Lead: Difference between revisions
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{{encyclopedia|moderator=Jouni|stub=Yes}} | {{encyclopedia|moderator=Jouni|stub=Yes}} | ||
'''Lead''' is a heavy metal and | [[Category:IEHIAS]] | ||
[[Category:Exposure]] | |||
[[Category:Biomarker]] | |||
:''The text on this page is taken from an equivalent page of the [[Talk:IEHIAS|IEHIAS]]-project. | |||
'''Lead''' is a heavy metal and a widespread environmental pollutant that can cause neurological, haematological and renal effects in exposed populations | |||
==Lead as a biomarker== | |||
===Sample collection and storage=== | |||
'''Matrix: | |||
Blood is the best biological matrix to monitor lead exposure | |||
'''Kinetics: | |||
*Uptake generally through inhalation or ingestion | |||
*Absorbed lead mainly stored in bones. Lead can cross the placenta and the brain- blood barriers | |||
*Lead is mainly excreted via urine and bile | |||
*Elimination follows the kinetics of a three compartment model with half-lives of 35 days (blood), 400 days (soft tissue), and 20 years (bones) | |||
'''Sampling conditions: | |||
Blood should be collected in containers free of any metal contamination. Samples can be stored at 4°C or frozen | |||
===Sample measurement=== | |||
'''Analytical aspects: | |||
*Measured through absorption spectrometry (AAS) or ICP-MS | |||
*Sensitivity of measures is 0.05-0.1 µg/l | |||
'''Performance characteristics: | |||
Analytical reproducibility is 1-2%, inter- and intralaboratory variability is 5-10% | |||
'''Validation: | |||
Measurement methods are fully validated, intercomparison programs and certified standards and reference materials is available | |||
'''Confounding factors: | |||
Smoking, alcohol consumption, menopauses and hormone-replacement therapy | |||
===Data interpretation=== | |||
'''Concentrations reported in literature: | |||
Mean values: | |||
*adults 30-50 µg/l | |||
*children 10-30 µg/l | |||
Critical values for children: 100 µg/l | |||
Occupational biological dose limit: 300 µg/l | |||
'''Dose-response/effect relationships: | |||
{| {{prettytable}} | |||
|rowspan="2"| Effects ||colspan="2"| Pb in blood (µg/l) | |||
|--- | |||
|Children || Adults | |||
|--- | |||
|Cognitive or hearing impairment || 50-100 || | |||
|--- | |||
|Vitamin D3 reduction || 100-150 || | |||
|--- | |||
|Erythrocyte porphyrin elevation || 150-200 || 200-300 | |||
|--- | |||
|Reduced haemoglobin synthesis || 250-300 || 500 | |||
|--- | |||
|Increased urinary delta-aminolevulinic acid || 400 || 400 | |||
|--- | |||
|Frank anaemia || 700 || 800 | |||
|--- | |||
|Encephalopathy || 800-1,000 || 1,000-1,200 | |||
|} | |||
'''Time trend, geographical variation, susceptibel groups: | |||
In countries where leaded-gasoline has been banned, concentrations of lead in the blood of general population have rapidly decreased to levels that are now about 70-80% lower than those prevailing in the 1970s | |||
==See also== | ==See also== | ||
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* [http://www.ncbi.nlm.nih.gov/pubmed/1891443 Kinetics of lead in bone and blood after end of occupational exposure] | * [http://www.ncbi.nlm.nih.gov/pubmed/1891443 Kinetics of lead in bone and blood after end of occupational exposure] | ||
* [http://lib.bioinfo.pl/meid:205090 Literature list of lead pharmacokinetics] | * [http://lib.bioinfo.pl/meid:205090 Literature list of lead pharmacokinetics] | ||
[http://cfpub.epa.gov/ncea/cfm/recordisplay.cfm?deid=139314] | |||
[http://cfpub.epa.gov/ncea/cfm/nceatools_human.cfm] | |||
[http://cfpub.epa.gov/ncea/cfm/recordisplay.cfm?deid=157668] | |||
[http://www.ncbi.nlm.nih.gov/pubmed/19562647] | |||
==See also== | |||
{{IEHIAS}} |
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- The text on this page is taken from an equivalent page of the IEHIAS-project.
Lead is a heavy metal and a widespread environmental pollutant that can cause neurological, haematological and renal effects in exposed populations
Lead as a biomarker
Sample collection and storage
Matrix:
Blood is the best biological matrix to monitor lead exposure
Kinetics:
- Uptake generally through inhalation or ingestion
- Absorbed lead mainly stored in bones. Lead can cross the placenta and the brain- blood barriers
- Lead is mainly excreted via urine and bile
- Elimination follows the kinetics of a three compartment model with half-lives of 35 days (blood), 400 days (soft tissue), and 20 years (bones)
Sampling conditions:
Blood should be collected in containers free of any metal contamination. Samples can be stored at 4°C or frozen
Sample measurement
Analytical aspects:
- Measured through absorption spectrometry (AAS) or ICP-MS
- Sensitivity of measures is 0.05-0.1 µg/l
Performance characteristics:
Analytical reproducibility is 1-2%, inter- and intralaboratory variability is 5-10%
Validation:
Measurement methods are fully validated, intercomparison programs and certified standards and reference materials is available
Confounding factors:
Smoking, alcohol consumption, menopauses and hormone-replacement therapy
Data interpretation
Concentrations reported in literature:
Mean values:
- adults 30-50 µg/l
- children 10-30 µg/l
Critical values for children: 100 µg/l
Occupational biological dose limit: 300 µg/l
Dose-response/effect relationships:
Effects | Pb in blood (µg/l) | |
Children | Adults | |
Cognitive or hearing impairment | 50-100 | |
Vitamin D3 reduction | 100-150 | |
Erythrocyte porphyrin elevation | 150-200 | 200-300 |
Reduced haemoglobin synthesis | 250-300 | 500 |
Increased urinary delta-aminolevulinic acid | 400 | 400 |
Frank anaemia | 700 | 800 |
Encephalopathy | 800-1,000 | 1,000-1,200 |
Time trend, geographical variation, susceptibel groups:
In countries where leaded-gasoline has been banned, concentrations of lead in the blood of general population have rapidly decreased to levels that are now about 70-80% lower than those prevailing in the 1970s
See also
- Toxicokinetics of bone lead [1]
- The development of a stochastic physiologically-based pharmacokinetic model for lead
- Dietary lead intakes for mother/child pairs and relevance to pharmacokinetic models
- Kinetics of lead in bone and blood after end of occupational exposure
- Literature list of lead pharmacokinetics