Registration Dossier
Registration Dossier
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EC number: 212-084-8 | CAS number: 760-93-0
- 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
Endpoint summary
Administrative data
Link to relevant study record(s)
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
- Objective of study:
- metabolism
- Principles of method if other than guideline:
- Determination of half-life in blood after i.v. application
- GLP compliance:
- not specified
- Radiolabelling:
- no
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Route of administration:
- intravenous
- Vehicle:
- physiological saline
- Details on exposure:
- Single i.v. injections of 10 or 20 mg/kg at a dosing volume of 2 ml/kg in physiological saline
- No. of animals per sex per dose / concentration:
- 2 at 10 mg/kg
3 at 20 mg/kg - Control animals:
- no
- Details on study design:
- A series of in vitro and in vivo studies with a series of methacrylates were used to develop PBPK models that accurately predict the metabolism and fate of these monomers. This study segment was performed in order to validate the model.
- Details on dosing and sampling:
- Blood samples were taken at defined intervals post-dosing. Not more than 10 % of the total average blood volume were taken.
- Toxicokinetic parameters:
- half-life 1st: 1.7 min
- Toxicokinetic parameters:
- other: Vmax = 19.8 mg/ hr * SRW
- Remarks:
- SRW = standard rat weight (250 g)
- Toxicokinetic parameters:
- other: km = 20.3 mg/L
- Conclusions:
- In conclusion, from a simultaneous fit of the in vivo data to a one-compartment model with non-linear elimination the half-life of MAA in blood was calculated to 1.7 min.
- Executive summary:
The PBPK model data were validated by i.v. administration of MAA in rats and subsequent analysis of blood from the tail vein.
In conclusion, from a simultaneous fit of the in vivo data to a one-compartment model with non-linear elimination, the half-life of MAA in blood was calculated to 1.7 min.
NOTE: Any of data in this dataset are disseminated by the European Union on a right-to-know basis and this is not a publication in the same sense as a book or an article in a journal. The right of ownership in any part of this information is reserved by the data owner(s). The use of this information for any other, e.g. commercial purpose is strictly reserved to the data owners and those persons or legal entities having paid the respective access fee for the intended purpose.
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Objective of study:
- other: adsorption and development of analytical method
- Principles of method if other than guideline:
- The test material was administered by gavage and analytically determined in blood
- GLP compliance:
- not specified
- Species:
- rat
- Strain:
- Wistar
- Sex:
- not specified
- Details on test animals or test system and environmental conditions:
- The test animals weighed 3-400 g
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- 2 ml of the test substance were administered as a 1 M aqueous solution.
- Duration and frequency of treatment / exposure:
- Animals were sacrificed at various(not specified) times after administration and blood was collected for determination of MAA.
- Details on dosing and sampling:
- Analysis by HPLC/UV-VIS; detection at 210/240 nM
LoQ: 0.5 µM - Conclusions:
- After a single oral administration of the sodium salt of methacrylic acid to Wistar rats (540 mg/kg bw) methacrylic acid was detected in the blood serum by means of HPLC. The maximum concentration was found after 10 min, whereas after 60 min no more methacrylic acid was detectable.
- Executive summary:
The presence of methacrylic acid (quantity not determined) was reported in Wistar rat blood serum 10 min after oral gavage administration of 2 ml of a 1 M solution of sodium methacrylate. After 60 min MAA could not anymore be detected in the blood serum (detection limit 0.5 µmol/l).
- Endpoint:
- basic toxicokinetics, other
- Remarks:
- (Q)SAR
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- accepted calculation method
- Justification for type of information:
- 1. SOFTWARE OECD toolbox
2. SMILES USED AS INPUT FOR THE MODEL CC(=C)C(=O)OCCOC(=O)C(=C)C - Principles of method if other than guideline:
- Protein/GSH reactivity modelling with OECD Toolbox
- GLP compliance:
- no
- Conclusions:
- No reactivity with GSH expected for MAA
A dataset with methacrylic acid derivatives has been assessed using the reactivity profiler in the OECD QSAR Toolbox. This profiler contains structural alerts derived from an analysis of experimental reactivity data as measured using glutathione (the Schultz assay). The profiler assigns chemicals to one of five potency classes (non-reactive, slightly reactive, moderately reactive, highly reactive and extremely reactive) based on the experimental results.
