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EC number: 227-642-6 | CAS number: 5919-74-4
- 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
Skin sensitisation in vivo (OECD 429, LLNA): not sensitising
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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
- Species:
- mouse
- Strain:
- CBA/Ca
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Envigo RMS B.V. Inc., Postbus 6174, 5960 AD Horst,The Netherlands
- Age at study initiation: 9 - 10 weeks (pretest and main test)
- Weight at study initiation: 18.5 - 22.2 g (main test); 18.4 - 21.2 g (pretest)
- Housing: 1 animal per cage
- Diet: Kliba mouse/rat maintenance diet “GLP”, supplied by Provimi Kliba SA, Kaiseraugst, Basel, Switzerland, ad libitum.
- Water: Drinking water ad libitum
- Acclimation period: al least 5 days before the first application
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24
- Humidity (%): 30 - 70
- Photoperiod (hrs dark / hrs light): 12/12 - Vehicle:
- methyl ethyl ketone
- Concentration:
- 25, 50 and 100%
- No. of animals per dose:
- 5
- Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- Mean values and standard deviations of the measured parameters were calculated for the test and control groups from the individual values. The stimulation indices of 3H-thymidine incorporation, cell count, lymph node weight and ear weight were calculated as the ratio of the test group mean values for these parameters divided by those of the vehicle control group or untreated control group.
3H-thymidine incorporation, cell count, lymph node weight and ear weight: WILCOXON-Test - Parameter:
- SI
- Value:
- 0.72
- Test group / Remarks:
- 25% in MEK
- Parameter:
- SI
- Value:
- 0.8
- Test group / Remarks:
- 50% in MEK
- Parameter:
- SI
- Value:
- 3.04
- Test group / Remarks:
- undilutest test substance
- Parameter:
- SI
- Value:
- 1
- Test group / Remarks:
- vehicle MEK
- Parameter:
- SI
- Value:
- 1
- Test group / Remarks:
- untreated
- Interpretation of results:
- other: CLP/EU GHS criteria are not met, no classification required according to Regulations (EC) No 1272/2008.
- Conclusions:
- Glycerol Monomethacrylate (GMMA) does not exhibit a skin sensitizing potential in the Murine Local Lymph Node Assay under the test conditions chosen.
Reference
Test Group |
Treatment |
³H-thymidine |
Cell Count |
Lymph Node Weight |
Ear Weight |
||||
1 |
Untreated |
1.00 |
|
1.00 |
|
1.00 |
|
1.00 |
|
2 |
vehicle MEK |
1.00 |
1.00 |
|
1.00 |
1.00 |
|
||
3 |
25% in MEK1 |
0.72 |
N.S. |
0.78 |
N.S. |
0.86 |
N.S. |
0.98 |
N.S. |
4 |
50% in MEK1 |
0.80 |
N.S. |
0.68 |
N.S. |
0.78 |
N.S. |
0.92 |
N.S. |
5 |
Undiluted test substance2 |
3.04 |
# |
1.05 |
N.S. |
0.99 |
N.S. |
0.98 |
N.S. |
The statistical evaluations were performed using the WILCOXON-test (# for p≤0.05, ## for p≤0.01); N.S. = not significant
1test group versus vehicle control;2test group versus untreated control
The mean body weight of test group 5 decreased considerably over the study period, indicating systemic toxicity. Beside the body weight loss of test group 5, no further signs of systemic toxicity were noticed during general observation.
When applied undiluted, the test substance induced a statistically significant increase of 3H-thymidine incorporation into the cells from the auricular lymph nodes at the border of biological relevance (increase to 3.0 fold of control value = stimulation index (SI) ≥ 3.0).However, neither the cell count index nor lymph node weight index substantiate this finding.
No increases in 3H-thymidine incorporation, lymph node cell counts and lymph node weights were observed at the concentrations of 50% and 25%.
