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EC number: 223-517-5 | CAS number: 3937-56-2
- 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:
- weight of evidence
- Study period:
- 2003-12-03 to 2003-12-08
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2004
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- 2002
- Deviations:
- yes
- Remarks:
- Lymph node proliferation was assessed by total cell count and not via tritiated thymidine incorporation.
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Nonane-1,9-diol
- EC Number:
- 223-517-5
- EC Name:
- Nonane-1,9-diol
- Cas Number:
- 3937-56-2
- Molecular formula:
- C9H20O2
- IUPAC Name:
- nonane-1,9-diol
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Chemical name: 1,9-Nonanediol
- CAS no.: 3937-56-2
- Source and lot/batch No.of test material: : BASF / 42638
- Expiration date of the lot/batch: March 2003
- Molecular weight: 160.254 g/mol
- Purity: 98.8%
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA/Ca
- Sex:
- female
- Details on test animals and environmental conditions:
- Weight at dosing: 19.5 - 25.0g
Age: 9 wks
Source: Charles River Deutschland GmbH, Sulzfeld, Germany
Acclimation period: 15 days
Diet: Kliba-Labordiat (Provimi), ad libitum
Water: Municipal water, ad libitum
Housing: Singly housed
Temperature: 20-24°C
Humidity: 30-70%
Air changes: not stated
Photoperiod: 12 hours light/dark
Study design: in vivo (LLNA)
- Vehicle:
- propylene glycol
- Concentration:
- 0, 10, 30, 60%
- No. of animals per dose:
- 6
- Details on study design:
- 1,9-Nonanediol was administered on 3 consecutive days to the dorsum of the ear of 6 female CBA mice/dose level. On each day of treatment the animals received an open application of 25 µL of the dose formulation. On day 6 all animals were sacrificed and each pair of draining auricular lymph nodes were collected from each animal. A single suspension of lymph node cells from each paired sample were prepared. Cell count was determined using a Casy-Counter.
- Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- Wilcoxon test
Results and discussion
- Positive control results:
- The positive control, alpha-hexylcinnamaldehyde, tech. 85% had a sensitising potential in the LLNA assay, thereby demonstrating the sensitivity and specificity of the assay.
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- other: Relative lymph node weight index
- Value:
- ca. 1
- Test group / Remarks:
- Vehicle control / 6 animals
- Parameter:
- other: Relative lymph node weight index
- Value:
- ca. 0.95
- Test group / Remarks:
- 10% in propylene glycol / 6 animals
- Parameter:
- other: Relative lymph node weight index
- Value:
- ca. 0.87
- Test group / Remarks:
- 30% in propylene glycol / 6 animals
- Parameter:
- other: Relative lymph node weight index
- Value:
- ca. 0.76
- Test group / Remarks:
- 60% in propylene glycol / 6 animals
- Parameter:
- other: Relative lymph node cell count index
- Value:
- ca. 1
- Test group / Remarks:
- Vehicle control / 6 animals
- Parameter:
- other: Relative lymph node cell count index
- Value:
- ca. 1.05
- Test group / Remarks:
- 10% in propylene glycol / 6 animals
- Parameter:
- other: Relative lymph node cell count index
- Value:
- ca. 0.92
- Test group / Remarks:
- 30% in propylene glycol / 6 animals
- Parameter:
- other: Relative lymph node cell count index
- Value:
- ca. 0.88
- Test group / Remarks:
- 60% in propylene glycol / 6 animals
- Parameter:
- SI
- Test group / Remarks:
- Vehicle control / 6 animals
- Remarks on result:
- not measured/tested
- Parameter:
- SI
- Test group / Remarks:
- 10% propylene glycol / 6 animals
- Remarks on result:
- not measured/tested
- Parameter:
- SI
- Test group / Remarks:
- 30% in propylene glycol / 6 animals
- Remarks on result:
- not measured/tested
- Parameter:
- SI
- Test group / Remarks:
- 60% in propylene glycol
- Remarks on result:
- not measured/tested
- Cellular proliferation data / Observations:
- refer to Table 7.4.1/01
Any other information on results incl. tables
There were no clinical signs of toxicity observed, with all animals gaining weight. All animals receiving 1,9-Nonanediol at 10, 30 and 60% did not induce a statistically significant increase in either lymph node weight or lymph node cell counts.
