Literature DB >> 20377243

Biomonitoring of arsenic in urine and saliva of children playing on playgrounds constructed from chromated copper arsenate-treated wood.

Kristi Lew1, Jason P Acker, Stephan Gabos, X Chris Le.   

Abstract

Children may be exposed to arsenic during contact with structures treated with chromated copper arsenate (CCA). A high frequency of hand-to-mouth activity may increase their risk of ingesting arsenic. Previous work showed that arsenic concentrations in the hand-wash samples of children playing on CCA playgrounds were four times higher than those playing on non-CCA playgrounds. It is not clear whether playing on CCA playgrounds results in elevated overall exposure to arsenic. The objective of this study was to perform arsenic biomonitoring in children to determine whether playing on CCA-treated playgrounds substantially contributes to their overall exposure to arsenic. One hundred and twenty five saliva samples from 61 children and 101 urine samples from 45 children were collected after children played on 8 CCA and 8 non-CCA playgrounds. Arsenic speciation analysis was conducted using high performance liquid chromatography combined with inductively coupled plasma mass spectrometry. The arsenic species detected in the urine and saliva samples from children playing on CCA and non-CCA playgrounds were similar. Dimethylarsinic acid and arsenobetaine were the main arsenic species found in urine samples. The sum of inorganic trivalent and pentavalent arsenic, monomethylarsonic acid, and dimethylarsinic acid in urine was 15 +/- 28 microg/L in the CCA group and 12 +/- 23 microg/L in the non-CCA group (p = 0.60). The sum of these species in saliva was 1.1 +/- 2.1 microg/L in the CCA group and 1.4 +/- 1.1 microg/L in the non-CCA group (p = 0.32). These results show that there is no significant difference in the concentration or speciation of arsenic between the samples from children playing on CCA and non-CCA playgrounds. Contact with CCA playgrounds is not likely to significantly contribute to the overall arsenic exposure in children; other sources such as dietary arsenic may be a main contributor to their overall exposure.

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Year:  2010        PMID: 20377243     DOI: 10.1021/es100128n

Source DB:  PubMed          Journal:  Environ Sci Technol        ISSN: 0013-936X            Impact factor:   9.028


  5 in total

Review 1.  Saliva as a matrix for human biomonitoring in occupational and environmental medicine.

Authors:  Bernhard Michalke; Bernd Rossbach; Thomas Göen; Anja Schäferhenrich; Gerhard Scherer
Journal:  Int Arch Occup Environ Health       Date:  2014-03-12       Impact factor: 3.015

2.  Total arsenic and speciation analysis of saliva and urine samples from individuals living in a chronic arsenicosis area in China.

Authors:  Dapeng Wang; Yasuyo Shimoda; Sanxiang Wang; Zhenghui Wang; Jian Liu; Xing Liu; Huanyu Jin; Fenfang Gao; Jian Tong; Kenzo Yamanaka; Jie Zhang; Yan An
Journal:  Environ Health Prev Med       Date:  2017-05-11       Impact factor: 3.674

Review 3.  Environmental and Health Hazards of Chromated Copper Arsenate-Treated Wood: A Review.

Authors:  Simone Morais; Henrique M A C Fonseca; Sónia M R Oliveira; Helena Oliveira; Vivek Kumar Gupta; Bechan Sharma; Maria de Lourdes Pereira
Journal:  Int J Environ Res Public Health       Date:  2021-05-21       Impact factor: 3.390

4.  Arsenic speciation in saliva of acute promyelocytic leukemia patients undergoing arsenic trioxide treatment.

Authors:  Baowei Chen; Fenglin Cao; Chungang Yuan; Xiufen Lu; Shengwen Shen; Jin Zhou; X Chris Le
Journal:  Anal Bioanal Chem       Date:  2013-01-15       Impact factor: 4.142

Review 5.  Evaluation of the association between arsenic and diabetes: a National Toxicology Program workshop review.

Authors:  Elizabeth A Maull; Habibul Ahsan; Joshua Edwards; Matthew P Longnecker; Ana Navas-Acien; Jingbo Pi; Ellen K Silbergeld; Miroslav Styblo; Chin-Hsiao Tseng; Kristina A Thayer; Dana Loomis
Journal:  Environ Health Perspect       Date:  2012-08-10       Impact factor: 9.031

  5 in total

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