Pesticide exposure and creatinine variation among young children
Pesticide exposure may differentially impact young children; they live closer to the ground and take in greater amounts of food relative to body mass than older children or adults. We are using an organophosphate (OP) urinary biomarker screen (gas chromatography with flame photometric detection, GC/...
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description | Pesticide exposure may differentially impact young children; they live closer to the ground and take in greater amounts of food relative to body mass than older children or adults. We are using an organophosphate (OP) urinary biomarker screen (gas chromatography with flame photometric detection, GC/FPD) to evaluate pesticide exposure among 154 children ≤6 years of age living in a heavily farmed border (US–Mexico) community. The screen detects diethylphosphates (DEPs) and dimethylphosphates (DMPs) above a reference range of 1000 non-occupationally exposed individuals (DL=25 µg/g creatinine, Cr). At least one metabolite was detected for 28% of the subjects; many samples contained multiple biomarkers. DEP was detected in 4% of the subjects. DMP and DMTP were frequently measured (20% and 23%, respectively). Biomarker concentrations are adjusted by the body's metabolism of Cr as an indicator of urine dilution. Cr concentrations were examined separately to evaluate their effect on internal dose measures. Cr concentrations were significantly different by season (K–W=0.83,
P
=0.022). Significant differences exist between the autumn:spring (
P
=0.038) Cr concentrations and between summer:autumn (
P
=0.041) Cr concentrations based on Mann–Whitney
U
=1070.5,
z
=−2.041, (
P
=0.041). Our analysis of NHANES III data did not reflect seasonal Cr differences for 6 year olds. No younger children were included. Absorbed daily dose (ADD) estimates were calculated for children with the highest concentrations of metabolite. Calculations are theoretical values assuming that the entirety of a given metabolite was metabolized from a single pesticide. Several class-appropriate pesticides were evaluated. For the children with the highest levels, almost all estimated ADDs exceeded the RfD. Although the actual metabolite concentrations dropped appreciably, ADD RfDs were still exceeded at the 95th percentile. The urinary OP screen was effective in identifying subjects with atypical internal doses. Daily Cr yield is a critical component in ADD calculations. Cr variability produces differences in internal dose measurement and estimates of ADD independent of exposure. Cr variability among young children needs to be examined, and caution should be applied when evaluating Cr adjusted internal doses for children. |
doi_str_mv | 10.1038/sj.jea.7500119 |
format | Article |
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P
=0.022). Significant differences exist between the autumn:spring (
P
=0.038) Cr concentrations and between summer:autumn (
P
=0.041) Cr concentrations based on Mann–Whitney
U
=1070.5,
z
=−2.041, (
P
=0.041). Our analysis of NHANES III data did not reflect seasonal Cr differences for 6 year olds. No younger children were included. Absorbed daily dose (ADD) estimates were calculated for children with the highest concentrations of metabolite. Calculations are theoretical values assuming that the entirety of a given metabolite was metabolized from a single pesticide. Several class-appropriate pesticides were evaluated. For the children with the highest levels, almost all estimated ADDs exceeded the RfD. Although the actual metabolite concentrations dropped appreciably, ADD RfDs were still exceeded at the 95th percentile. The urinary OP screen was effective in identifying subjects with atypical internal doses. Daily Cr yield is a critical component in ADD calculations. Cr variability produces differences in internal dose measurement and estimates of ADD independent of exposure. Cr variability among young children needs to be examined, and caution should be applied when evaluating Cr adjusted internal doses for children.