Registration Dossier
Registration Dossier
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: 700-696-2 | CAS number: 1062580-52-2
- 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

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:
- From 19 Jan to 10 Feb 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study run to a method comparable with current guidelines and to GLP
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- yes
- Type of study:
- mouse local lymph node assay (LLNA)
- Species:
- mouse
- Strain:
- other: CBA/Ca
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Harlan Laboratories UK Ltd, Bicester, Oxon, UK.
- Age at study initiation: 8-12 weeks old
- Weight at study initiation: 15-23 g
- Housing: Individual housed in suspended solid-floor polypropylene cages furnished with softwood woodflakes.
- Diet (e.g. ad libitum): Free access to mains food.
- Water (e.g. ad libitum): Free access to mains tap water.
- Acclimation period: At least 5 days.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-25°C
- Humidity (%): 30-70%
- Air changes (per hr): Approx. 15 changes per hour.
- Photoperiod (hrs dark / hrs light): 12 hours continuous light (06:00 to 18:00) and 12 hours darkness.
IN-LIFE DATES: From: 19 Jan 2009 To: 10 Feb 2009 - Vehicle:
- other: 1% pluronic L92 in distilled water
- Concentration:
- Preliminary screening test: 50 % w/w
Main test: 50%, 25% , 10% w/w and 0% (vehicle) - No. of animals per dose:
- Preliminary screening test: one mouse
Main test: four mice - Details on study design:
- Preliminary screening test
The mouse was treated by daily application of 25 μL of the test material at a concentration of 50% w/w in 1% pluronic L92 in distilled water, to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The mouse was observed twice daily on Days 1, 2 and 3 and once daily on Days 4, 5 and 6. Any signs of toxicity or excessive local irritation noted during this period were recorded. The bodyweight was recorded on Day 1 (prior to dosing) and on Day 6.
Main test
Test material administration:
Groups of four mice were treated with the test material at concentrations of 50%, 25% or 10% w/w in 1% pluronic L92 in distilled water. The mice were treated by daily application of 25 μL of the appropriate concentration of the test material to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The test material formulation was administered using an automatic micropipette and spread over the dorsal surface of the ear using the tip of the pipette.
A further group of four mice received the vehicle alone in the same manner.
3H-Methyl Thymidine administration:
Five days following the first topical application of the test material (Day 6) all mice were injected via the tail vein with 250 μL of phosphate buffered saline (PBS) containing 3H-Methyl Thymidine giving a total of 20 μCi to each mouse.
Terminal procedures:
Termination: Five hours following the administration of 3HTDR all mice were killed by carbon dioxide asphyxiation. The draining auricular lymph nodes from the four mice were excised and pooled for each experimental group. For each group 1 mL of PBS was added to the pooled lymph nodes.
Preparation of single cell suspension: A single cell suspension of pooled lymph node cells was prepared by gentle mechanical disaggregation through a 200-mesh stainless steel gauze. The lymph node cells were rinsed through the gauze with 4 mL of PBS into a petri dish labelled with the project number and dose concentration. The lymph node cell suspension was transferred to a centrifuge tube. The petri dish was washed with an additional 5 mL of PBS to remove all remaining lymph node cells and these were added to the centrifuge tube. The pooled lymph node cells were pelleted at 1400 rpm for ten minutes. The pellet was resuspended in 10 mL of PBS and re-pelleted. To precipitate out the radioactive material, the pellet was resuspended in 3 mL of 5% Trichloroacetic acid (TCA).
Determination of 3HTDR incorporation: After approximately 18 hours incubation at approx. 4℃, the precipitates were recovered by centrifugation at 2100 rpm for 10 minutes, resuspended in 1 mL of TCA and transferred to 10 mL of scintillation fluid. 3HTDR incorporation was measured by β-scintillation counting. The "Poly QTM" vials containing the samples and scintillation fluid were placed in sample changer of the scintillator and left for approx. 20 minutes. The purpose of this period of time in darkness was to reduce the risk of radioactive disintegrations per minute was then measured using the Beckman LS6500 scintillation system. - Positive control substance(s):
- not specified
- Statistics:
- None stated
- Parameter:
- SI
- Remarks on result:
- other: see Remark
- Remarks:
- The SI value for the vehicle control group was NA. The SI value for the experimental group treated with test substance concentrations 10% was 0.68. The SI value for the experimental group treated with test substance concentrations 25% was 1.05. The SI value for the experimental group treated with test substance concentrations 50% was 0.70.
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: see Remark
- Remarks:
- The mean DPM/animal value for the vehicle control group was 5770.57 DPM. The mean DPM/animal value for the experimental group treated with test substance concentrations 10% was 3916.51 DPM. The mean DPM/animal value for the experimental group treated with test substance concentrations 25% was 6034.62 DPM. The mean DPM/animal value for the experimental group treated with test substance concentrations 50% was 4029.25 DPM.
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The test substance was considered to be a non-sensitiser under the conditions of the test.
Reference
Clinical observations and Mortality data:
There were no deaths. No signs of systemic toxicity were noted in the test or control animals during the test. Off white material on the ears was noted in animals treated with the test material at concentrations of 50% or 25% w/w in 1% pluronic L92 in distilled water.
Bodyweight:
Bodyweight changes of the test animals between Day 1 and Day 6 were comparable to those observed in the corresponding control group animals over the same period.
Disintegrations per minute, Disintegrations per minute/Node and Stimulation index:
Concentration (% w/w) |
DPM |
DPM/Node |
SI |
Result |
0 (vehicle) |
5770.57 |
721.32 |
NA |
Negative |
10% |
3916.51 |
489.56 |
0.68 |
Negative |
25% |
6034.62 |
754.33 |
1.05 |
Negative |
50% |
4029.25 |
503.66 |
0.70 |
Negative |
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
A LLNA study was conducted according to OECD 429 using mouse (Pooles, 2009). Key study.
This study showed that the test substance could not elicit a SI ≥3, hence the test substance is not sensitising.
Migrated from Short description of key information:
A LLNA study (Pooles, 2009) is available which is key study. This study showed that the test substance is not sensitising.
Justification for selection of skin sensitisation endpoint:
Study run to a method comparable with current guidelines and to GLP
Justification for classification or non-classification
Skin sensitisation: Animal test gave negative result (LLNA SI < 3 (actual value 1.05)).
Therefore in accordance with Regulation (EC) No. 1272/2008 Table 3.4.2 the test substance is not classified for the skin sensitisation endpoint.
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.
