Literature DB >> 3384487

Exposure to lead and cadmium of children living in different areas of north-west Germany: results of biological monitoring studies 1982-1986.

A Brockhaus1, W Collet, R Dolgner, R Engelke, U Ewers, I Freier, E Jermann, U Krämer, N Manojlovic, M Turfeld.   

Abstract

Between 1982 and 1986 several surveys were carried out to determine the levels of lead and cadmium in blood, urine, and shed deciduous teeth (incisors only) of children living in rural, suburban, urban, and industrial areas of North-West Germany. Blood lead (PbB) and blood cadmium (CdB) were measured in about 4000 children. In rural, suburban and urban areas the median PbB levels vary between 5.5 and 7 micrograms/dl, with 98th percentiles varying between 10 and 13 micrograms/dl. The median CdB levels are between 0.1 and 0.2 microgram/dl, with 95th percentiles between 0.3 and 0.4 microgram/l. Children from urban areas have significantly higher PbB levels than children from rural and suburban areas. Regarding CdB no differences could be detected. Children living in areas around lead and zinc smelters, particularly those living very close to the smelters, have substantially increased PbB and CdB levels. Children from lead worker families also have substantially increased PbB and CdB levels. The lead levels in shed milk teeth (PbT) were determined in about 3000 children. In rural, suburban and urban areas the median PbT levels are between 2 and 3 micrograms/g, with 95th percentiles between 4 and 7 micrograms/g. Children from urban areas have significantly higher PbT levels than children from rural and suburban areas. The highest PbT levels (on a group basis) are in children from nonferrous smelter areas. The median levels of lead in urine (PbU) are between 6 and 10 micrograms/g creatinine, with 95th percentiles between 20 and 30 micrograms/g creatinine. Children from polluted areas have higher PbU levels than children from less polluted areas. The median levels of cadmium in urine (CdU) are in the order of 0.1 microgram/g creatinine, with 95th percentiles being in the range of 0.5 and 1.0 microgram/g creatinine. Girls have higher CdU levels than boys. There are no differences between groups of children from different areas. Children from lead worker families have higher PbU and CdU levels than otherwise comparable children. The results of the present studies indicate a further decrease of PbB in children from North-West Germany since the CEC blood lead campaigns carried out in 1979 and 1981. The decrease of lead exposure also seems to be reflected by a decrease of tooth lead levels.

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Year:  1988        PMID: 3384487     DOI: 10.1007/bf00378699

Source DB:  PubMed          Journal:  Int Arch Occup Environ Health        ISSN: 0340-0131            Impact factor:   3.015


  33 in total

1.  [Studies of lead and cadmium exposure in children and adolescents in an area exposed to heavy metals (Stolberg)].

Authors:  U Ewers; R Dolgner; A Brockhaus; I Freier; E Jermann; W Hilser; K Domisch; R Braun
Journal:  Offentl Gesundheitswes       Date:  1984-05

2.  The Arnhem Lead Study. I. Lead uptake by 1- to 3-year-old children living in the vicinity of a secondary lead smelter in Arnhem, The Netherlands.

Authors:  B Brunekreef; S J Veenstra; K Biersteker; J S Boleij
Journal:  Environ Res       Date:  1981-08       Impact factor: 6.498

3.  Contributions to automated trace analysis. Part II. Rapid method for the automated determination of lead in whole blood by electrothermal atomic-absorption spectrophotometry.

Authors:  M Stoeppler; K Brandt; T C Rains
Journal:  Analyst       Date:  1978-07       Impact factor: 4.616

4.  Assessment and comparison of human exposure to lead between Belgium, Malta, Mexico and Sweden.

Authors:  F Claeys-Thoreau; L Thiessen; P Bruaux; G Ducoffre; G Verduyn
Journal:  Int Arch Occup Environ Health       Date:  1987       Impact factor: 3.015

5.  [Cadmium content of whole blood of inhabitants from various regions of Bavaria].