</description><identifier>ISSN: 1559-0631</identifier><identifier>ISSN: 1053-4245</identifier><identifier>EISSN: 1559-064X</identifier><identifier>DOI: 10.1038/sj.jea.7500119</identifier><identifier>PMID: 11138659</identifier><language>eng</language><publisher>New York: Nature Publishing Group US</publisher><subject>Agriculture ; Analysis and chemistry ; Autumn ; Biomarkers ; Biomarkers - analysis ; Blood ; Body mass ; Child, Preschool ; Children ; Chromatography, Gas ; Chromium ; Creatinine ; Creatinine - urine ; Critical components ; Dilution ; Environmental aspects ; Environmental Exposure - analysis ; Epidemiology ; Estimates ; Evaluation ; Exposure ; Female ; Gas chromatography ; Health aspects ; Hispanic Americans ; Humans ; Infant ; Infant, Newborn ; Insecticides - adverse effects ; Insecticides - analysis ; Male ; Mathematical analysis ; Medicine ; Medicine & Public Health ; Metabolites ; Occupational exposure ; Organophosphates ; Organophosphorus Compounds ; Pesticides ; Physiological aspects ; Risk Assessment ; Spring ; Summer ; supplement ; Tungsten ; Variability</subject><ispartof>Journal of exposure analysis and environmental epidemiology, 2000-11, Vol.10 (Suppl 6), p.672-681</ispartof><rights>Springer Nature America, Inc. 2000</rights><rights>COPYRIGHT 2000 Nature Publishing Group</rights><rights>Copyright Nature Publishing Group Nov 2000</rights><rights>Nature Publishing Group 2000.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c453t-4a7e19a5a978dfe5d65f50fce5aa821a4a73e5adbc3fa80f96e143d363d8cda63</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://link.springer.com/content/pdf/10.1038/sj.jea.7500119$$EPDF$$P50$$Gspringer$$H</linktopdf><linktohtml>$$Uhttps://link.springer.com/10.1038/sj.jea.7500119$$EHTML$$P50$$Gspringer$$H</linktohtml><link.rule.ids>314,776,780,27901,27902,41464,42533,51294</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/11138659$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>O'ROURKE, MARY KAY</creatorcontrib><creatorcontrib>LIZARDI, PATRICIA SÁNCHEZ</creatorcontrib><creatorcontrib>ROGAN, SÉUMAS P</creatorcontrib><creatorcontrib>FREEMAN, NATALIE C</creatorcontrib><creatorcontrib>AGUIRRE, AMANDA</creatorcontrib><creatorcontrib>SAINT, CHRISTOPHER G</creatorcontrib><title>Pesticide exposure and creatinine variation among young children</title><title>Journal of exposure analysis and environmental epidemiology</title><addtitle>J Expo Sci Environ Epidemiol</addtitle><addtitle>J Expo Anal Environ Epidemiol</addtitle><description>Pesticide exposure may differentially impact young children; they live closer to the ground and take in greater amounts of food relative to body mass than older children or adults. We are using an organophosphate (OP) urinary biomarker screen (gas chromatography with flame photometric detection, GC/FPD) to evaluate pesticide exposure among 154 children ≤6 years of age living in a heavily farmed border (US–Mexico) community. The screen detects diethylphosphates (DEPs) and dimethylphosphates (DMPs) above a reference range of 1000 non-occupationally exposed individuals (DL=25 µg/g creatinine, Cr). At least one metabolite was detected for 28% of the subjects; many samples contained multiple biomarkers. DEP was detected in 4% of the subjects. DMP and DMTP were frequently measured (20% and 23%, respectively). Biomarker concentrations are adjusted by the body's metabolism of Cr as an indicator of urine dilution. Cr concentrations were examined separately to evaluate their effect on internal dose measures. Cr concentrations were significantly different by season (K–W=0.83,
P
=0.022). Significant differences exist between the autumn:spring (
P
=0.038) Cr concentrations and between summer:autumn (
P
=0.041) Cr concentrations based on Mann–Whitney
U
=1070.5,
z
=−2.041, (
P