A statistically significant increase in ear weight was observed in animals treated at 30%, this however was not deemed biologically relevant as it was not dose related.
Table
7.4.1/01:
Individual and group mean data
Group (%) |
Lymph node weight (mg) |
Lymph node weight index1 |
Lymph node cell count |
Lymph node index1 |
Ear weight (mg) |
Ear weight index1 |
Untreated |
4.3 ±0.7 |
0.89 |
6296833 |
0.89 |
27.8 ±2.3 |
0.97 |
Vehicle (propylene glycol) |
4.9± 0.5 |
1.00 |
7082167 |
1.00 |
28.7 ±1.8 |
1.00 |
10% |
4.6 ±0.4 |
0.95 |
7458833 |
1.05 |
30.4 ±1.3 |
1.06 |
30% |
4.3 ±0.5 |
0.87 |
6546500 |
0.92 |
31.1 ±1.8 |
1.08* |
60% |
3.7 ±0.8 |
0.76 |
6232167 |
0.88 |
29.9 ±0.9 |
1.04 |
Positive control |
||||||
Vehicle (acetone) |
- |
1.00 |
- |
1.00 |
- |
1.00 |
1% HCA in acetone |
- |
1.08 |
- |
1.25 |
- |
1.07* |
3% HCA in acetone |
- |
1.21* |
- |
1.56* |
- |
1.14** |
10% HCA in acetone |
- |
1.73** |
- |
2.58** |
- |
1.14** |
* test group / vehicle control * p<0.05; ** p<0.01 |
Deficiencies:
Lymph node proliferation was assessed by total cell count and not via tritiated thymidine incorporation.
Ear erythema was not assessed by thickness at the end of treatment, but via ear weight. A defined area of 0.8 cm was punched out of the apical part of each ear and for each animal the weight of the pooled punches was determined in order to obtain an indication of possible skin irritation.
Evidence of skin sensitisation was based on statistically significant increases in lymph node cell count and/or lymph node weight compared to the vehicle control. Whilst it is recognised that this study is insufficient in addressing the endpoint sufficiently, a weight of evidence approach has been taken to address this endpoint conclusively.
Applicant's summary and conclusion
- Interpretation of results:
- study cannot be used for classification
- Conclusions:
- Under the condition of the study, administration of 1,9-Nonanediol to mice at concentrations of 10%, 30% or 60% resulted in lymph node cell counts and lymph node weights which were comparable to the vehicle control. In accordance with the criteria defined by Ulrich et al (2001) 1,9-Nonanediol was not considered to be a skin sensitizer. This study provides supportive information but it is not suitable for classification and labelling purposes.
- Executive summary:
1,9-Nonanediol was administered on 3 consecutive days to the dorsum of the ear of 6 female CBA mice/dose level. On each day of treatment the animals received an open application of 25 µL of the dose formulation. On day 6 all animals were sacrificed and each pair of draining auricular lymph nodes were collected from each animal. A single suspension of lymph node cells from each paired sample were prepared. Cell count was determined using a Casy-Counter.
The weight of ear punches taken from the areas of test article application as a measure of inflammatory ear swelling was determined, serving as an indicator for the irritant action of the test article.
A positive control study was conducted using hexylcinnamic aldehyde (HCA) approximately six-months before the study on 1,9-Nonanediol and confirmed the specificity and sensitivity of the assay.
There were no clinical signs of toxicity observed, with all animals gaining weight. All animals receiving 1,9-Nonanediol at 10, 30 and 60% did not induce a statistically significant increase in either lymph node weight or lymph node cell counts.
A statistically significant increase in ear weight was observed in animals treated at 30%, this however was not deemed biologically relevant as it was not dose related.
Under the condition of the study, administration of 1,9-Nonanediol to mice at concentrations of 10%, 30% or 60% resulted in lymph node cell counts and lymph node weights which were comparable to the vehicle control. In accordance with the criteria defined by Ulrich et al (2001) 1,9-Nonanediol was not considered to be a skin sensitizer. This study provides supportive information but it is not suitable for classification and labelling purposes.
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