Literature DB >> 24254680

Biological monitoring, by in vivo XRF measurements, of occupational exposure to lead, cadmium, and mercury.

S Skerfving1, J O Christoffersson, A Schütz, H Welinder, G Spång, L Ahlgren, S Mattsson.   

Abstract

In vivo X-ray fluorescence (XRF) techniques were used for biological monitoring of lead, cadmium, and mercury. Lead accumulates in bone, the level of which may thus be used for monitoring of exposure. However, there was no close association between lead levels in bone and exposure time, partly because of differences in exposure patterns and partly, probably, because of variations in the toxicokinetics of lead. There are at least two separate bone lead compartments. The average over-all half-time is probably 5-10 yr. The finger bone level may be an index of the lead status of the total skeleton. In lead workers, the mobilization of bone lead causes an "internal" lead exposure and affects the blood lead level considerably. In cadmium workers, in vivo XRF is a sensitive and risk-free method for assessment of accumulation in kidney cortex, the critical tissue as to toxic effects; workers displayed increased levels. However, there was no clear association with duration and intensity of exposure, cadmium levels in urine, or microglobulinuria. Determinations of kidney cadmium may add important information on the state of accumulation and, thus, risk of kidney damage. Workers exposed to elemental mercury vapor, as well as fishermen exposed to methyl mercury, had mercury levels in bone below the detection limit of the XRF method.

Entities:  

Year:  1987        PMID: 24254680     DOI: 10.1007/BF02796636

Source DB:  PubMed          Journal:  Biol Trace Elem Res        ISSN: 0163-4984            Impact factor:   3.738


  11 in total

1.  Long-term sampling of airborne cadmium dust in an alkaline battery factory.

Authors:  E Adamsson
Journal:  Scand J Work Environ Health       Date:  1979-09       Impact factor: 5.024

2.  Methylmercury exposure, mercury levels in blood and hair, and health status in Swedes consuming contaminated fish.

Authors:  S Skerfving
Journal:  Toxicology       Date:  1974-03       Impact factor: 4.221

3.  Elimination of chromium in urine after stainless steel welding.

Authors:  H Welinder; M Littorin; B Gullberg; S Skerfving
Journal:  Scand J Work Environ Health       Date:  1983-10       Impact factor: 5.024

4.  Conceptual problems in establishing the critical concentration of cadmium in human kidney cortex.

Authors:  T Kjellström; C G Elinder; L Friberg
Journal:  Environ Res       Date:  1984-04       Impact factor: 6.498

5.  In vivo measurement of liver and kidney cadmium in workers exposed to this metal: its significance with respect to cadmium in blood and urine.

Authors:  H A Roels; R R Lauwerys; J P Buchet; A Bernard; D R Chettle; T C Harvey; I K Al-Haddad
Journal:  Environ Res       Date:  1981-10       Impact factor: 6.498

6.  In-vivo determination of lead in the skeleton after occupational exposure to lead.

Authors:  L Ahlgren; B Haeger-Aronsen; S Mattsson; A Schütz
Journal:  Br J Ind Med       Date:  1980-05

7.  Blood cell gamma-aminolevulinic acid dehydratase activity in humans exposed to methylmercury.

Authors:  A Schutz; S Skerfving
Journal:  Scand J Work Environ Health       Date:  1975-03       Impact factor: 5.024

8.  X-ray fluorescence analysis of lead in human skeleton in vivo.

Authors:  L Ahlgren; K Lidén; S Mattsson; S Tejning
Journal:  Scand J Work Environ Health       Date:  1976-06       Impact factor: 5.024

9.  Kinetic analysis of lead metabolism in healthy humans.

Authors:  M B Rabinowitz; G W Wetherill; J D Kopple
Journal:  J Clin Invest       Date:  1976-08       Impact factor: 14.808

10.  Polarised X-rays in XRF-analysis for improved in vivo detectability of cadmium in man.

Authors:  J O Christoffersson; S Mattsson
Journal:  Phys Med Biol       Date:  1983-10       Impact factor: 3.609

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