Literature DB >> 9169060

Simulated dermal contamination with capillary samples and field cholinesterase biomonitoring.

K L Yuknavage1, R A Fenske, D A Kalman, M C Keifer, C E Furlong.   

Abstract

The extensive international use of organophosphorus compounds (OP) results in numerous acute intoxications each year. OPs inhibit acetylcholinesterase, the enzyme responsible for breaking down the neurotransmitter acetylcholine. The World Health Organization recognizes cholinesterase (ChE) biomonitoring as a preventive measure against OP overexposure. The aim of this study was to determine if dermal OP contamination could interfere with current field ChE biomonitoring assays, which use a fingerstick blood sample. In this study we also sought to determine if high levels of a plasma enzyme, A-esterase, could protect ChE from inhibition by hydrolyzing environmentally generated oxons potentially present in a fingerstick sample. A heparinized venous blood sample was collected from a volunteer. Erythrocyte acetylcholinesterase (AChE) and plasma butyrylcholinesterase (PChE) activities were measured using a field-based colorimetric cholinesterase kit. ChE dose-response curves were constructed by allowing 10-microliters blood samples to contact environmentally realistic levels of OP thioate and oxon for 10 s. An inhibition threshold could not be established for PChE when exposed to oxon within the time necessary to perform a fingerstick analysis. AChE was also inhibited by trace amounts of oxon consistent with previously reported environmental levels. These findings suggest that the reliability of field-based biomonitoring results is limited if OP residues remain on a skin surface at the time of sample collection. A-esterase's role in protecting ChE activity was investigated using capillary and venous blood from 30 unexposed individuals. Baseline ChE activities were measured, as were individual A-esterase activities using paraoxon, diazoxon, and phenylacetate as substrates. Results were then compared to ChE activities measured after 10 s of contact with an environmentally realistic amount of OP, containing 1% oxon. Both ChE activities were significantly inhibited, with capillary values being significantly more inhibited than their venous counterparts. However, no protective effect could be associated between the degree of A-esterase activity and the subsequent level of ChE inhibition observed in an individual's blood. These results suggest that (1) if there is any uncertainty about OP skin contamination, venous blood would be a more appropriate specimen to employ when using field ChE biomonitoring kits--it is collected in larger volumes and has essentially no direct contact to dermal surfaces; and (2) A-esterase activity demonstrates no protective effect against ChE inhibition upon a blood droplet's brief contact with an OP residue containing traces of oxon.

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Year:  1997        PMID: 9169060     DOI: 10.1080/00984109708984010

Source DB:  PubMed          Journal:  J Toxicol Environ Health        ISSN: 0098-4108


  9 in total

1.  Neurobehavioral assessment of mice following repeated postnatal exposure to chlorpyrifos-oxon.

Authors:  Toby B Cole; Jenna C Fisher; Thomas M Burbacher; Lucio G Costa; Clement E Furlong
Journal:  Neurotoxicol Teratol       Date:  2012-03-07       Impact factor: 3.763

2.  Repeated developmental exposure of mice to chlorpyrifos oxon is associated with paraoxonase 1 (PON1)-modulated effects on cerebellar gene expression.

Authors:  Toby B Cole; Richard P Beyer; Theo K Bammler; Sarah S Park; Federico M Farin; Lucio G Costa; Clement E Furlong
Journal:  Toxicol Sci       Date:  2011-06-14       Impact factor: 4.849

3.  Paraoxonases-1, -2 and -3: What are their functions?

Authors:  Clement E Furlong; Judit Marsillach; Gail P Jarvik; Lucio G Costa
Journal:  Chem Biol Interact       Date:  2016-05-26       Impact factor: 5.192

Review 4.  Paraoxonase-1 and Early-Life Environmental Exposures.

Authors:  Judit Marsillach; Lucio G Costa; Clement E Furlong
Journal:  Ann Glob Health       Date:  2016 Jan-Feb       Impact factor: 2.462

5.  Biomarkers of sensitivity and exposure in Washington state pesticide handlers.

Authors:  Jonathan N Hofmann; Matthew C Keifer; Harvey Checkoway; Anneclaire J De Roos; Federico M Farin; Richard A Fenske; Rebecca J Richter; Gerald van Belle; Clement E Furlong
Journal:  Adv Exp Med Biol       Date:  2010       Impact factor: 2.622

6.  Paraoxonase 1 (PON1) status and substrate hydrolysis.

Authors:  Rebecca J Richter; Gail P Jarvik; Clement E Furlong
Journal:  Toxicol Appl Pharmacol       Date:  2008-11-13       Impact factor: 4.219

7.  Repeated gestational exposure of mice to chlorpyrifos oxon is associated with paraoxonase 1 (PON1) modulated effects in maternal and fetal tissues.

Authors:  Toby B Cole; Wan-Fen Li; Aila L Co; Ariel M Hay; James W MacDonald; Theo K Bammler; Federico M Farin; Lucio G Costa; Clement E Furlong
Journal:  Toxicol Sci       Date:  2014-07-28       Impact factor: 4.849

8.  Association of in utero organophosphate pesticide exposure and fetal growth and length of gestation in an agricultural population.

Authors:  Brenda Eskenazi; Kim Harley; Asa Bradman; Erin Weltzien; Nicholas P Jewell; Dana B Barr; Clement E Furlong; Nina T Holland
Journal:  Environ Health Perspect       Date:  2004-07       Impact factor: 9.031

9.  Serum cholinesterase inhibition in relation to paraoxonase-1 (PON1) status among organophosphate-exposed agricultural pesticide handlers.

Authors:  Jonathan N Hofmann; Matthew C Keifer; Clement E Furlong; Anneclaire J De Roos; Federico M Farin; Richard A Fenske; Gerald van Belle; Harvey Checkoway
Journal:  Environ Health Perspect       Date:  2009-06-09       Impact factor: 9.031

  9 in total

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