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Diss Factsheets
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EC number: 239-290-0 | CAS number: 15245-44-0
- 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
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption in vivo
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 948
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Rats were lightly anesthetized and preparations of lead acetate (77 mg Pb/rat), lead ortho arsenate (102 mg Pb/rat) or lead oleate (148 mg Pb/rat) were applied to an area of 29 square centimeters on clipped dorsal skin. In some experiments, mechanical injury to the skin was induced prior to application. The substances were rubbed in for two minutes with a glass rod, then, without removal of excess, the animals were wrapped in a cylindrical celluloid shield cemented to the body at the shoulders and hips, which prevented bending of the body and oral contact with the shield. After 24 or 48 hours, animals were sacrificed and various organs were removed for measurement of lead. An equal number of control animals were analyzed with each exposure.
- GLP compliance:
- no
Test material
- Reference substance name:
- Lead acetate
- EC Number:
- 239-379-4
- EC Name:
- Lead acetate
- Cas Number:
- 15347-57-6
- IUPAC Name:
- lead(4+) tetraacetate
- Reference substance name:
- Lead ortho arsenate
- IUPAC Name:
- Lead ortho arsenate
- Reference substance name:
- Lead oleate
- EC Number:
- 239-378-9
- EC Name:
- Lead oleate
- Cas Number:
- 15347-55-4
- IUPAC Name:
- lead(4+) tetraoctadec-9-enoate
- Reference substance name:
- Lead tetraethyl
- IUPAC Name:
- Lead tetraethyl
- Details on test material:
- Lead acetate was in aqueous solution, lead ortho arsenate was an aqueous paste, and lead oleate was an ointment in petrolatum and oleic acid vehicles.
Constituent 1
Constituent 2
Constituent 3
Constituent 4
- Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- not specified
- Sex:
- not specified
- Details on test animals or test system and environmental conditions:
- No details provided on test animals and environmental conditions, with the exception that the rats were of uniform size and weighed between 300 and 350 grams.
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- other: water; petrolatum; oleic acid
- Duration of exposure:
- 24 or 48 hours.
- Doses:
- Lead acetate: 77 mg lead/rat
Lead ortho arsenate: 102 mg lead/rat
Lead oleate: 148 mg lead/rat - Control animals:
- yes
- Remarks:
- Negative controls were used, but no information was provided on whether the control animals received vehicle or no treatment.
Results and discussion
- Signs and symptoms of toxicity:
- not examined
- Dermal irritation:
- not examined
- Absorption in different matrices:
- In the experiments with lead oleate in petrolatum vehicle, the concentration of lead in kidney and in skin from the leg was higher in treated animals compared to controls. The lead concentration was not higher in liver, muscle, lung, brain, spleen, gastrointestinal tract, or thigh bone. Absorption of lead acetate and lead oleate, as measured in the kidney, was higher when applied to skin that underwent mechanical injury (Table 1). A comparison of the absorption of lead in the kidney from lead oleate, lead acetate, and lead arsenate is shown in Table 2. Absorption of lead arsenate was similar to control values. The absorption of lead acetate appeared to be higher than that of lead oleate, but the difference was not statistically significant. Absorption of lead from these three lead compounds was also compared to that of lead tetraethyl. Measurements of lead in kidneys were 10- to 20-fold higher with lead tetraethyl than with the three nonvolatile lead compounds.
Any other information on results incl. tables
Table 1: Effect of injury to the skin on absorption of lead compounds, as measured by lead concentration in kidney (ug lead per gram wet kidney).
Lead Oleate - Intact | Lead Oleate - Injured | Lead Acetate - Intact | Lead Acetate - Injured | |
1.3 | 4.9 | --- | --- | |
3.3 | 5.1 | --- | --- | |
0.80 | 3.1 | 1.4 | 2.3 | |
0.60 | 7.1 | 1.7 | 4.5 | |
0.90 | 4.1 | 2.9 | 7.8 | |
0.82 | 1.9 | 1.5 | 7.2 | |
1.3 | 3.8 | 2.1 | 6.4 | |
0.90 | 3.6 | 1.0 | 7.3 | |
Average | 1.3 | 4.2 | 1.8 | 5.9 |
Table 2: Comparison of the cutaneous penetration of lead from three different compounds, as measured by lead concentration in kidney (ug lead per gram wet kidney).
24 -Hr Exposure | Control | |
Lead Oleate (n = 12) | 1.3 | 0.59 |
Lead Acetate (n = 6) | 1.8 | 0.82 |
Lead Arsenate (n = 8) | 0.85 | 0.55 |
Applicant's summary and conclusion
- Conclusions:
- The authors concluded that: (1) cutaneous absorption of lead oleate, lead acetate, and lead arsenate, as measured by the storage of lead in the kidneys, is extremely small; (2) mechanical injury to the skin increases the penetration of lead; and (3) the absorption of lead tetraethyl is much higher, with concentrations of lead in the kidneys being 10- to 20-fold higher than the three nonvolatile lead compounds.
- Executive summary:
Rats were lightly anesthetized and preparations of lead acetate (77 mg Pb/rat), lead ortho arsenate (102 mg Pb/rat) or lead oleate (148 mg Pb/rat) were applied to an area of 29 square centimeters of clipped dorsal skin. In some experiments, mechanical injury to the skin was induced prior to application. The substances were rubbed in for two minutes with a glass rod, then, without removal of excess, the animals were wrapped in a cylindrical celluloid shield cemented to the body at the shoulders and hips, which prevented bending of the body and oral contact with the shield. After 24 or 48 hours, animals were sacrificed and various organs were removed for measurement of lead. An equal number of control animals were analyzed with each exposure. In the experiments with lead oleate in petrolatum vehicle, the concentration of lead in kidney and in skin from the leg was higher in treated animals compared to controls. The lead concentration was not higher in liver, muscle, lung, brain, spleen, gastrointestinal tract, or thigh bone. Absorption of lead acetate and lead oleate, as measured in the kidney, was higher when applied to skin that underwent mechanical injury. A comparison of the absorption of lead in the kidney from lead oleate, lead acetate, and lead arsenate indicated that absorption of lead arsenate was similar to control values. The absorption of lead acetate appeared to be higher than that of lead oleate, but the difference was not statistically significant. Absorption of lead from these three lead compounds was also compared to that of lead tetraethyl. Measurements of lead in kidneys were 10- to 20-fold higher with lead tetraethyl than with the three nonvolatile lead compounds. The authors concluded that: (1) cutaneous absorption of lead oleate, lead acetate, and lead arsenate, as measured by the storage of lead in the kidneys, is extremely small; (2) mechanical injury to the skin increases the penetration of lead; and (3) the absorption of lead tetraethyl is much higher, with concentrations of lead in the kidneys being 10- to 20-fold higher than the three nonvolatile lead compounds.
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