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EC number: 225-306-3 | CAS number: 4767-03-7
- 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
- Study period:
- 23 September 2009 to 04 February 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
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:
- 2,2-bis(hydroxymethyl)propionic acid
- EC Number:
- 225-306-3
- EC Name:
- 2,2-bis(hydroxymethyl)propionic acid
- Cas Number:
- 4767-03-7
- Molecular formula:
- C5H10O4
- IUPAC Name:
- 3-hydroxy-2-(hydroxymethyl)-2-methylpropanoic acid
Constituent 1
- Specific details on test material used for the study:
- - Name of the test material used in the study report: Bis-MPA TM
- Batch no.: 581017
- Purity: 98%
- Appearance: white crystalline powder
- Expiry date: 16 March 2010
- Storage conditions: ambient temperature in the dark
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- Twenty-two female (nulliparous and non-pregnant) mice of the CBA/Ca strain were used. All animals were supplied by Charles River UK Limited, Manston Road, Margate, Kent, UK and arrived at Charles River, Edinburgh on 29 September 2009. They were 7 to 8 weeks old and weighed 16 to 20 g on dispatch. The mice were acclimatized for at least 8 days, and were randomly assigned to treatment groups on arrival. Each animal received a subcutaneous implant which identified it individually within the study and which corresponded to that animal's number.
The animals were housed in groups of 2 or 3 in polycarbonate cages (dimensions 36.5 x 20.7 x 14 cm) with a stainless steel grid top and an integrated food hopper. Wood shavings were used as bedding and nesting material (‘Nestlets’) was provided. Both were supplied by Datesand Limited, Manchester, UK. A wooden chewstick, supplied by Estap OÜ, 75401 Harjumaa, Estonia, was placed in each cage as environmental enrichment. Certificates of analysis for bedding, Nestlets and chewsticks were retained by the laboratory. Analysis did not provide evidence of contamination that might have prejudiced the outcome of the study. Each cage was supplied with a water bottle.
The environment is monitored throughout the day and recordings are made every 15 min. From animal arrival to the end of the observation period, average daily environmental temperatures were within a range of approximately 21 to 22 C and the range for average daily relative humidity was approximately 46 to 61%. A 12 h light/dark cycle was in operation (light hours 0700 to 1900 h) with a minimum of 15 air changes per hour.
Rat and Mouse No. 1 Maintenance Diet (Special Diets Services, PO Box 705, Witham, Essex, UK) and water taken from the public supply (Scottish Water, Edinburgh, Midlothian, UK) were available ad libitum throughout the study. Each batch of diet is routinely analysed by the supplier for various nutritional components and chemical and microbiological contaminants. The quality of water supply is stipulated by legislation in Water Quality, Scotland, Regulations 2001 and certificates of analysis for dissolved materials, heavy metals, pesticide residues, pH, nitrates and nitrites are periodically provided. These analyses are based on water samples taken from these laboratories. The results of diet and water analyses did not provide evidence of contamination and so the outcome of the study was not prejudiced.
Study design: in vivo (LLNA)
- Vehicle:
- propylene glycol
- Concentration:
- 0, 10, 25 and 50%
- No. of animals per dose:
- 5 per/concentration
- Details on study design:
- Preliminary test: 2 females were treated with 25 µL of the 50% concentration on the dorsum of each ear for 3 consecutive days (Days 1-3). There was no treatment on days 4 and 5. Observations were conducted frequently on each day of dosing (predose, immediately post dose and approximately 1 and 2 h after dosing) and once daily thereafter until the kill, by an intravenous overdose of sodium pentobarbitone, on day 6. The animals were then discarded. There were no signs of systemic toxicity or local irritation and no effect on body weight was noted. Therefore, dose concentrations of 10%, 25% and 50% were selected as suitable non-toxic doses for administration in the main study.
Main study: For 3 consecutive days (days 1 to 3) animals received an open application of 25 μL of the appropriate formulation onto the dorsum of each ear. There was no treatment on days 4 and 5. On day 6 each animal received an intravenous injection (250 μL) of phosphate buffered saline (PBS) containing 18.7 μCi of [methyl-3H] thymidine into the lateral tail vein. Approximately 5 h after intravenous administration all animals were killed by exposure to a rising concentration of carbon dioxide and the major blood vessels were severed to exsanguinate. The lymph nodes were collected according to the methods below.
