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EC number: 202-307-7 | CAS number: 94-13-3
- 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
Endpoint summary
Administrative data
Description of key information
Key value for chemical safety assessment
Skin sensitisation
Link to relevant study records
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- No data about GLP
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- not specified
- Type of study:
- mouse local lymph node assay (LLNA)
- Species:
- mouse
- Strain:
- other: CBA/Ca
- Sex:
- not specified
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 8 -12 weeks - Vehicle:
- acetone/olive oil (4:1 v/v)
- Concentration:
- 5, 10 and 25%
- No. of animals per dose:
- 4
- Details on study design:
- MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Criteria used to consider a positive response: A chemical was regarded as a sensitizer in the LLNA if at least one concentration of the chemical resulted in a three-fold or greater increase in ³HTdR incorporation compared to the control values. Also the data had to be compatible with a biological dose response although an allowance was made, especially at high doses, for either local toxicity or immunological suppression.
TREATMENT PREPARATION AND ADMINISTRATION:
Groups of 4 mice were treated by a daily topical application of 25 µL of each test substance concentration on the dorsal surface of each ear for 3 consecutive days. The negative control group was treated with vehicle only. Four days after the first topical application, all mice were injected intraveniously through the tail vein with 20 µCi [³H]methyl thymidine (³HTdR) in 250 µL phosphate buffered saline (PBS). After 5 h, the mice were killed by carbon dioxide asphyxiation and the draining auricular lymph nodes were excised and pooled for each group. A single cell suspension of lymph node cells was prepared. ³HTdR incorporation was measured by β-scintillation counting. - Positive control substance(s):
- mercaptobenzothiazole (CAS No 149-30-4)
- Positive control results:
- Stimulation Index:
10% positive control substance: 4.5
25% positive control substance: 4.6
50% positive control substance: 5.5 - Key result
- Parameter:
- SI
- Remarks:
- proliferation response test/control ratio
- Value:
- 1.3
- Test group / Remarks:
- 5% test item
- Remarks on result:
- other:
- Remarks:
- A chemical was regarded as a sensitizer in the LLNA if at least one concentration of the chemical resulted in a three-fold or greater increase in the T/C ration
- Key result
- Parameter:
- SI
- Remarks:
- proliferation response test/control ratio
- Value:
- 1.6
- Test group / Remarks:
- 10% test item
- Remarks on result:
- other:
- Remarks:
- A chemical was regarded as a sensitizer in the LLNA if at least one concentration of the chemical resulted in a three-fold or greater increase in the T/C ration
- Key result
- Parameter:
- SI
- Remarks:
- proliferation response test/control ratio
- Value:
- 1.3
- Test group / Remarks:
- 25% test item
- Remarks on result:
- other:
- Remarks:
- A chemical was regarded as a sensitizer in the LLNA if at least one concentration of the chemical resulted in a three-fold or greater increase in the T/C ration
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- CLP: not classified
DSD: not classified
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
Propylparaben was examined in several reliable local lymph node assays in mice according to OECD 429 (Basketter and Scholes, 1992; Basketter et al., 1991, Basketter et al., 1994). Groups of mice were treated by topical applications of 5, 10 or 25% propylparaben in acetone/olive oil (4:1, v/v) on the dorsal surface of each ear for 3 consecutive days. On Day 5, all mice were injected intravenously with 20 µCi [³H]methyl thymidine (³HTdR). After 5 h, the mice were sacrificed and a single cell suspension of draining auricular lymph nodes was prepared for each group. ³HTdR incorporation was measured by β-scintillation counting. Stimulation indices for propylparaben were in all dose groups < 3. The used positive controls were valid. Under the test conditions, propylparaben was not considered to be a skin sensitizer.
Moreover, propylparaben was examined in a Guinea Pig Maximization Test according to OECD 406 (Basketter and Scholes, 1992). After intradermal and epicutaneous induction treatment with 0.5% and 25% propylparaben and a challenge application of 10% propylparaben, no positive response was observed at the 24 and 48 h reading time point in any animal. The used positive controls were valid. Under the test conditions, propylparaben was not considered to be a skin sensitizer.
Migrated from Short description of key information:
Skin (Local Lymph Node Assay): not sensitizing
Justification for selection of skin sensitisation endpoint:
The selected study is the most adequate and reliable study based on overall quality assessment (refer to the endpoint discussion for further details).
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
The available data on skin sensitisation of the test substance does not meet the criteria for classification according to Regulation (EC) 1272/2008 or Directive 67/548/EEC, and is therefore conclusive but not sufficient for classification.
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