Major Limitations in Using Element Concentrations in Hair as Biomarkers of Exposure to Toxic and Essential Trace Elements in Children

Hair is a commonly used exposure biomarker for metals and other trace elements, but concern has been raised regarding its appropriateness for assessing the internal dose. The aim of the present study was to evaluate children's hair as biomarker of internal dose for toxic (As, Mn, Cd, Pb) and es...

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Veröffentlicht in:Environmental health perspectives 2017-06, Vol.125 (6), p.067021-067021
Hauptverfasser: Skröder, Helena, Kippler, Maria, Nermell, Barbro, Tofail, Fahmida, Levi, Michael, Rahman, Syed Moshfiqur, Raqib, Rubhana, Vahter, Marie
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container_end_page 067021
container_issue 6
container_start_page 067021
container_title Environmental health perspectives
container_volume 125
creator Skröder, Helena
Kippler, Maria
Nermell, Barbro
Tofail, Fahmida
Levi, Michael
Rahman, Syed Moshfiqur
Raqib, Rubhana
Vahter, Marie
description Hair is a commonly used exposure biomarker for metals and other trace elements, but concern has been raised regarding its appropriateness for assessing the internal dose. The aim of the present study was to evaluate children's hair as biomarker of internal dose for toxic (As, Mn, Cd, Pb) and essential elements (Mg, Ca, Fe, Co, Cu, Zn, Se, Mo). In 207 children (9-10 years of age), originating from a population-based cohort in rural Bangladesh, we measured concentrations of the selected elements in hair ( closest to the scalp) using ICP-MS. We compared these with previously measured concentrations in erythrocytes, urine, and water. For a subset of children (n=19), we analyzed four consecutive 2 cm pieces of hair. There were strong associations between hair As and the other biomarkers (erythrocytes: =0.73, p
doi_str_mv 10.1289/EHP1239
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The aim of the present study was to evaluate children's hair as biomarker of internal dose for toxic (As, Mn, Cd, Pb) and essential elements (Mg, Ca, Fe, Co, Cu, Zn, Se, Mo). In 207 children (9-10 years of age), originating from a population-based cohort in rural Bangladesh, we measured concentrations of the selected elements in hair ( closest to the scalp) using ICP-MS. We compared these with previously measured concentrations in erythrocytes, urine, and water. For a subset of children (n=19), we analyzed four consecutive 2 cm pieces of hair. There were strong associations between hair As and the other biomarkers (erythrocytes: =0.73, p<0.001; urine: rS=0.66, p<0.001); and water ( =0.60, p<0.001); and there were significant correlations between Se in hair and erythrocytes (overall =0.38, p<0.001), and urine ( =0.29, p<0.001). Hair Co and Mo showed weak correlations with concentrations in erythrocytes. Hair Mn was not associated with Mn in erythrocytes, urine, or water, and the geometric mean concentration increased almost five times from the 2 cm closest to the head to the 7th–8th cm (p<0.001). Also Mg, Ca, Co, Cd, and Pb increased from the scalp outward (>50% higher in 7th–8th cm compared with 1st–2nd cm, p<0.001). Hair was found to be a useful exposure biomarker of absorbed As and Se only. 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The aim of the present study was to evaluate children's hair as biomarker of internal dose for toxic (As, Mn, Cd, Pb) and essential elements (Mg, Ca, Fe, Co, Cu, Zn, Se, Mo). In 207 children (9-10 years of age), originating from a population-based cohort in rural Bangladesh, we measured concentrations of the selected elements in hair ( closest to the scalp) using ICP-MS. We compared these with previously measured concentrations in erythrocytes, urine, and water. For a subset of children (n=19), we analyzed four consecutive 2 cm pieces of hair. There were strong associations