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EC number: 500-204-4 | CAS number: 68334-05-4
- 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
- Study period:
- 14 Apr - 16 May 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- adopted in 2002
- Deviations:
- no
- GLP compliance:
- yes
- Type of study:
- mouse local lymph node assay (LLNA)
- Species:
- mouse
- Strain:
- CBA
- Sex:
- male/female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Harlan, Horst, The Netherlands
- Age at study initiation: 10 weeks
- Mean weight at study initiation: 20.9 g
- Housing: Individual housing in labelled Makrolon cages (MI type; height 12.5 cm) containing sterilized sawdust as bedding material (Litalabo, S.P.P.S., Argenteuil, France). Paper (Enviro-dri, Wm. Lillico & Son (Wonham Mill Ltd), Surrey, United Kingdom) was supplied as cage-enrichment.
The paper was removed on Day 1 prior to dosing and was supplied again after scoring of the ears on Day 3.
- Diet: pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany), ad libitum
- Water: tap water, ad libitum
- Acclimation period: at least 5 days before the start of treatment under laboratory conditions, accommodation was as described above except that the animals were group housed in Makrolon cages (MIII type; height 18 cm)
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21.0 ± 3.0 (actual range: 19.7 – 22.9)
- Humidity (%): 40-70 (actual range: 37 - 83)
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12 - Vehicle:
- acetone/olive oil (4:1 v/v)
- Concentration:
- 0, 25, 50 and 100% (w/w)
- No. of animals per dose:
- 5
- Details on study design:
- RANGE FINDING TESTS:
A preliminary irritation study was conducted in order to select the highest test substance concentration to be used in the main study. In principle, this concentration should be well tolerated systemically by the animals and may give moderate irritation at the highest concentration. Based on the results, the highest test substance concentration selected for the main study was a 100% concentration.
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Name of test method: Local Lymph Node Assay
- Criteria used to consider a positive response: Disintegrations Per Minute (DPM) values are presented for each animal and for each dose group. A Stimulation Index (SI) is calculated for each group. The SI is the ratio of the DPM/group compared to DPM/vehicle control group. If the results indicate a SI ≥ 3, the test substance may be regarded as a skin sensitizer, based on the test guideline and recommendations done by ICCVAM. The results were evaluated according to the Globally Harmonized System of Classification and Labelling of Chemicals (GHS) of the United Nations (2007) and the Regulation (EC) No 1272/2008 of the European Parliament and of the Council of 16 December 2008 on classification, labelling and packaging of substances and mixtures.
TREATMENT PREPARATION AND ADMINISTRATION: The dorsal surface of both ears was epidermally treated (25 μL/ear) with the test substance concentration, at approximately the same time per day. Each animal was injected via the tail vein with 0.25 mL of sterile phosphate buffered saline (PBS) (Merck, Darmstadt, Germany) containing 20 μCi of 3H-methyl thymidine (PerkinElmer Life and Analytical Sciences, Boston, MA, US). After approximately five hours, all animals were killed by intraperitoneal injection with Euthasol® 20% (AST Farma BV, Oudewater, The Netherlands). The draining (auricular) lymph node of each ear was excised. The relative size of the nodes (as compared to normal) was estimated by visual examination and abnormalities of the nodes and surrounding area were recorded. The nodes were pooled for each animal in approximately 3 mL PBS and radioactive measurements were performed using a Packard scintillation counter (2800TR). - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Positive control results:
- The six-month reliability check with alpha-hexylcinnamic aldehyde indicated that the Local Lymph Node Assay as performed at NOTOX is an appropriate model for testing for contact hypersensitivity.
- Parameter:
- SI
- Remarks on result:
- other: The SI values calculated for the substance concentrations 25, 50 and 100% were 1.6, 1.6 and 2.5, respectively.
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: Mean DPM/animal values for the experimental groups treated with test substance concentrations 25, 50 and 100% were 1644, 1717 and 2675 DPM respectively. The mean DPM/animal value for the vehicle control group was 1060 DPM.
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- CLP: not classified
DSD: not classified
Reference
Table 1: Radioactivity measurements (individual animals)
group |
test substance1(% w/w) |
animal |
DPM / animal |
||
|
|
|
|
||
1 |
0% |
1 |
1529 |
|
|
|
(Vehicle) |
2 |
578 |
|
|
|
|
3 |
1355 |
|
|
|
|
4 |
939 |
|
|
|
|
5 |
898 |
|
|
|
|
|
|
|
|
2 |
25% |
6 |
678 |
|
|
|
|
7 |
2490 |
|
|
|
|
8 |
2104 |
|
|
|
|
9 |
1235 |
|
|
|
|
10 |
1712 |
|
|
|
|
|
|
|
|
3 |
50% |
11 |
1506 |
|
|
|
|
12 |
1544 |
|
|
|
|
13 |
2260 |
|
|
|
|
14 |
1497 |
|
|
|
|
15 |
1780 |
|
|
|
|
|
|
|
|
4 |
100% |
16 |
3393 |
|
|
|
|
17 |
2354 |
|
|
|
|
18 |
2537 |
|
|
|
|
19 |
2339 |
|
|
|
|
20 |
2751 |
|
|
|
|
|
|
||
1 Vehicle: Acetone/Olive oil (4:1 v/v).
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
A Local Lymph Node Assay (LLNA) was performed according to OECD guideline 429 in male and female CBA/J mice (Stitzinger, 2010). The dorsal surface of both ears was epidermally treated (25 μL/ear) with the test substance concentrations of 25, 50 and 100% (w/w) in Acetone/Olive oil (4:1 v/v) or the vehicle alone at approximately the same time per day. Three days after the last exposure, all animals were injected with3H-methyl thymidine and after five hours the draining (auricular) lymph nodes were excised and pooled for each animal. After precipitating the lymph node cells, radioactivity measurements were performed. Mean DPM (Disintegrations Per Minute )/animal values for the experimental groups treated with test substance concentrations 25, 50 and 100% were 1644, 1717 and 2675 DPM respectively. The mean DPM/animal value for the vehicle control group was 1060 DPM. The SI values calculated for the substance concentrations 25, 50 and 100% were therefore 1.6, 1.6 and 2.5, respectively. Since there was no indication that the test substance elicits an SI (stimulation index) ≥3 when tested up to 100%, fatty acids, C18-unsaturated, dimers, 2-ethylhexyl esters was considered to be a non skin sensitizer.
Migrated from Short description of key information:
LLNA (Local Lymph Node Assay) mouse: not sensitising
Justification for selection of skin sensitisation endpoint:
There is only one study available.
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Additional information:
no data available
Migrated from Short description of key information:
no data available
Justification for selection of respiratory sensitisation endpoint:
Study not required according to Annex VII-X of Regulation (EC) No 1907/2006.
Justification for classification or non-classification
Based on the available data on skin sensitisation, Fatty acids, C18 -unsatd., dimers, 2 -ethylhexyl esters do not meet the classification criteria according to Regulation (EC) 1272/2008 or Directive 67/548/EEC, and are therefore conclusive but not sufficient for classification.
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.
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