homes with no such activity (median 210 micrograms/l), although the B-Pb of the latter were nonetheless clearly elevated. B-Cd and B-Hg were low (medians 0.25 microgram Cd/l and 1.6 micrograms Hg/l, respectively), indicating that the exposure from utility batteries containing Cd and Hg was low. The blood hemoglobin concentrations decreased significantly with rising B-Pb, indicating an effect on the heme synthesis. This was supported by a marked increase in the blood concentration of protoporphyrins with increasing B-Pb. It can be concluded that children from families with cottage industries producing glazed tiles are at risk for severe health effects due to high lead exposure.
Asunto(s)
Países en Desarrollo , Monitoreo del Ambiente , Contaminantes Ambientales/efectos adversos , Intoxicación por Plomo/epidemiología , Plomo/efectos adversos , Adolescente , Cadmio/farmacocinética , Niño , Preescolar , Ecuador , Empleo , Contaminantes Ambientales/farmacocinética , Monitoreo Epidemiológico , Femenino , Humanos , Plomo/farmacocinética , Intoxicación por Plomo/sangre , Masculino , Mercurio/farmacocinéticaRESUMEN
For conducting an adequate human cancer risk assessment of inorganic arsenic (As) in the low-dose region, it is important to establish its mode of action. In this context, the nature of genotoxic effects induced by this agent is of considerable interest. However, the results from such investigations in human have been conflicting. In an attempt to resolve this issue, the clastogenic and aneugenic potential of As was investigated in women and children from native population exposed to high levels (around 0.2 mg/l) of natural As via drinking water in San Antonio de los Corbes in the Andean region of Salta, Northwestern Argentina. The water did not contain elevated levels of heavy metals, such as lead or cadmium, nor was the investigated population exposed to significant industrial pollution or to pesticides. An ethnically similar control group from Rosario de Lerma, Salta, where only extremely low concentration of arsenic in drinking water could be detected, was used as a control. To evaluate the genotoxic effects in peripheral blood lymphocytes, micronuclei (MN) in binucleated cells, sister-chromatid exchanges (SCEs) and the fluorescence in situ hybridization technique (FISH) in combination with chromosome specific DNA libraries were employed. The data obtained clearly indicate a highly significant increase in the frequency of MN and of trisomy in lymphocytes from exposed children and women in comparison with controls, but no notable effects were found on the frequencies of SCEs, specific translocations, or on cell cycle progression. As supported by FISH analysis, at least a proportion of MN appears to originate from whole chromosome loss. An additional finding was the unusually low background levels of MN in unexposed individuals from this ethnic group as compared to other populations, e.g., Caucasians.
Asunto(s)
Arsénico/toxicidad , Aberraciones Cromosómicas , Mutágenos/toxicidad , Contaminantes Químicos del Agua/toxicidad , Abastecimiento de Agua , Adolescente , Adulto , Argentina , Niño , Femenino , Humanos , Hibridación Fluorescente in Situ , Pruebas de Micronúcleos , Persona de Mediana Edad , Intercambio de Cromátides Hermanas , TrisomíaRESUMEN
The metabolism of inorganic arsenic (As) in native women in four Andean villages in north-western Argentina with elevated levels of As in the drinking water (2.5, 14, 31, and 200 micrograms/1, respectively) has been investigated. Collected foods contained 9-427 micrograms As/kg wet weight, with the highest concentrations in soup. Total As concentrations in blood were markedly elevated (median 7.6 micrograms/1) only in the village with the highest concentration in the drinking water. Group median concentrations of metabolites of inorganic As (inorganic As, methylarsonic acid (MMA) and dimethylarsinic acid (DMA)) in the urine varied between 14 and 256 micrograms/1. Urinary concentrations of total As were only slightly higher (18-258 micrograms/1), indicating that inorganic As was the main form of As ingested. In contrast to all other populations studied so far, arsenic was excreted in the urine mainly as inorganic As and DMA. There was very little MMA in the urine (overall median 2.2%, range 0.0-11%), which should be compared to 10-20% of the urinary arsenic in all other populations studied. This may indicate the existence of genetic polymorphism in the control of the methyltransferase activity involved in the methylation of As. Furthermore, the percentage of DMA in the urine was significantly higher in the village with 200 micrograms As/1 in the water, indicating an induction of the formation of DMA. Such an effect has not been observed in other studies on human subjects with elevated exposure to arsenic.