between hair As and the other biomarkers (erythrocytes: =0.73, p<0.001; urine: rS=0.66, p<0.001); and water ( =0.60, p<0.001); and there were significant correlations between Se in hair and erythrocytes (overall =0.38, p<0.001), and urine ( =0.29, p<0.001). Hair Co and Mo showed weak correlations with concentrations in erythrocytes. Hair Mn was not associated with Mn in erythrocytes, urine, or water, and the geometric mean concentration increased almost five times from the 2 cm closest to the head to the 7th–8th cm (p<0.001). Also Mg, Ca, Co, Cd, and Pb increased from the scalp outward (>50% higher in 7th–8th cm compared with 1st–2nd cm, p<0.001). Hair was found to be a useful exposure biomarker of absorbed As and Se only. Of all measured elements, hair Mn seemed the least reflective of internal dose. https://doi.org/10.1289/EHP1239.]]></description><subject>Acids</subject><subject>Age</subject><subject>Analysis</subject><subject>Arsenic</subject><subject>Bangladesh</subject><subject>Bioindicators</subject><subject>Biological markers</subject><subject>Biomarkers</subject><subject>Biomarkers - analysis</subject><subject>Cadmium</subject><subject>Child</subject><subject>Children</subject><subject>Children &amp; youth</subject><subject>Cognitive ability</subject><subject>Copper</subject><subject>Drinking water</subject><subject>Environmental Exposure - analysis</subject><subject>Environmental Exposure - statistics &amp; numerical data</subject><subject>Environmental Pollutants - analysis</subject><subject>Erythrocytes</subject><subject>Exposure</subject><subject>Female</subject><subject>Hair</subject><subject>Hair - chemistry</subject><subject>Hair analysis</subject><subject>Humans</subject><subject>Iron</subject><subject>Laboratories</subject><subject>Lead</subject><subject>Magnesium</subject><subject>Male</subject><subject>Manganese</subject><subject>Metals</subject><subject>Pregnancy</subject><subject>Quality control</subject><subject>Scalp</subject><subject>Seafood</subject><subject>Selenium</subject><subject>Set theory</subject><subject>Surveillance</subject><subject>Trace elements</subject><subject>Trace Elements - analysis</subject><subject>Trace metals</subject><subject>Urine</subject><subject>Zinc</subject><issn>0091-6765</issn><issn>1552-9924</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2017</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>8G5</sourceid><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><sourceid>GUQSH</sourceid><sourceid>M2O</sourceid><sourceid>D8T</sourceid><recordid>eNqNk1Fv0zAQxyMEYt1AfANkCYnBQ4aT2E78gjSqQicVDUHHq-U4l9ZdYhc7gfIB-N54bbcuaA_ID2f5fve3784XRS8SfJakBX83mX5J0ow_ikYJpWnMeUoeRyOMeRKznNGj6Nj7FcY4KRh7Gh2lwXCe8VH057NcWYdmutWd7LQ1HmmDrrw2CzRpoAXTobE1Klh38E-ldkh69EHbVrprcB7ZGk02a-t7B6izaG43WiFpKjTxPgRr2aC5kwpuVbc646VuKgfmWfSklo2H53t7El19nMzH03h2-elifD6LVY5pF0tZpqTKeAW8UDIkx0tZ5ZRJLmlV56rEZV6XNGGUEoJTKlWwNaFJlZdFjXF2EsU7Xf8L1n0p1k6H9_8WVmqxP7oOOxCEU8ZZ4N_v-OBpodpVoRmEDT1GL8XC_hQ0JxklWRB4sxdw9kcPvhOt9gqaRhqwvRcJD_0K8BZ99Q-6sr0zoRwixSRlRZGy_EAtZANCm9qGe9WNqDgnvCgIywk75DmgFmAgPNIaqHU4HvBnD_BhVdBq9WDA20FAYDrYdAvZey8uvn39f_by-5B9fY9dgmy6pbdNv_15Q_B0BypnvXdQ3zUlweJmJMR-JAL58n4P77jbGcj-AkTwBFg</recordid><startdate>20170601</startdate><enddate>20170601</enddate><creator>Skröder, Helena</creator><creator>Kippler, Maria</creator><creator>Nermell, Barbro</creator><creator>Tofail, Fahmida</creator><creator>Levi, Michael</creator><creator>Rahman, Syed Moshfiqur</creator><creator>Raqib, Rubhana</creator><creator>Vahter, Marie</creator><general>National Institute of Environmental Health Sciences</general><general>Environmental Health Perspectives</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>IOV</scope><scope>ISR</scope><scope>3V.