All animals were checked for viability early in the morning and again as late as possible on each day. On each day of dosing the observations were conducted predose, immediately post dose and approximately 1 and 2 h post dose. Thereafter animals were observed once daily until sacrifice on day 6 (the day of the thymidine injection). The body weight of each individual animal was recorded on day 1 (before the first dose) and on day 6.
Formulations of Bis-MPA were prepared on each day of dosing. A correction factor of 1.02 was used in preparing each formulation in order to take account of the test item purity. For each formulation the appropriate amount of Bis-MPA was weighed and transferred to a suitable glass container. Propylene glycol was added and the mixture was stirred using a magnetic stirrer and either a mechanical mixer or a mini-homogeniser until the formulation was visibly homogeneous. The formulation was then made up to the final volume. An appropriate amount of propylene glycol was also dispensed for administration to the vehicle control group. The pH of the formulation prepared on day 1 of the preliminary test and also of each of the formulations prepared on day 1 of the main study was pH 7. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- No formal statistical analysis was carried out.
Results and discussion
- Positive control results:
- The stimulation indices in a recent positive control study were 1.7, 2.4 and 5.0 for 5%, 10% and 25% hexylcinnamicaldehyde, respectively.
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Value:
- 1.5
- Test group / Remarks:
- Test item concentration of 10%.
- Remarks on result:
- other: The stimulation indices for mice treated with the test item at concentrations of 10%, 25% or 50%, when compared with the control group, were 1.5, 1.2 and 1.2, respectively.
- Parameter:
- SI
- Value:
- 1.2
- Test group / Remarks:
- Test item concentration of 25%.
- Remarks on result:
- other: The stimulation indices for mice treated with the test item at concentrations of 10%, 25% or 50%, when compared with the control group, were 1.5, 1.2 and 1.2, respectively.
- Parameter:
- SI
- Value:
- 1.2
- Test group / Remarks:
- Test item concentration of 50%.
- Remarks on result:
- other: The stimulation indices for mice treated with the test item at concentrations of 10%, 25% or 50%, when compared with the control group, were 1.5, 1.2 and 1.2, respectively.
- Parameter:
- other: disintegrations per minute (DPM)
- Test group / Remarks:
- Test item concentrations of 0%, 10%, 25% or 50%
- Remarks on result:
- other: DPM for mice (group means) treated with the test item at concentrations of 0%, 10%, 25% or 50% were 1733, 2610, 2082 and 2131, respectively.
Any other information on results incl. tables
No systemic signs were noted in any animal during the observation period. Body weight gains were considered to be acceptable for mice of this age and strain.
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- Under the conditions of the study, since treatment with Bis-MPA at concentrations of up to 50% did not achieve a stimulation index of ≥3, it was considered that the test item does not have the potential to cause sensitisation.
- Executive summary:
In a dermal sensitization study (conducted according to OECD TG 429) with Bis-MPA (purity 98%) in propylene glycol, CBA/Ca mice (7-8 weeks old, 5 females/group) were tested using the method of LLNA (OECD 429). A preliminary test using 50% formulation of Bis-MPA in 2 females on 3 consecutive days resulted in no evidence of systemic toxicity or local irritation. Therefore, for the main study, three groups were treated with concentrations prepared at 10%, 25% and 50%, respectively, for 3 consecutive days. Three days after the final application, each animal received an intravenous injection of [methyl-3H] thymidine into the lateral tail vein and 5 h later the draining lymph nodes were assessed by scintillation counting. There were no systemic signs noted in any animal during the observation period and body weight changes were considered to be acceptable for mice of this age and strain. The stimulation index (SI) values for the mice treated with Bis-MPA at concentrations of 10%, 25% or 50%, when compared with the control group, were 1.5, 1.2 and 1.2, respectively. Under the conditions of the study, Bis-MPA is not classified as a skin sensitiser.
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