Authors:  K H Schaller; L Schneider; G Hall; H Valentin
Journal:  Zentralbl Bakteriol Mikrobiol Hyg B       Date:  1984-01

6.  Increased dietary cadmium absorption in mice and human subjects with iron deficiency.

Authors:  P R Flanagan; J S McLellan; J Haist; G Cherian; M J Chamberlain; L S Valberg
Journal:  Gastroenterology       Date:  1978-05       Impact factor: 22.682

7.  Levels of cadmium and lead in blood in relation to smoking, sex, occupation, and other factors in an adult population of the FRG.

Authors:  A Brockhaus; I Freier; U Ewers; E Jermann; R Dolgner
Journal:  Int Arch Occup Environ Health       Date:  1983       Impact factor: 3.015

8.  [Indoor and outdoor lead burden in pregnant women and newborn infants in the Nordenham region].

Authors:  H L Thron; G Biesewig
Journal:  Schriftenr Ver Wasser Boden Lufthyg       Date:  1984

9.  Environmental exposure to cadmium and renal function of elderly women living in cadmium-polluted areas of the Federal Republic of Germany.

Authors:  U Ewers; A Brockhaus; R Dolgner; I Freier; E Jermann; A Bernard; R Stiller-Winkler; R Hahn; N Manojlovic
Journal:  Int Arch Occup Environ Health       Date:  1985       Impact factor: 3.015

10.  Contribution of lead in dust to children's blood lead.

Authors:  M J Duggan
Journal:  Environ Health Perspect       Date:  1983-04       Impact factor: 9.031

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  8 in total

1.  Chemical speciation and bioaccessibility of lead in surface soil and house dust, Lavrion urban area, Attiki, Hellas.

Authors:  Alecos Demetriades; Xiangdong Li; Michael H Ramsey; Iain Thornton
Journal:  Environ Geochem Health       Date:  2010-06-04       Impact factor: 4.609

2.  Internal lead and cadmium exposure in 6-year-old children from western and eastern Germany.

Authors:  J Begerow; I Freier; M Turfeld; U Krämer; L Dunemann
Journal:  Int Arch Occup Environ Health       Date:  1994       Impact factor: 3.015

3.  Blood lead levels in children and pregnant women living near a lead-reclamation plant.

Authors:  P Levallois; M Lavoie; L Goulet; A J Nantel; S Gingras
Journal:  CMAJ       Date:  1991-04-01       Impact factor: 8.262

4.  Urinary heavy metals, phthalates, phenols, thiocyanate, parabens, pesticides, polyaromatic hydrocarbons but not arsenic or polyfluorinated compounds are associated with adult oral health: USA NHANES, 2011-2012.

Authors:  Ivy Shiue
Journal:  Environ Sci Pollut Res Int       Date:  2015-05-28       Impact factor: 4.223

5.  High lead content of deciduous teeth in chronic renal failure.

Authors:  K Schärer; G Veits; A Brockhaus; U Ewers
Journal:  Pediatr Nephrol       Date:  1991-11       Impact factor: 3.714

6.  Substantial decrease of blood lead in Swedish children, 1978-94, associated with petrol lead.

Authors:  U Strömberg; A Schütz; S Skerfving
Journal:  Occup Environ Med       Date:  1995-11       Impact factor: 4.402

7.  Temporal changes in blood lead levels of hazardous waste workers in New Jersey, 1984-1987.

Authors:  M Gochfeld; I Udasin; E Favata; G Buckler; C Natarelli; J Burger
Journal:  Environ Monit Assess       Date:  1993-04       Impact factor: 2.513

8.  Advantages of the use of deciduous teeth, hair, and blood analysis for lead and cadmium bio-monitoring in children. A study of 6-year-old children from Krakow (Poland).

Authors:  Henryk J Barton
Journal:  Biol Trace Elem Res       Date:  2010-11-18       Impact factor: 3.738

  8 in total

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