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EC number: 202-500-6 | CAS number: 96-33-3
- 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
Key value for chemical safety assessment
Additional information
In-vitro studies: Bacterial systems
Methyl acrylate was not mutagenic in the Ames test in Salmonella typhimurium strains TA1535, TA1537, TA1538, TA98, TA97 and TA100, both in the presence and in the absence of S-9 mix from Aroclor 1254 induced rats when tested up to cytotoxic doses (BASF AG 1977, Waegemaekers 1984; Zeiger 1987). In addition, a modified Ames assay (plate gradient assay) was performed in ten tester strains (Salmonella typhimurium G 46, TA 1535, TA 100, C 3076, TA 1537, D 3052, TA 1538,TA 98, E. coli WP2, E. coli WP2uvrA-) with and without metabolic activation. Methyl acrylate was reported to be negative (McMahon 1979)
In-vitro studies: Mammalian cell gene mutation test
Methyl acrylate did not induce increases in mutant frequencies in the Chinese Hamster Ovary (CHO) HGPRT test performed in the absence of metabolic activation (Moore 1991), and no mutagenicity was demonstrated in AS52/XPRT Chinese hamster cells in which the hgprt gene has been largely deleted and replaced by a single copy of the functional xanthine-guanine phosphoribosyl transferase (XPRT) gene from E. coli. This test was also performed only in the absence of metabolic activation (Oberly 1993).
In contrast, methyl acrylate was active at clearly cytotoxic concentrations (≤ 50% cell survival) in the Mouse Lymphoma TK+/- mutation assay using L5178Y cells in the absence of metabolic activation (Moore 1988, 1989). The majority of the mutant colonies were small colonies, suggesting that methyl acrylate did act via a clastogenic mechanism (Moore 1988, 1989, Amtower 1986).
Moore et al have described a mutagenic effect of Methylacrylate in the TK assay. The induction of mutant colonies was also closely associated with the induced cytotoxicity. It has been previously reported, that Glutathione has a high affinity for Methylacrylate. This could lead to a depletion of the intracellular levels of Glutathione. In the study by BAMM (2019) the cultures were treated with the same levels of the test substance as previously described to be cytotoxic and mutagenic. Furthermore, a group of the cultures were replenished with Glutathione in order to assess the impact of Glutathione supplementation on mutagenicity and cytotoxicity. The results in the absence of supplementary Glutathione confirmed the data from Moore et al. However, the addition of 1 mM Glutathione abrogated this observed cytotoxicity. Furthermore, according to the results of the present in vitro study, the test substance Methylacrylate did not lead to a relevant increase in the number of mutant colonies after the addition of 1 mM Glutathione The mutant frequencies at any concentration were close to the range of the concurrent vehicle control value and within the range of historical negative control data without S9 mix.
In-vitro studies: Genotoxicity tests
There is a number of chromosome aberration tests in vitro available for MA (Ishidate 1981, Moore et al. 1988, 1989). Assays were performed with CHL cells, L5178Y mouse lymphoma cells and CHO cells with (Ishidate 1981) and without metabolic activation (Ishidate 1981, Moore et al. 1988, 1989). All assays gave positive or equivocal results at doses which reduced cell survival to 50 % or lower. There were no doses tested for chromosome aberrations which resulted in 60 % cell survival or more. Thus, there is no experimental evidence that MA might cause chromosome aberrations at non-cytotoxic doses.
More recent studies have indicated that there is an association between chromosomal aberrations and cytotoxicity at exposure concentrations which reduce cell growth to less than 50% of the control value (Galloway, 2000 and references cited therein). These data suggest that the increase in mutagenicity reported in the cytogenicity assays with methyl acrylate may be an artifact of the experimental method.
Conclusion-In vitro studies
In vitro, methyl acrylate was negative in a variety of studies for point mutation both in the presence (Ames test only) and in the absence of metabolic activation, but induced chromosome aberrations in Chinese hamster cells, Chinese ovary cells and L5178Y mouse lymphoma cells in the absence of metabolic activation. Further studies by BAMM (2019) clearly indicate that the genotoxic effects in vitro are associated with glutathione depletion and cytotoxicity since supplimentation of glutathione completed negated the observed cytotoxicity and did not lead to a relevant increase in the number of mutant colonies.
In vivo studies
Methyl acrylate has been tested in three in vivo micronucleus assays. It did not induce micronuclei in bone marrow cells of male ddY mice exposed for 3 hours to atmospheres containing 1300 or 2100 ppm (4.64 or 7.50 mg/L) methyl acrylate. Bone marrow samples were taken at 18, 24, 30, 48 or 72 hours after exposure. (The group size was not specified) (Sofuni 1984).
No induction of micronuclei was also found in male ddY mice after single oral doses (62.5, 125 or 250 mg/kg bw; 6 mice per group) or repeated dosing (125 mg/kg bw/d for 4 consecutive days; 4 mice). Bone marrow cells were sampled 24 hours after the last dose (Hachiya 1982).
In contrast, exposure of Balb/C mice to 37.5, 75, 150 or 300 mg/kg bw (4 mice/dose; 2 injections, 24 hours apart) by the intraperitoneal route, induced a not clearly dose-dependant increase in micronuclei at toxic dose levels as evidenced by significant reductions in the ratio of polychromatic to normochromatic erythrocytes. Only a short summary of the results is available (Przybojewska 1984). The validity of the results of this study is questionable. In the available publication methyl and ethyl acrylate were tested in parallel and both are described to be positive in the mouse micronucleus test (i.p.). In the case of ethyl acrylate, different laboratories tried to reproduce the positive results reported in Przybojewsla et al. In these well conducted and documented studies the results were negative (Ashby 1989, Kligerman 1991, Hara 1994). Therefore, based on the data available and the questionability of the findings in the Przybojewska et al. study, the weight of evidence indicates that methyl acrylate is negative in vivo in mouse micronucleus studies.
Conclusion-in vivo studies
In vivo, two micronucleus tests using the inhalation and oral route in ddY mice were negative.
Galloway SM (2000). Environmental and Molecular Mutagenesis 35:191-201.
Short description of key information:
Methyl acrylate was negative in bacterial mutation tests. In gene
mutation assays in mammalian cells, i.e. HGPRT and XPRT assays, MA was
clearly negative. MA seems to have some potential for genotoxicity in
mammalian cells, presumably by a clastogenic mechanism. Further in vitro
studies confirm genotoxicity in vitro is clearly associated with
significant glutathione depletion and cytotoxicity since such effects
are completely abrogated when glutathione supplimentation is employed.
Since this effect is limited to doses with moderate to strong
cytotoxicity, it is highly unlikely that this potential will be
expressed in vivo. Methyl acrylate was negative in several in vivo mouse
micronucleus assays. Thus, taking the negative test results in vivo for
MA into consideration, it can be assumed that MA will not cause any DNA
damage, i.e. genotoxicity in vivo. Furthermore, in carconogeicity
studies conducted via the inhalation route (the most relevant route for
MA) histopathological data demonstrated toxicity (decreased body weight
gain and olfactory epithelial degeneration) in the absence of
mutagenicity (i.e. tumors) in either somatic cell or germ cells in wide
array of tissues. This comprehensive in vivo study provides strong
weight of evidence to indicate that methyl acrylate is not a mutagen in
vivo.
Endpoint Conclusion: No adverse effect observed (negative)
Justification for classification or non-classification
EU classification according to Regulation (EC) No. 1272/2008: no classification required
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