=0.041). Our analysis of NHANES III data did not reflect seasonal Cr differences for 6 year olds. No younger children were included. Absorbed daily dose (ADD) estimates were calculated for children with the highest concentrations of metabolite. Calculations are theoretical values assuming that the entirety of a given metabolite was metabolized from a single pesticide. Several class-appropriate pesticides were evaluated. For the children with the highest levels, almost all estimated ADDs exceeded the RfD. Although the actual metabolite concentrations dropped appreciably, ADD RfDs were still exceeded at the 95th percentile. The urinary OP screen was effective in identifying subjects with atypical internal doses. Daily Cr yield is a critical component in ADD calculations. Cr variability produces differences in internal dose measurement and estimates of ADD independent of exposure. Cr variability among young children needs to be examined, and caution should be applied when evaluating Cr adjusted internal doses for children.</description><subject>Agriculture</subject><subject>Analysis and chemistry</subject><subject>Autumn</subject><subject>Biomarkers</subject><subject>Biomarkers - analysis</subject><subject>Blood</subject><subject>Body mass</subject><subject>Child, Preschool</subject><subject>Children</subject><subject>Chromatography, Gas</subject><subject>Chromium</subject><subject>Creatinine</subject><subject>Creatinine - urine</subject><subject>Critical components</subject><subject>Dilution</subject><subject>Environmental aspects</subject><subject>Environmental Exposure - analysis</subject><subject>Epidemiology</subject><subject>Estimates</subject><subject>Evaluation</subject><subject>Exposure</subject><subject>Female</subject><subject>Gas chromatography</subject><subject>Health aspects</subject><subject>Hispanic Americans</subject><subject>Humans</subject><subject>Infant</subject><subject>Infant, Newborn</subject><subject>Insecticides - adverse effects</subject><subject>Insecticides - analysis</subject><subject>Male</subject><subject>Mathematical analysis</subject><subject>Medicine</subject><subject>Medicine & Public Health</subject><subject>Metabolites</subject><subject>Occupational exposure</subject><subject>Organophosphates</subject><subject>Organophosphorus Compounds</subject><subject>Pesticides</subject><subject>Physiological aspects</subject><subject>Risk Assessment</subject><subject>Spring</subject><subject>Summer</subject><subject>supplement</subject><subject>Tungsten</subject><subject>Variability</subject><issn>1559-0631</issn><issn>1053-4245</issn><issn>1559-064X</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2000</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>BENPR</sourceid><recordid>eNp1kctLAzEQxoMotj6uHmXRc2vSbLK7N0vxBYIeFLyFMZnULN2kJl3R_96IxV4sgeRj5jeP8BFywuiYUV5fpHbcIowrQSljzQ4ZMiGaEZXly-6f5mxADlJqKS3LStJ9MmCM8VqKZkguHzGtnHYGC_xchtRHLMCbQkeElfPOY_EB0WUdfAFd8PPiK_T51m9uYSL6I7JnYZHweP0ekufrq6fZ7ej-4eZuNr0f6VLw1aiEClkDApqqNhaFkcIKajUKgHrCIOd51uZVcws1tY1EVnLDJTe1NiD5ITn_7buM4b3PS6s29NHnkWoiSyoqMal5ps62UqwRfFLJatNqDgtUztuwiqA7l7SasoZzyqvyZ-D4Hyofg53TwaN1Of5fgY4hpYhWLaPrIH4pRtWPWSq1Kpul1mblgtP1sv1rh2aDr93JwMUvkHLKzzFufrOl5TdX-566</recordid><startdate>20001101</startdate><enddate>20001101</enddate><creator>O'ROURKE, MARY KAY</creator><creator>LIZARDI, PATRICIA 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exposure and creatinine variation among young children</title><author>O'ROURKE, MARY KAY ; LIZARDI, PATRICIA SÁNCHEZ ; ROGAN, SÉUMAS P ; FREEMAN, NATALIE C ; AGUIRRE, AMANDA ; SAINT, CHRISTOPHER G</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c453t-4a7e19a5a978dfe5d65f50fce5aa821a4a73e5adbc3fa80f96e143d363d8cda63</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2000</creationdate><topic>Agriculture</topic><topic>Analysis and chemistry</topic><topic>Autumn</topic><topic>Biomarkers</topic><topic>Biomarkers - analysis</topic><topic>Blood</topic><topic>Body mass</topic><topic>Child, Preschool</topic><topic>Children</topic><topic>Chromatography, Gas</topic><topic>Chromium</topic><topic>Creatinine</topic><topic>Creatinine - urine</topic><topic>Critical components</topic><topic>Dilution</topic><topic>Environmental aspects</topic><topic>Environmental Exposure - 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SÁNCHEZ</creatorcontrib><creatorcontrib>ROGAN, SÉUMAS P</creatorcontrib><creatorcontrib>FREEMAN, NATALIE C</creatorcontrib><creatorcontrib>AGUIRRE, AMANDA</creatorcontrib><creatorcontrib>SAINT, CHRISTOPHER G</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Biotechnology Research Abstracts</collection><collection>Environment