Concentrations of urinary arsenic species in relation to rice and seafood consumption among children living in Spain
Inorganic arsenic (i-As) has been related to wide-ranging health effects in children, leading to lifelong concerns. Proportionally, dietary i-As exposure dominates in regions with low arsenic drinking water. This study aims to investigate the relation between rice and seafood consumption and urinary...
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| Published in | Environmental research Vol. 159; pp. 69 - 75 |
|---|---|
| Main Authors | , , , , , , , , , , , , , , |
| Format | Journal Article |
| Language | English |
| Published |
Netherlands
Elsevier Inc
01.11.2017
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| Subjects | |
| Online Access | Get full text |
| ISSN | 0013-9351 1096-0953 1096-0953 |
| DOI | 10.1016/j.envres.2017.07.046 |
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| Abstract | Inorganic arsenic (i-As) has been related to wide-ranging health effects in children, leading to lifelong concerns. Proportionally, dietary i-As exposure dominates in regions with low arsenic drinking water. This study aims to investigate the relation between rice and seafood consumption and urinary arsenic species during childhood and to assess the proportion of urinary i-As metabolites. Urinary arsenic species concentration in 400 4-year-old children living in four geographical areas of Spain, in addition to repeated measures from 100 children at 7 years of age are included in this study. Rice and seafood products intake was collected from children's parents using a validated food frequency questionnaire (FFQ). At 4 years of age, children's urine i-As and monomethylarsonic acid (MMA) concentrations increased with rice product consumption (p-value = 0.010 and 0.018, respectively), and urinary arsenobetaine (AsB) with seafood consumption (p = 0.002). Four-year-old children had a higher consumption of both rice and seafood per body weight and a higher urinary %MMA (p-value = 0.001) and lower % dimethylarsinic acid (DMA) (p-value = 0.017). This study suggests increased dietary i-As exposure related to rice product consumption among children living in Spain, and the younger ones may be especially vulnerable to the health impacts of this exposure also considering that they might have a lower i-As methylation capacity than older children. In contrast, seafood consumption did not appear to influence the presence of potentially toxic arsenic species in this population of children.
•Rice and seafood consumption per body weight was higher for younger children.•Urinary inorganic arsenic metabolites increased with children's rice consumption.•Children's seafood intake was associated with an increase of urinary arsenobetaine.•Older children suggested higher inorganic arsenic methylation capacity. |
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| AbstractList | Inorganic arsenic (i-As) has been related to wide-ranging health effects in children, leading to lifelong concerns. Proportionally, dietary i-As exposure dominates in regions with low arsenic drinking water. This study aims to investigate the relation between rice and seafood consumption and urinary arsenic species during childhood and to assess the proportion of urinary i-As metabolites. Urinary arsenic species concentration in 400 4-year-old children living in four geographical areas of Spain, in addition to repeated measures from 100 children at 7 years of age are included in this study. Rice and seafood products intake was collected from children's parents using a validated food frequency questionnaire (FFQ). At 4 years of age, children's urine i-As and monomethylarsonic acid (MMA) concentrations increased with rice product consumption (p-value = 0.010 and 0.018, respectively), and urinary arsenobetaine (AsB) with seafood consumption (p = 0.002). Four-year-old children had a higher consumption of both rice and seafood per body weight and a higher urinary %MMA (p-value = 0.001) and lower % dimethylarsinic acid (DMA) (p-value = 0.017). This study suggests increased dietary i-As exposure related to rice product consumption among children living in Spain, and the younger ones may be especially vulnerable to the health impacts of this exposure also considering that they might have a lower i-As methylation capacity than older children. In contrast, seafood consumption did not appear to influence the presence of potentially toxic arsenic species in this population of children.Inorganic arsenic (i-As) has been related to wide-ranging health effects in children, leading to lifelong concerns. Proportionally, dietary i-As exposure dominates in regions with low arsenic drinking water. This study aims to investigate the relation between rice and seafood consumption and urinary arsenic species during childhood and to assess the proportion of urinary i-As metabolites. Urinary arsenic species concentration in 400 4-year-old children living in four geographical areas of Spain, in addition to repeated measures from 100 children at 7 years of age are included in this study. Rice and seafood products intake was collected from children's parents using a validated food frequency questionnaire (FFQ). At 4 years of age, children's urine i-As and monomethylarsonic acid (MMA) concentrations increased with rice product consumption (p-value = 0.010 and 0.018, respectively), and urinary arsenobetaine (AsB) with seafood consumption (p = 0.002). Four-year-old children had a higher consumption of both rice and seafood per body weight and a