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EC number: 263-467-1 | CAS number: 62229-08-7
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Exposure related observations in humans: other data
Administrative data
- Endpoint:
- exposure-related observations in humans: other data
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 975
Materials and methods
- Endpoint addressed:
- basic toxicokinetics
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Between 1966 and 1973, up to 35 different organs and tissues from a total of 129 cadavers were analyzed for lead content. Of this total, 119 (60 male adults, 36 female adults, and 23 male and female children) had no history of occupational exposure to lead. Seven of the remaining 10 subjects, all male adults, had defined histories of occupational lead exposure. The remaining three subjects had unknown occupational histories. Causes of death were varied, and all cases had been subjected to postmortem examination for reasons associated with unusual or ill-defined causes of death.
- GLP compliance:
- no
Test material
- Reference substance name:
- Lead
- EC Number:
- 231-100-4
- EC Name:
- Lead
- Cas Number:
- 7439-92-1
- Molecular formula:
- Pb
- IUPAC Name:
- lead
Constituent 1
Method
- Ethical approval:
- not applicable
Results and discussion
- Results:
- Bone lead concentrations increased with age in both sexes, particularly in males and in dense bone, varying between mean values of 2 ppm in the ribs of children to over 50 ppm in the dense petrous temporal bones of elderly male adults. Male adults had over 30% more lead in their bones than females. Mean concentrations of lead in soft tissues varied from less than 0.1 ppm in organs such as muscle and heart to over 2 ppm in the aorta. In most tissues with lead values greater than 0.2 ppm, the male concentrations exceeded female values by about 30%. With the exception of the aorta, spleen, lung, and prostate, lead concentrations did not increase with age in the soft tissues of either sex after about the second decade of life. The concentrations of lead in the soft tissues of children were comparable to female adults, but the concentrations in bone were much lower (range of 2-5 ppm in children vs. range of 6-26 ppm in adult females).
In male adults occupationally exposed to lead, the concentrations of lead in bone exceeded the concentrations in unexposed adults within the same age group by two- to three-fold. Soft tissue lead concentrations between the two groups were less divergent.
An assessment of the total body burden of lead indicated higher levels in adult male subjects (mean value of 164.8 mg) compared to adult female subjects (mean value of 103.6 mg). Over 90% of the total body burden of lead in adults was in bone, of which over 70% was in dense bone. Male adults occupationally exposed to lead had mean total body burdens of 566.4 mg lead, of which 97% was in bone.
Lead concentrations in hair and nails were higher than soft tissue lead concentrations and varied widely. Hair lead measurements were not considered to provide a reliable assessment of lead absorption.
Applicant's summary and conclusion
- Conclusions:
- The authors concluded that the findings do not suggest that levels of lead in the environment, with the exception of unusual circumstances of exposure, have caused an increase of lead uptake in body tissues in recent decades and that the physiological capacity for humans to excrete varying quantities of absorbed lead appears to be well adapted to protect from the adverse effects of lead.
- Executive summary:
Between 1966 and 1973, up to 35 different organs and tissues from a total of 129 cadavers were analyzed for lead content. Of this total, 119 (60 male adults, 36 female adults, and 23 male and female children) had no history of occupational exposure to lead. Seven of the remaining 10 subjects, all male adults, had defined histories of occupational lead exposure. The remaining three subjects had unknown occupational histories. Causes of death were varied, and all cases had been subjected to postmortem examination for reasons associated with unusual or undefined casuses of death. Bone lead concentrations increased with age in both sexes, particularly in males and in dense bone, varying between mean values of 2 ppm in the ribs of children to over 50 ppm in the dense petrous temporal bones of elderly male adults. Male adults had over 30% more lead in their bones than females. Mean concentrations of lead in soft tissues varied from less than 0.1 ppm in organs such as muscle and heart to over 2 ppm in the aorta. In most tissues with lead values greater than 0.2 ppm, the male concentrations exceeded female values by about 30%. With the exception of the aorta, spleen, lung, and prostate, lead concentrations did not increase with age in the soft tissues of either sex after about the second decade of life. The concentrations of lead in the soft tissues of children were comparable to female adults, but the concentrations in bone were much lower (range of 2-5 ppm in children vs. range of 6-26 ppm in adult females). In male adults occupationally exposed to lead, the concentrations of lead in bone exceeded the concentrations in unexposed adults within the same age group by two- to three-fold. Soft tissue lead concentrations between the two groups were less divergent. An assessment of the total body burden of lead indicated higher levels in adult male subjects (mean value of 164.8 mg) compared to adult female subjects (mean value of 103.6 mg). Over 90% of the total body burden of lead in adults was in bone, of which over 70% was in dense bone. Male adults occupationally exposed to lead had mean total body burdens of 566.4 mb lead, of which 97% was in bone. Lead concentrations in hair and nails were higher than soft tissue lead concentrations and varied widely. Hair lead measurements were not considered to provide a reliable assessment of lead absorption. The authors concluded that the findings do not suggest that levels of lead in the environment, with the exception of unusual circumstances of exposure, have caused an increase of lead uptake in body tissues in recent decades and that the physiological capacity for humans to excrete varying quantities of absorbed lead appears to be well adapted to protect from the adverse effects of lead.
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