For Methacrylic acid, no alert was found, while the majority of the methacrylate esters are slightly reactive. For methacrylate esters it is well known that the addition of an alkyl group on the alpha-carbon significantly reduces reactivity in the Michael addition reaction.
There are also a group of vinyl carboxamides (methacrylamide derivatives) that have been flagged as being moderately reactive. It should be noted, however, that in the underlying QSAR data in the TB there is no information regarding the effect of an alpha substituent for this class of chemical. In reality this means that no chemicals were tested with glutathione that contained an alpha alkyl substituent thus the prediction is being made based on the un-substituted parent (acrylamide; thus the over-cautious prediction). The investigator indicated that they are likely to be pretty unreactive in reality. - Executive summary:
A dataset with methacrylic acid derivatives has been assessed using the reactivity profiler in the OECD QSAR Toolbox. This profiler contains structural alerts derived from an analysis of experimental reactivity data as measured using glutathione (the Schultz assay). The profiler assigns chemicals to one of five potency classes (non-reactive, slightly reactive, moderately reactive, highly reactive and extremely reactive) based on the experimental results.
For Methacrylic acid, no alert was found, while the majority of the methacrylate esters are slightly reactive. For methacrylate esters it is well known that the addition of an alkyl group on the alpha-carbon significantly reduces reactivity in the Michael addition reaction.
There are also a group of vinyl carboxamides (methacrylamide derivatives) that have been flagged as being moderately reactive. It should be noted, however, that in the underlying QSAR data in the TB there is no information regarding the effect of an alpha substituent for this class of chemical. In reality this means that no chemicals were tested with glutathione that contained an alpha alkyl substituent thus the prediction is being made based on the un-substituted parent (acrylamide; thus the over-cautious prediction). The investigator indicated that they are likely to be pretty unreactive in reality.
- Endpoint:
- basic toxicokinetics
- Type of information:
- other: modelling
- Adequacy of study:
- supporting study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- accepted calculation method
- Objective of study:
- toxicokinetics
- Principles of method if other than guideline:
- A hybrid 9 and physiologically based pharmacokinetic inhalation model was constructed based on modifications of a CFD-PBPK model for acrylic acid.
- GLP compliance:
- no
- Radiolabelling:
- no
- Species:
- rat
- Details on study design:
- Chemical specific partitioning for a variety of tissues and physicochemical characteristics (molecular weight and pKa) were incorporated into the model. The rate of ionization was 100 ml/hr/µmol.
To model human physiology in the workplace, additional CFD simulations were conducted at a flow rate of 35 L/min which approximates the inspiratory flow rate associated with a work load of 50 W and minute volume of 20-25 L/min. An oral shunt of air flow into the nasopharynx was include din the model to accomodate the switch from nasal to oronasal breathing with increasing workload.
Liquid-air partitioning of acrylic acid vapor was evaluated for saline (buffered to pH 2.0) and rat blood, liver, kidney, inguinal fat and nasal tissue. - Details on absorption:
- The CFD-PBPK model predicted that whole-nose uptake of MAA would be 95% of the 20 ppm inhaled vapor concentration at a unidirectional flow rate of 200 ml/min. Simulated exposure of the human nasal cavity at a unidirectional flow rate of 18.9 and 35.0 L/min resulted in predicted whole nose uptake values of 78% and 74%, respectively, of the inhaled vapor concentration.
Comparisons of predicted olfactory tissue concentrations of MAA following simulated exposure of rat, mouse, and human nasal cavities indictated that under identical exposure conditions (including resting physiology in all species), human olfacotry tissue woudl have a 2-3 fold lower concentration of MAA than comparable rodent tissue. Using human phsiology assocaited with light physical activity (workload of 50 W and a minute volume of 20.8 L/min) resulted in a range of values based onthe extent to which humanoral breathing is included in the evaluation (approximately 20% lower tissue concentration in humans with no oral breathing to a 4 fold lower tissue concentration with 80% oral breathing). At a reported average of 40% oral breathing at this workload, the human olfactory tissue concentration would be approximately one-half of the concentration of the comparable rat tissue. The lower tissue concentration predicted for human olfactory tissue relative to rodent tissue would suggest that no adverse histopathological effects would be observed in the human nasal cavity at this exposure level. - Details on distribution in tissues:
- Shake-vial partitioning studies with tissue homogenates indicates that MAA partitions between air and liquid phases and between blood and tissues similarly to acrylic acid. The measured partition coefficients were blood:air (1900), liver:air (6000), kidney:air (3500), fat:air (430), combined nasal tissue:air (1500) and pH 2.0 buffer:air (1310).
