Literature DB >> 20029459

Influences on transfer of selected synthetic pyrethroids from treated Formica to foods.

Lisa Jo Melnyk1, Thomas E Hieber, Tracy Turbeville, Anne P Vonderheide, Jeffrey N Morgan.   

Abstract

Children's unstructured eating habits and activities may lead to excess dietary exposures not traditionally measured by the US Environmental Protection Agency. Influence of these activities on transfer of pesticides from treated Formica to foods was studied. The objective was to perform simulation experiments using four foods (bread, apple slices, bologna, and sugar cookies) exposed to treated Formica after varied time intervals between surface contamination and contact (1, 6, and 24 h) and frequency of contact with and without recontamination. Pesticides investigated included permethrin, bifenthrin, cyfluthrin, cypermethrin, and deltamethrin. Data will be used as input parameters for transfer efficiencies (TEs) within the Children's Dietary Intake Model (CDIM), which predicts total dietary exposure of a child. Pesticide transfer from surfaces to bologna and apples was more efficient than to bread and cookies. For the bread and cookies, all pyrethroids had a TE that ranged from below detectible levels to ≤ 4%. A combined average of 32-64% and 19-43% was transferred to bologna and apples, respectively, for the three contact times for all pyrethroids. The TEs of the varied time intervals indicated that increased time between contamination and contact showed little difference for bologna, bread, and cookies, but a significant difference for apples. As long as pesticide levels are measureable on surfaces in children's eating environment, it can be concluded that transfer of pesticides to foods will take place. Foods' characteristics had an important function in the transfer of pesticides when multiple contacts occurred. Regardless of recontamination, pesticides were efficiently transferred from the treated surface to bologna. The bologna did not reach a saturation point during the contacts. Pesticides were also efficiently transferred to apples, but reached a maximum TE during the second contact. The distribution of activity factors within CDIM needs to reflect the differences in the characteristics of the foods.

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Year:  2009        PMID: 20029459     DOI: 10.1038/jes.2009.66

Source DB:  PubMed          Journal:  J Expo Sci Environ Epidemiol        ISSN: 1559-0631            Impact factor:   5.563


  3 in total

1.  Absorption of strontium by foods prepared in drinking water.

Authors:  Lisa Jo Melnyk; Maura J Donohue; Maily Pham; Joyce Donohue
Journal:  J Trace Elem Med Biol       Date:  2019-01-04       Impact factor: 3.849

2.  Assessing children's dietary pesticide exposure: direct measurement of pesticide residues in 24-hr duplicate food samples.

Authors:  Chensheng Lu; Frank J Schenck; Melanie A Pearson; Jon W Wong
Journal:  Environ Health Perspect       Date:  2010-11       Impact factor: 9.031

3.  Pesticide exposures to migrant farmworkers in Eastern NC: detection of metabolites in farmworker urine associated with housing violations and camp characteristics.

Authors:  J H Raymer; W B Studabaker; M Gardner; J Talton; S A Quandt; H Chen; L C Michael; M McCombs; T A Arcury
Journal:  Am J Ind Med       Date:  2013-11-25       Impact factor: 2.214

  3 in total

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