Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 212-110-8 | CAS number: 763-32-6
- 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP - Guideline Study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- adopted 24 April 2002
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- GLP compliance:
- yes
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- 3-methylbut-3-en-1-ol
- EC Number:
- 212-110-8
- EC Name:
- 3-methylbut-3-en-1-ol
- Cas Number:
- 763-32-6
- Molecular formula:
- C5H10O
- IUPAC Name:
- 3-methylbut-3-en-1-ol
- Details on test material:
- - Name of test material (as cited in study report): Isoprenol
- Analytical purity: 98.4 area-%; dose calculation not adjusted to purity
- Lot/batch No.: 20614288Q0
- Expiration date of the lot/batch: January 31, 2011
- Storage condition of test material: At room temperature
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- male
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Harlan Laboratories B.V., Postbus, AD Horst / The Netherlands
- Age at study initiation: 8 - 12 weeks
- Mean weight (± SD) at study initiation: 20.2 ± 1.4 g
- Housing: Single caging
- Diet (e.g. ad libitum): pelleted standard diet, ad libitum (Harlan Laboratories B.V., Netherlands)
- Water (e.g. ad libitum): tap water, ad libitum,
- Acclimation period: At least 5 days prior to the start of dosing under test conditions
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 + 2°C
- Humidity (%): 20-65%
- Photoperiod (hrs dark / hrs light): 12h/12h
Study design: in vivo (LLNA)
- Vehicle:
- acetone/olive oil (4:1 v/v)
- Concentration:
- 25, 50, and 100% (w/v)
- No. of animals per dose:
- 4
- Details on study design:
- RANGE FINDING TESTS:
- Compound solubility: The highest test item concentration, which can be technically used was 100% of the undiluted test item. The dilutions were formulated in acetone:olive oil (4+1). Vortexing was necessary to formulate the test item.
- Irritation: To determine the highest non-irritant test concentration, a pre-test was performed in two animals. Two mice were treated with concentrations of 50% and 100% each on three consecutive days. At the tested concentrations the animals did not show any signs of local irritation as confirmed by the ear thickness and ear weight measurements. Also, animals did not show any signs of systemic toxicity.
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Name of test method:
- Criteria used to consider a positive response:
TREATMENT PREPARATION AND ADMINISTRATION:
- Topical Application
Each test group of mice was treated by topical (epidermal) application to the dorsal surface of each ear (left and right) with different test item concentrations of 25, 50, and 100% (w/v) in acetone:olive oil (4+1). The application volume, 25 µl, was spread over the entire dorsal surface (8 mm) of each ear once daily for three consecutive days. A further group of mice was treated with an equivalent volume of the relevant vehicle alone (control animals).
- Administration of ³H-Methyl Thymidine
Five days after the first topical application, all mice were administered with 250 µl of 79.4 µCi/ml ³HTdR (corresponds to 19.9 µCi ³HTdR per mouse) by intravenous injection via a tail vein.
- Determination of lymph node weights
For the determination of lymph node weight, after excision, the lymph nodes were pooled per animal and weighed immediately after removal using an analytical balance.
- Determination of incorporated ³HTdR
The draining lymph nodes were rapidly excised and pooled per group (8 nodes per group). Single cell suspensions (in phosphate buffered saline) of pooled lymph node cells were prepared by gentle mechanical disaggregation through stainless steel gauze (200 µm mesh size). After further processing, the level of ³HTdR incorporation was measured on a ß-scintillation counter as the number of radioactive disintegrations per minute (DPM).
- Determination of Ear Weights
After the lymph nodes have been excised, both ears (left and right) of mice were punched at the apical area using a biopsy punch. For each animal both punches were immediately weighed per animal.
- Interpretation of Raw Data
The proliferative response of lymph node cells is expressed as the number of radioactive disintegrations per minute per lymph node (DPM/node) and as the ratio of 3HTdR incorporated into lymph node cells of test lymph nodes relative to that recorded for control lymph nodes (stimulation index). Before DPM/node values were determined, mean scintillation-background DPM was subtracted from test and control raw data.
A test item is regarded as a sensitiser in the LLNA if the following criteria are fulfilled:
• First, that exposure to at least one concentration of the test item resulted in an incorporation of 3HTdR at least 3-fold or greater than that recorded in control mice, as indicated by the stimulation index.
• Second, that the data are compatible with a conventional dose response, although allowance must be made (especially at high topical concentrations) for either local toxicity or immunological suppression. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- The mean values and standard deviations were calculated in the body weight tables.
The ANOVA (Dunnett-test) was conducted on the ear and lymph node weights to assess whether the difference is statistically significant between test item groups and negative control (vehicle) group. However, both biological and statistical significance were considered together.
Results and discussion
- Positive control results:
- Positive control substance: alpha-Hexylcinnamaldehyde
Test item concentration % (w/v) S.I.
0 1.00
5 1.21
10 2.09
25 6.22
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- other: SI
- Remarks on result:
- other: see Remark
- Remarks:
- Test item concentration % (w/v) SI 0 - 25 1.48 50 1.67 100 2.28 None of the tested concentrations induced an S.I. greater than 3.
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: Test item concentration % (w/v) Measurement DPM 0 4785 25 7070 50 7966 100 10898
- Key result
- Parameter:
- SI
- Value:
- 1.48
- Test group / Remarks:
- 25 % test group
- Key result
- Parameter:
- SI
- Value:
- 1.67
- Test group / Remarks:
- 50 % test group
- Key result
- Parameter:
- SI
- Value:
- 2.28
- Test group / Remarks:
- 100 % test group
Any other information on results incl. tables
Further results:
- No deaths occurred during the study period.
- No symptoms of local irritation at the ears of the animals and no signs of systemic toxicity were observed during the study period.
- The body weight of the animals, recorded prior to the first application and prior to treatment with ³HTdR, was within the range commonly recorded for animals of this strain and age.
- A relevant increase in ear weights was not observed.
- A statistically significant increase in lymph node weights was observed in the groups treated with 50 and 100% test item concentration in comparison to the vehicle control group (p=0.027):
Table of Lymph Node Weights
Animal No. |
Concentration |
Lymph Node Weights after Necropsy |
|
|
Lymph Node Weight (mg per animal) |
Mean Lymph Node Weight (mg per animal) |
SD |
||
1 |
0 |
3.90 |
4.45 |
0.61 |
2 |
4.30 |
|||
3 |
4.27 |
|||
4 |
5.32 |
|||
5 |
25 |
5.04 |
5.43 |
0.65 |
6 |
5.80 |
|||
7 |
4.73 |
|||
8 |
6.13 |
|||
9 |
50 |
5.91 |
6.11* |
0.73 |
10 |
5.27 |
|||
11 |
7.02 |
|||
12 |
6.25 |
|||
13 |
100 |
4.73 |
6.28* |
1.10 |
14 |
6.71 |
|||
15 |
6.36 |
|||
16 |
7.30 |
* statistically significant increase vs. control group (p=0.027)
SD= Standard Deviation
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.