- Conclusions:
- Using a valid modeling technique, it is predicted that exposure concentrations for human olfactory tissue relative to rodent tissue would be at least 50 % lower.
- Executive summary:
Using a valid modeling technique, it is predicted that exposure concentrations for human olfactory tissue relative to rodent tissue would be at least 50 % lower.
Referenceopen allclose all
Non-compartmental analysis of the blood concentration data for MAA at the two doses, gives volumes of distribution of 23 ml (10 mg kg-1) and 35 ml (20 mg kg-1). The clearance of MAA was calculated to be 0.324 L hr-1 SRW-1 at the 10 mg kg-1 dose and 0.25 L hr-1 SRW-1 at the 20 mg kg-1 dose. The change in clearance from the lower dose to the higher dose indicates non-linear saturable metabolism in the rat.
Based on that information, the following kinetic parameters were determined from a simultaneous fit of the in vivo data to a one-compartment model with non-linear elimination (Vss = 0.039 L/SRW; Vmax = 19.8 mg/hrxSRW; Km = 20.3 mg/L; SRW: standard rat weight = 250 g) the half-life of MAA in blood was calculated to 1.7 min.
The algorithm of the OECD toolbox has been used to predict GSH/protein reactiviry.
Test Chemical / Compound Identity |
Acronym |
SMILES |
Molecular Weight |
Protein Binding Potency |
2-ethylhexyl methacrylate |
EHMA |
O=C(OCC(CCCC)CC)\C(=C)C |
198.3 |
Slightly reactive (GSH) >> Methacrylates (MA) |
ethyl methacrylate |
EMA |
CCOC(=O)C(=C)C |
114.14 |
Slightly reactive (GSH) >> Methacrylates (MA) |
isobutyl methacrylate |
iBMA |
CC(C)COC(=O)C(=C)C |
142.2 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Methacrylic acid |
MAA |
CC(=C)C(=O)O |
100.12 |
No alert found |
Methyl methacrylate |
MMA |
CC(=C)C(=O)OC |
100.12 |
Slightly reactive (GSH) >> Methacrylates (MA) |
n-butyl methacrylate |
nBMA |
CCCCOC(=O)C(=C)C |
142.2 |
Slightly reactive (GSH) >> Methacrylates (MA) |
n-Hexyl methacrylate |
n-HMA |
CCCCCCOC(=O)C(=C)C |
170.25 |
Slightly reactive (GSH) >> Methacrylates (MA) |
ter-Butyl Methacrylate |
tBMA |
CC(=C)C(=O)OC(C)(C)C |
142.2 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Diethylaminoethyl methacrylate |
DEAEMA |
O=C(OCCN(CC)CC)C(=C)C |
185.263 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2-tert-Butylaminoethyl methacrylate |
TBAEMA |
O=C(OCCNC(C)(C)C)C(=C)C |
185.26 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2-Dimethylaminoethyl methacrylate |
MADAME |
CC(=C)C(=O)OCCN(C)C |
157.22 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2-(2-Butoxyethoxy) ethyl methacrylate, Butyldiglycol methacrylate |
BDGMA |
CCCCOCCOCCOC(=O)C(=C)C |
230.3 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2-(2-(2-Ethoxy ethoxy)-thoxyethyl methacrylate |
ET3EGMA |
O=C(OCCOCCOCCOCC)C(=C)C |
246.3 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2-Methoxyethyl methacrylate |
MTMA |
CC(=C)C(=O)OCCOC |
144.08 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2-Ethoxyethyl methacrylate |
ETMA |
CCOCCOC(=O)C(=C)C |
158.09 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Phenoxyethyl Methacrylate |
PTMA |
CC(=C)C(=O)OCCOC1=CC=CC=C1 |
206.24 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Allyl methacrylate |
AMA |
CC(=C)C(=O)OCC=C |
126.15 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Benzyl methacrylate |
