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Arsenic exposure of child populations in Northern Argentina.
Calatayud, Marta; Farias, Silvia Sara; de Paredes, Gladys Soria; Olivera, Mónica; Carreras, Natalia Ávila; Giménez, Maria Cecilia; Devesa, Vicenta; Vélez, Dinoraz.
Afiliação
  • Calatayud M; Instituto de Agroquímica y Tecnología de Alimentos (CSIC), C/ Agustín Escardino 7, 46980 Paterna, Valencia, Spain.
  • Farias SS; Investigador Consulto Gerencia Química, Gerencia de Área de Seguridad y Ambiente, Comisión Nacional de Energía Atómica, Buenos Aires, Argentina.
  • de Paredes GS; Programa Provincial H.A.C.R.E. Ministerio de Salud, Santiago del Estero, Argentina.
  • Olivera M; Cátedra de Toxicología y Química Legal, Facultad de Farmacia y Bioquímica, Universidad de Buenos Aires, Argentina.
  • Carreras NÁ; Universidad Nacional del Chaco Austral, Provincia Roque Sáenz Peña, Chaco, Argentina.
  • Giménez MC; Facultad de Ciencias Agrarias, Universidad Nacional de Jujuy, Jujuy, Argentina.
  • Devesa V; Instituto de Agroquímica y Tecnología de Alimentos (CSIC), C/ Agustín Escardino 7, 46980 Paterna, Valencia, Spain.
  • Vélez D; Instituto de Agroquímica y Tecnología de Alimentos (CSIC), C/ Agustín Escardino 7, 46980 Paterna, Valencia, Spain. Electronic address: deni@iata.csic.es.
Sci Total Environ ; 669: 1-6, 2019 Jun 15.
Article em En | MEDLINE | ID: mdl-30877956
ABSTRACT
Chronic exposure to inorganic arsenic (As) is associated with numerous adverse effects. Argentina is one of the countries affected by arsenicism; however, there are few studies that evaluate inorganic As exposure and its effects on child population. The aim of this study is to evaluate exposure to As through water and food in child populations living in the provinces of Santiago del Estero and Chaco (n = 101), and to determine the impact of this exposure analysing biomarkers of exposure (urine and hair As contents) and effect [8-oxo-7,8-dihydro-2'-deoxyguanosine (8-OHdG)]. The populations selected live in three areas with different levels of As in the drinking water (Santa Teresa de Carballo, 0.925 mg/L; Taco Pozo, 0.210 mg/L; Jumi Pozo, 0.016 mg/L). The As intakes through water and food are especially high in the areas with the greatest As exposure (Santa Teresa de Carballo, 1575 ±â€¯8 µg/day; Taco Pozo, 386 ±â€¯8 µg/day; Jumi Pozo, 39 ±â€¯1 µg/day). The total As contents in most of the samples of hair (0.11-13.11 mg/kg) and urine (31-4258 µg/g creatinine) are higher than the reference values (hair 1 mg/kg; urine 50 µg/g creatinine). The increase in the level of As exposure alters the profile of metabolites in urine, with a decrease of dimethylarsinic acid (10%) and an increase in the percentages of monomethylarsonic acid (4%) and inorganic As (6%). The results also show high values of 8-OHdG (3.7-37.8 µg/g creatinine), a oxidative DNA damage marker, in the two areas with greater As exposure.
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Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Assunto principal: Arsênio / Arsenicais / Desoxiguanosina / Exposição Ambiental / Poluentes Ambientais / Cabelo Limite: Child, preschool / Female / Humans / Male País/Região como assunto: America do sul / Argentina Idioma: En Revista: Sci Total Environ Ano de publicação: 2019 Tipo de documento: Article País de afiliação: Espanha

Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Assunto principal: Arsênio / Arsenicais / Desoxiguanosina / Exposição Ambiental / Poluentes Ambientais / Cabelo Limite: Child, preschool / Female / Humans / Male País/Região como assunto: America do sul / Argentina Idioma: En Revista: Sci Total Environ Ano de publicação: 2019 Tipo de documento: Article País de afiliação: Espanha