No increase of ear weights compared to the respective control group was observed in all concentrations. The animals treated with the undiluted test substance or with the 50% concentration exhibited a slight swelling of the ear skin on study day 1 and 2. Furthermore, an accumulation of the applied test item with concomitant slight erythema of the affected skin in the shoulder and neck region was observed in both concentrations during the observation period. However, the test substance did not induce relevant skin irritation at the application site up to the highest tested concentration. Due to the borderline increase of 3H-thymidine incorporation and the absence of a concentration-dependent effect in combination with the presence of test-substance related body weight loss, the SI-increase in 3H-thymidine incorporation of the undiluted test substance is not considered to indicate a skin sensitizing potential.
Moreover, due to signs of systemic toxicity, effects observed after application of the undiluted test substance should be considered with cautiousness as induction of rather unspecific systemic effects due to general toxicity cannot be excluded.
Thus, it is concluded that Glycerol Monomethacrylate (GMMA) does not exhibit a skin sensitizing potential in the Murine Local Lymph Node Assay under the test conditions chosen.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
The skin sensitising potential of 2,3-Dihydroxypropyl methacrylate (GMMA) (CAS 5919-74-4) was evaluated in a Murine Local Lymph Node Assay performed according to OECD 429 (BASF SE, 2017). Groups of 5 female CBA/CaOlaHsd mice each were treated with the undiluted test substance, 50% and 25% w/w preparations of the test substance in Methyl Ethyl Ketone (MEK) or with the vehicle alone, respectively. Additionally, untreated control animals were used for the comparison versus animals of the high dose group (undiluted test substance). The study used 3 test groups and 2 control groups. Each test animal was treated with 25 µL per ear of the appropriate test-substance preparation, applied to the dorsal surface of both ears for three consecutive days. The vehicle control group was treated with 25 µL of the vehicle per ear. The second control group was left untreated. Three days after the last application, 250 µL of sterile saline containing 20 µCi of3H-thymidine was injected into each animal via one lateral tail vein. Immediately after sacrifice a circular tissue sample (diameter 0.8 cm) from each animal was punched out of the apical part of each ear. The ear samples were pooled per animal and the weight was determined. The measurements served for detection of a potential inflammatory ear swelling. Incorporation of3H thymidine into the cells was measured in a β-scintillation counter.
The mean body weight of the test group that had been treated with the undiluted test substance, decreased considerably over the study period, indicating systemic toxicity. Beside the body weight loss observed in this test group, no further signs of systemic toxicity were noticed during general observations. When applied undiluted, the test substance induced a statistically significant increase of3H-thymidine incorporation into the cells from the auricular lymph nodes at the border of biological relevance (increase to 3.0 fold of control value = stimulation index (SI) ≥ 3.0). However, neither the cell count index nor lymph node weight index substantiated this finding. No increases in3H-thymidine incorporation, lymph node cell counts and lymph node weights were observed at the concentrations of 50% and 25%. No increase of ear weights compared to the respective control group was observed in any of the concentrations. The animals treated with the undiluted test substance or with the 50% concentration exhibited a slight swelling of the ear skin on study day 1 and 2. Furthermore, an accumulation of the applied test item with concomitant slight erythema of the affected skin in the shoulder and neck region was observed in both concentrations during the observation period. However, the test substance did not induce relevant skin irritation at the application site up to the highest tested concentration. Due to the borderline increase of3H-thymidine incorporation and the absence of a concentration-dependent effect in combination with the presence of test-substance related body weight loss, the increase in3H-thymidine incorporation following application of the undiluted test substance is not considered to indicate a skin sensitizing potential.
Moreover, due to signs of systemic toxicity, effects observed after application of the undiluted test substance should be considered with cautiousness as induction of rather unspecific systemic effects due to general toxicity cannot be excluded.
Thus, it is concluded that Glycerol Monomethacrylate (GMMA) does not exhibit a skin sensitizing potential in the Murine Local Lymph Node Assay under the test conditions chosen.
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
The available data on skin sensitization do not meet the criteria for classification according to Regulation (EC) No. 1272/2008, and are therefore conclusive but not sufficient for classification.
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