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EC number: 218-463-4 | CAS number: 2156-97-0
- 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:
- supporting study
- Study period:
- 25 Oct 2005 - 22 Nov 2005
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: OECD guideline study conducted in compliance with GLP regulations
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
- Report date:
- 2006
- Reference Type:
- publication
- Title:
- Comparative analysis of skin sensitization potency of acrylates (methyl acrylate, ethyl acrylate, butyl acrylate, and ethylhexyl acrylate) using the local lymph node assay.
- Author:
- Dearman RJ, Betts CJ, Farr C, McLaughlin J, Berdasco N, Wiench K, Kimber I
- Year:
- 2 007
- Bibliographic source:
- Contact Dermatitis 57: 242-247
Materials and methods
Test guideline
- 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)
Test material
- Reference substance name:
- 2-ethylhexyl acrylate
- EC Number:
- 203-080-7
- EC Name:
- 2-ethylhexyl acrylate
- Details on test material:
- - Name of test material (as cited in study report): ethylhexyl acrylate
- Substance type: pure substance
- Physical state: liquid
- Analytical purity: 99.84 %
- Purity test date: 10 Feb 2006 (reanalysis)
- Lot/batch No.: CTL bottle No 281914, 011093eda0, GV/T No. 00/0903-3
- Expiration date of the lot/batch: 31 May 2006 (reanalysed February 2006)
- Stability under test conditions: stable
- Storage condition of test material: Ambient temperature in the dark
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Strain: CBA/Ca/Ola/Hsd
- Source: Harlan Interfauna UK Limited, Blackthorne, Bicester, Oxon, UK
- Age at study initiation: Young adults (8-12 weeks of age)
- Mean body weight at study initiation: 19.2 g
- Housing: maximum of 4 mice per cage
- Diet (ad libitum): Diet (RM1), supplied by Special Diet Services Limited, Witham, Essex, UK
- Water (ad libitum): mains water
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22±3°C
- Humidity (%): 30-70%
- Air changes (per hr): A minimum of 15 changes per hour
- Photoperiod (hrs dark / hrs light): 12 hours light, 12 hours dark
Study design: in vivo (LLNA)
- Vehicle:
- acetone/olive oil (4:1 v/v)
- Concentration:
- 0.5, 1, 2.5, 5 and 10 % w/v
- No. of animals per dose:
- 4
- Details on study design:
- RANGE FINDING TESTS
A preliminary sighting study was conducted on one animal per dose group for 2.5, 10 and 50 % w/v concentrations to determine the acceptable toxicity and lymph node activation levels.
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Criteria used to consider a positive response: The criterion for a positive response is that one or more concentrations of the test substance
should elicit a 3-fold or greater increase in isotope incorporation relative to the vehicle control group.
TREATMENT PREPARATION AND ADMINISTRATION:
Groups of four female mice were used for the main LLNA study. Approximately 25μl of a 0.5, 1, 2.5, 5 or 10 % w/v preparation of the test substance in acetone in olive oil (4:1) was applied, using a variable volume micro-pipette, to the dorsal surface of each ear. A vehicle control group was similarly treated using acetone in olive oil (4:1) alone. The procedure was repeated daily for 3 consecutive days.
Three days after the third application, all the animals were injected, via the tail vein, with approximately 250μl of phosphate buffered saline (PBS) containing 20μCi of a 2.0Ci/mmol specific activity 3H-methyl thymidine. Approximately 5 hours later, the animals were humanely killed by inhalation of halothane vapour followed by cervical dislocation. The draining auricular lymph nodes were removed from each animal and, together with the nodes from the other animals in the group, were placed in a container of PBS.
A single cell suspension was prepared by mechanical disaggregation of lymph nodes through a 200-mesh stainless steel gauze. The cell suspensions were then washed three times by centrifugation with approximately 10mL of PBS. Approximately 3mL of 5 % w/v trichloroacetic acid (TCA) was added and, after overnight precipitation at 4°C, the samples were pelleted by centrifugation and the supernatant was discarded. The cells were then resuspended in approximately 1 mL of TCA.
The lymph node suspensions were transferred to scintillation vials and 10 mL of scintillant (Optiphase) was added prior to β-scintillation counting using a Packard Tri-Carb 3100TR Liquid Scintillation Counter.
Animals were checked at least once daily for signs of systemic toxicity.
The bodyweight of each animal was recorded prior to dosing on day 1 and prior to injection of 3H-methyl thymidine on day 6 for LLNA study mice or prior to termination for sighting study mice. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- The EC3 value was derived by interpolating between two points on the Stimulation Index (SI) axis, one immediately above and the other immediately below the SI value of 3 (vehicle-treated control values [SI=1] not being used for the latter). Where the data points lying immediately above and below the SI value of three have the co-ordinates a (the concentration giving the SI immediately above 3), b (the SI of a), c (the concentration giving the SI immediately below 3) and d (the SI of c), the EC3 value was calculated using the following equation:
EC3 = [(3-d)/(b-d)] x (a-c) + c
Results and discussion
- Positive control results:
- The application of hexylcinnamaldehyde at concentrations of 5 %, 10 % and 25 % w/v in acetone : olive oil (4:1) resulted in a greater than 3-fold increase in isotope incorporation at the 10 and 25 % w/v concentrations. Therefore, hexylcinnamaldehyde was shown to be a skin sensitiser, confirming the validity of the protocol used for the study.
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Remarks on result:
- other: 3.1
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: At 10 % w/v 17989 dpm.
Any other information on results incl. tables
Concentration of test substance (% w/v) |
Number of lymph nodes assayed |
Disintegrations per minute (dpm) |
dpm per lymph node |
Test : control ratio (SI) |
0 (vehicle only) |
8 |
5822 |
728 |
N/A |
0.5 |
8 |
6172 |
772 |
1.1 |
1 |
8 |
7026 |
878 |
1.2 |
2.5 |
8 |
5503 |
688 |
1.0 |
5 |
8 |
7012 |
877 |
1.2 |
10 |
8 |
17989 |
2249 |
3.1 |
EC3 |
Calculated to be 9.7 % (2425μg/cm2) |
N/A - not applicable
The application of the test substance at concentrations of 0.5, 1, 2.5, 5 and 10 %w/v in acetone : olive oil (4:1) resulted in an increase in isotope incorporation which was greater than 3-fold at the 10 % w/v concentration. Consequently, the test substance was shown to be a potential skin sensitiser. The concentration giving rise to a 3 fold increase in lymphocyte proliferation (EC3) was calculated to be 9.7 % w/v (2425 μg/cm2), indicative of a sensitiser of moderate potency.
Applicant's summary and conclusion
- Interpretation of results:
- sensitising
- Remarks:
- Migrated information
- Conclusions:
- According to test results, the test substance is a sensitiser of moderate potency.
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