Abstracts</collection><collection>Health and Safety Science Abstracts (Full archive)</collection><collection>Toxicology Abstracts</collection><collection>Health & Medical Collection</collection><collection>ProQuest Central (purchase pre-March 2016)</collection><collection>Medical Database (Alumni Edition)</collection><collection>Science Database (Alumni Edition)</collection><collection>ProQuest Pharma 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environmental epidemiology</jtitle><stitle>J Expo Sci Environ Epidemiol</stitle><addtitle>J Expo Anal Environ Epidemiol</addtitle><date>2000-11-01</date><risdate>2000</risdate><volume>10</volume><issue>Suppl 6</issue><spage>672</spage><epage>681</epage><pages>672-681</pages><issn>1559-0631</issn><issn>1053-4245</issn><eissn>1559-064X</eissn><abstract>Pesticide exposure may differentially impact young children; they live closer to the ground and take in greater amounts of food relative to body mass than older children or adults. We are using an organophosphate (OP) urinary biomarker screen (gas chromatography with flame photometric detection, GC/FPD) to evaluate pesticide exposure among 154 children ≤6 years of age living in a heavily farmed border (US–Mexico) community. The screen detects diethylphosphates (DEPs) and dimethylphosphates (DMPs) above a reference range of 1000 non-occupationally exposed individuals (DL=25 µg/g creatinine, Cr). At least one metabolite was detected for 28% of the subjects; many samples contained multiple biomarkers. DEP was detected in 4% of the subjects. DMP and DMTP were frequently measured (20% and 23%, respectively). Biomarker concentrations are adjusted by the body's metabolism of Cr as an indicator of urine dilution. Cr concentrations were examined separately to evaluate their effect on internal dose measures. Cr concentrations were significantly different by season (K–W=0.83,
P
=0.022). Significant differences exist between the autumn:spring (
P
=0.038) Cr concentrations and between summer:autumn (
P
=0.041) Cr concentrations based on Mann–Whitney
U
=1070.5,
z
=−2.041, (
P
=0.041). Our analysis of NHANES III data did not reflect seasonal Cr differences for 6 year olds. No younger children were included. Absorbed daily dose (ADD) estimates were calculated for children with the highest concentrations of metabolite. Calculations are theoretical values assuming that the entirety of a given metabolite was metabolized from a single pesticide. Several class-appropriate pesticides were evaluated. For the children with the highest levels, almost all estimated ADDs exceeded the RfD. Although the actual metabolite concentrations dropped appreciably, ADD RfDs were still exceeded at the 95th percentile. The urinary OP screen was effective in identifying subjects with atypical internal doses. Daily Cr yield is a critical component in ADD calculations. Cr variability produces differences in internal dose measurement and estimates of ADD independent of exposure. Cr variability among young children needs to be examined, and caution should be applied when evaluating Cr adjusted internal doses for children.</abstract><cop>New York</cop><pub>Nature Publishing Group US</pub><pmid>11138659</pmid><doi>10.1038/sj.jea.7500119</doi><tpages>10</tpages></addata></record> |
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subjects | Agriculture Analysis and chemistry Autumn Biomarkers Biomarkers - analysis Blood Body mass Child, Preschool Children Chromatography, Gas Chromium Creatinine Creatinine - urine Critical components Dilution Environmental aspects Environmental Exposure - analysis Epidemiology Estimates Evaluation Exposure Female Gas chromatography Health aspects Hispanic Americans Humans Infant Infant, Newborn Insecticides - adverse effects Insecticides - analysis Male Mathematical analysis Medicine Medicine & Public Health Metabolites Occupational exposure Organophosphates Organophosphorus Compounds Pesticides Physiological aspects Risk Assessment Spring Summer supplement Tungsten Variability |
title | Pesticide exposure and creatinine variation among young children |
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