</scope><scope>4T-</scope><scope>4U-</scope><scope>7RV</scope><scope>7ST</scope><scope>7T7</scope><scope>7U7</scope><scope>7WY</scope><scope>7WZ</scope><scope>7X7</scope><scope>7XB</scope><scope>87Z</scope><scope>88E</scope><scope>8AO</scope><scope>8C1</scope><scope>8FD</scope><scope>8FE</scope><scope>8FG</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>8FL</scope><scope>8G5</scope><scope>ABJCF</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>AN0</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BEZIV</scope><scope>BGLVJ</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>FRNLG</scope><scope>FYUFA</scope><scope>F~G</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>GUQSH</scope><scope>HCIFZ</scope><scope>K60</scope><scope>K6~</scope><scope>K9-</scope><scope>K9.</scope><scope>KB0</scope><scope>L.-</scope><scope>L6V</scope><scope>M0C</scope><scope>M0R</scope><scope>M0S</scope><scope>M1P</scope><scope>M2O</scope><scope>M7S</scope><scope>MBDVC</scope><scope>NAPCQ</scope><scope>P64</scope><scope>PATMY</scope><scope>PIMPY</scope><scope>PQBIZ</scope><scope>PQBZA</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PTHSS</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>S0X</scope><scope>SOI</scope><scope>7X8</scope><scope>5PM</scope><scope>ADTPV</scope><scope>AOWAS</scope><scope>D8T</scope><scope>ZZAVC</scope></search><sort><creationdate>20170601</creationdate><title>Major Limitations in Using Element Concentrations in Hair as Biomarkers of Exposure to Toxic and Essential Trace Elements in Children</title><author>Skröder, Helena ; 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The aim of the present study was to evaluate children's hair as biomarker of internal dose for toxic (As, Mn, Cd, Pb) and essential elements (Mg, Ca, Fe, Co, Cu, Zn, Se, Mo). In 207 children (9-10 years of age), originating from a population-based cohort in rural Bangladesh, we measured concentrations of the selected elements in hair ( closest to the scalp) using ICP-MS. We compared these with previously measured concentrations in erythrocytes, urine, and water. For a subset of children (n=19), we analyzed four consecutive 2 cm pieces of hair. There were strong associations between hair As and the other biomarkers (erythrocytes: =0.73, p<0.001; urine: rS=0.66, p<0.001); and water ( =0.60, p<0.001); and there were significant correlations between Se in hair and erythrocytes (overall =0.38, p<0.001), and urine ( =0.29, p<0.001). Hair Co and Mo showed weak correlations with concentrations in erythrocytes. Hair Mn was not associated with Mn in erythrocytes, urine, or water, and the geometric mean concentration increased almost five times from the 2 cm closest to the head to the 7th–8th cm (p<0.001). Also Mg, Ca, Co, Cd, and Pb increased from the scalp outward (>50% higher in 7th–8th cm compared with 1st–2nd cm, p<0.001). Hair was found to be a useful exposure biomarker of absorbed As and Se only. Of all measured elements, hair Mn seemed the least reflective of internal dose. https://doi.org/10.1289/EHP1239.]]></abstract><cop>United States</cop><pub>National Institute of Environmental Health Sciences</pub><pmid>28669939</pmid><doi>10.1289/EHP1239</doi><tpages>67021(-67019)</tpages><oa>free_for_read</oa></addata></record>
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subjects Acids
Age
Analysis
Arsenic
Bangladesh
Bioindicators
Biological markers
Biomarkers
Biomarkers - analysis
Cadmium
Child
Children
Children & youth
Cognitive ability
Copper
Drinking water
Environmental Exposure - analysis
Environmental Exposure - statistics & numerical data
Environmental Pollutants - analysis
Erythrocytes
Exposure
Female
Hair
Hair - chemistry
Hair analysis
Humans
Iron
Laboratories
Lead
Magnesium
Male
Manganese
Metals
Pregnancy
Quality control
Scalp
Seafood
Selenium
Set theory
Surveillance
Trace elements
Trace Elements - analysis
Trace metals
Urine
Zinc
title Major Limitations in Using Element Concentrations in Hair as Biomarkers of Exposure to Toxic and Essential Trace Elements in Children
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