higher urinary %MMA (p-value = 0.001) and lower % dimethylarsinic acid (DMA) (p-value = 0.017). This study suggests increased dietary i-As exposure related to rice product consumption among children living in Spain, and the younger ones may be especially vulnerable to the health impacts of this exposure also considering that they might have a lower i-As methylation capacity than older children. In contrast, seafood consumption did not appear to influence the presence of potentially toxic arsenic species in this population of children. Inorganic arsenic (i-As) has been related to wide-ranging health effects in children, leading to lifelong concerns. Proportionally, dietary i-As exposure dominates in regions with low arsenic drinking water. This study aims to investigate the relation between rice and seafood consumption and urinary arsenic species during childhood and to assess the proportion of urinary i-As metabolites. Urinary arsenic species concentration in 400 4-year-old children living in four geographical areas of Spain, in addition to repeated measures from 100 children at 7 years of age are included in this study. Rice and seafood products intake was collected from children's parents using a validated food frequency questionnaire (FFQ). At 4 years of age, children's urine i-As and monomethylarsonic acid (MMA) concentrations increased with rice product consumption (p-value = 0.010 and 0.018, respectively), and urinary arsenobetaine (AsB) with seafood consumption (p = 0.002). Four-year-old children had a higher consumption of both rice and seafood per body weight and a higher urinary %MMA (p-value = 0.001) and lower % dimethylarsinic acid (DMA) (p-value = 0.017). This study suggests increased dietary i-As exposure related to rice product consumption among children living in Spain, and the younger ones may be especially vulnerable to the health impacts of this exposure also considering that they might have a lower i-As methylation capacity than older children. In contrast, seafood consumption did not appear to influence the presence of potentially toxic arsenic species in this population of children. Inorganic arsenic (i-As) has been related to wide-ranging health effects in children, leading to lifelong concerns. Proportionally, dietary i-As exposure dominates in regions with low arsenic drinking water. This study aims to investigate the relation between rice and seafood consumption and urinary arsenic species during childhood and to assess the proportion of urinary i-As metabolites. Urinary arsenic species concentration in 400 4-year-old children living in four geographical areas of Spain, in addition to repeated measures from 100 children at 7 years of age are included in this study. Rice and seafood products intake was collected from children's parents using a validated food frequency questionnaire (FFQ). At 4 years of age, children's urine i-As and monomethylarsonic acid (MMA) concentrations increased with rice product consumption (p-value = 0.010 and 0.018, respectively), and urinary arsenobetaine (AsB) with seafood consumption (p = 0.002). Four-year-old children had a higher consumption of both rice and seafood per body weight and a higher urinary %MMA (p-value = 0.001) and lower % dimethylarsinic acid (DMA) (p-value = 0.017). This study suggests increased dietary i-As exposure related to rice product consumption among children living in Spain, and the younger ones may be especially vulnerable to the health impacts of this exposure also considering that they might have a lower i-As methylation capacity than older children. In contrast, seafood consumption did not appear to influence the presence of potentially toxic arsenic species in this population of children. •Rice and seafood consumption per body weight was higher for younger children.•Urinary inorganic arsenic metabolites increased with children's rice consumption.•Children's seafood intake was associated with an increase of urinary arsenobetaine.•Older children suggested higher inorganic arsenic methylation capacity. |
| Author | Sunyer, Jordi García de la Hera, Manoli Amorós, Rubén Casas, Maribel Bilbao, José R. Tardón, Adonina Amiano, Pilar Navarrete-Muñoz, Eva M. Riaño-Galán, Isolina Llop, Sabrina Meharg, Andrew A. Signes-Pastor, Antonio J. Carey, Manus Karagas, Margaret R. Vioque, Jesus |
| AuthorAffiliation | b University Miguel Hernández, Faculty of Medicine and Institute for Health and Biomedical Research (ISABIAL-FISABIO Foundation), Ctra. Valencia s/n, 03550 Sant Joan d́ Alacant, Spain a Institute for Global Food Security, Queen’s University Belfast, David Keir Building, Malone Road, Belfast BT9 5BN, Northern Ireland, UK m Department of Genetics, Physical Anthropology and Animal Physiology, University of the Basque Country (UPV-EHU), BioCruces Health Research Institute, Leioa, Spain d Department of Epidemiology, Geisel School of Medicine, Dartmouth College, 1 Medical Center Dr, 7927 Rubin Bldg, Lebanon NH03766, USA i Epidemiology and Environmental Health Joint Research Unit, Universitat Jaume I-Universitat de València, València, Spain g Pediatric Unit, Hospital Universitario Central de Asturias, Oviedo, Spain k Carlos III Institute of Health, Avenida Monforte de Lemos 5, 28029 Madrid, Spain f Universitat Pompeu Fabra, Barcelona, Spain h IUOPA-Universidad de Oviedo, Spain l Public Health Departme |
| AuthorAffiliation_xml | – name: j Foundation for the Promotion of Health and Biomedical Research in the Valencian Region, FISABIO, Valencia, Spain – name: l Public Health Department of Gipuzkoa, Government of the Basque Country, Avenida Navarra, 4, 20013, San Sebastian, Spain; Biodonostia Research Institute, Paseo Dr Beguiristain s/n, 20014, San Sebastian, Spain – name: g Pediatric Unit, Hospital Universitario Central de Asturias, Oviedo, Spain – name: m Department of Genetics, Physical Anthropology and Animal Physiology, University of the Basque Country (UPV-EHU), BioCruces Health Research Institute, Leioa, Spain – name: f Universitat Pompeu Fabra, Barcelona, Spain – name: k Carlos III Institute of Health, Avenida Monforte de Lemos 5, 28029 Madrid, Spain – name: d Department of Epidemiology, Geisel School of Medicine, Dartmouth College, 1 Medical Center Dr, 7927 Rubin Bldg, Lebanon NH03766, USA – name: a Institute for Global Food Security, Queen’s University Belfast, David Keir Building, Malone Road, Belfast BT9 5BN, Northern Ireland, UK – name: i Epidemiology and Environmental Health Joint Research Unit, Universitat Jaume I-Universitat de València, València, Spain – name: h IUOPA-Universidad de Oviedo, Spain – name: e ISGlobal, Centre for Research in Environmental Epidemiology (CREAL), Barcelona, Spain – name: b University Miguel Hernández, Faculty of Medicine and Institute for Health and Biomedical Research (ISABIAL-FISABIO Foundation), Ctra. Valencia s/n, 03550 Sant Joan d́ Alacant, Spain – name: c Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Spain |
| Author_xml | – sequence: 1 givenname: Antonio J. surname: Signes-Pastor fullname: Signes-Pastor, Antonio J. email: antonio.j.signes-pastor@dartmouth.edu organization: Institute for Global Food Security, Queen's University Belfast, David Keir Building, Malone Road, Belfast BT9 5BN, Northern Ireland, UK – sequence: 2 givenname: Jesus surname: Vioque fullname: Vioque, Jesus organization: University Miguel Hernández, Faculty of Medicine and Institute for Health and Biomedical Research (ISABIAL-FISABIO Foundation), Ctra. Valencia s/n, 03550 Sant Joan d ́Alacant, Spain – sequence: 3 givenname: Eva M. surname: Navarrete-Muñoz fullname: Navarrete-Muñoz, Eva M. organization: University Miguel Hernández, Faculty of Medicine and Institute for Health and Biomedical Research (ISABIAL-FISABIO Foundation), Ctra. Valencia s/n, 03550 Sant Joan d ́Alacant, Spain – sequence: 4 givenname: Manus surname: Carey fullname: Carey, Manus organization: Institute for Global Food Security, Queen's University Belfast, David Keir Building, Malone Road, Belfast BT9 5BN, Northern Ireland, UK – sequence: 5 givenname: Manoli surname: García de la Hera fullname: García de la Hera, Manoli organization: University Miguel Hernández, Faculty of Medicine and Institute for Health and Biomedical Research (ISABIAL-FISABIO Foundation), Ctra. Valencia s/n, 03550 Sant Joan d ́Alacant, Spain – sequence: 6 givenname: Jordi surname: Sunyer fullname: Sunyer, Jordi organization: Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Spain – sequence: 7 givenname: Maribel surname: Casas fullname: Casas, Maribel organization: Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Spain – sequence: 8 givenname: Isolina surname: Riaño-Galán fullname: Riaño-Galán, Isolina organization: Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Spain – sequence: 9 givenname: Adonina surname: Tardón fullname: Tardón, Adonina organization: Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Spain – sequence: 10 givenname: Sabrina surname: Llop fullname: Llop, Sabrina organization: Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Spain – sequence: 11 givenname: Rubén surname: Amorós fullname: Amorós, Rubén organization: Foundation for the Promotion of Health and Biomedical Research in the Valencian Region, FISABIO, Valencia, Spain – sequence: 12 givenname: Pilar surname: Amiano fullname: Amiano, Pilar organization: Spanish Consortium for Research on Epidemiology and Public Health (CIBERESP), Spain – sequence: 13 givenname: José R. surname: Bilbao fullname: Bilbao, José R. organization: Department of Genetics, Physical Anthropology and Animal Physiology, University of the Basque Country (UPV-EHU), BioCruces Health Research Institute, Leioa, Spain – sequence: 14 givenname: Margaret R. surname: Karagas fullname: Karagas, Margaret R. organization: Department of Epidemiology, Geisel School of Medicine, Dartmouth College, 1 Medical Center Dr, 7927 Rubin Bldg, Lebanon NH03766, USA – sequence: 15 givenname: Andrew A. surname: Meharg fullname: Meharg, Andrew A. organization: Institute for Global Food Security, Queen's University Belfast, David Keir Building, Malone Road, Belfast BT9 5BN, Northern Ireland, UK |
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| Keywords | Arsenic speciation Young children Urinary biomarker Childhood Seafood Food frequency questionnaire Inorganic arsenic Rice |
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| SubjectTerms | arsenic Arsenic - urine Arsenic speciation body weight cacodylic acid Child Child, Preschool Childhood children Diet drinking water Environmental Exposure Environmental Monitoring Environmental Pollutants - analysis Female Food Contamination - analysis Food frequency questionnaire food frequency questionnaires Humans Inorganic arsenic Male metabolites methylation Oryza - chemistry parents Rice Seafood Seafood - analysis seafood consumption seafoods Spain Surveys and Questionnaires toxicity Urinary biomarker urine Young children |
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| Title | Concentrations of urinary arsenic species in relation to rice and seafood consumption among children living in Spain |
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