BNMA |
CC(=C)C(=O)OCC1=CC=CC=C1 |
176.21 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Cyclohexyl methacrylate |
c-HMA |
O=C(OC(CCCC1)C1)C(=C)C |
168.23 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Isobornyl methacrylate |
IBOMA |
CC(=C)C(=O)OC1CC2CCC1(C2(C)C)C |
222.32 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Phenyethyl methacrylate |
Phenylethyl MA |
CC(=C)C(=O)OCCC1=CC=CC=C1 |
190.24 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Phenyl methacrylate |
PHMA |
CC(=C)C(=O)OC1=CC=CC=C1 |
162.19 |
Slightly reactive (GSH) >> Methacrylates (MA) |
3,3,5-Trimethylcyclohexyl methacrylate |
TMCHMA |
CC1CC(CC(C1)(C)C)OC(=O)C(=C)C |
210.31 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Tridecyl methacrylate |
TDMA C13MA |
CCCCCCCCCCCCCOC(=O)C(=C)C |
268.43 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Isodecyl methacrylate |
IDMA |
CC(C)CCCCCCCOC(=O)C(=C)C |
226.36 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Dodecyl methacrylate |
LMA |
CCCCCCCCCCCCOC(=O)C(=C)C |
254.41 |
Slightly reactive (GSH) >> Methacrylates (MA) |
n-Octyl methacrylate |
n-OMA |
CCCCCCCCOC(=O)C(=C)C |
198.3 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2-Hydroxyethyl methacrylate |
HEMA |
CC(=C)C(=O)OCCO |
130.1 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Hydroxypropyl methacrylate |
HPMA |
CC(COC(=O)C(=C)C)O |
144.17 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Hydroxypropyl methacrylate |
HPMA |
CC(CO)OC(=O)C(=C)C |
144.17 |
Slightly reactive (GSH) >> Methacrylates (MA) |
N-butoxymethyl methacrylamide |
N-BMMA |
CCCCOCNC(=O)C(=C)C |
157.21 |
Moderately reactive (GSH) >> 2-Vinyl carboxamides (MA) |
N-Methylol methacrylamide |
N-MMAA |
CC(=C)C(=O)NCO |
115.13 |
Moderately reactive (GSH) >> 2-Vinyl carboxamides (MA) |
N,N'-methylenbis(methacrylamide) |
|
O=C(NCNC(=O)\C(=C)C)\C(=C)C |
154.19 |
Moderately reactive (GSH) >> 2-Vinyl carboxamides (MA) |
N-Dimethylaminopropyl methacrylamide |
DMAPMA |
CC(=C)C(=O)NCCCN(C)C |
170.25 |
Moderately reactive (GSH) >> 2-Vinyl carboxamides (MA) |
Methacrylamide |
MAA |
CC(=C)C(=O)N |
85.1 |
Moderately reactive (GSH) >> 2-Vinyl carboxamides (MA) |
1,12-Dodecanediol dimethacrylate |
1,12 DDDMA |
O=C(OCCCCCCCCCCCCOC(=O)\C(=C)C)\C(=C)C |
338.48 |
Slightly reactive (GSH) >> Methacrylates (MA) |
1,3-Butandiol dimethacrylate |
1,3-BDDMA |
CC(CCOC(=O)C(=C)C)OC(=O)C(=C)C |
226.27 |
Slightly reactive (GSH) >> Methacrylates (MA) |
1,4-Butandiol dimethacrylate |
1,4-BDDMA |
CC(=C)C(=O)OCCCCOC(=O)C(=C)C |
226.27 |
Slightly reactive (GSH) >> Methacrylates (MA) |
1,6-Hexanediol dimethacrylate |
1,6 HDDMA |
O=C(OCCCCCCOC(=O)\C(=C)C)\C(=C)C |
254.32 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Ethylene glycol dimethacrylate |
EGDMA |
CC(=C)C(=O)OCCOC(=O)C(=C)C |
198.22 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Trimethylpropane trimethacrylate |
TMPTMA |
CCC(COC(=O)C(=C)C)(COC(=O)C(=C)C)COC(=O)C(=C)C |
338.4 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Ethoxylated bisphenol A dimethacrylate |
2EBADMA |
CC(C)(C1=CC=C(C=C1)O)C2=CC=C(C=C2)O.C=CC(=O)O.C(CO)O |
452.5394 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2,2-bis-[4-(3'-methacryloyloxy-2'-hydroxy)propoxyphenyl] propane |
bis-GMA |
O=C(OCC(O)COc1ccc(cc1)C(c2ccc(OCC(O)COC(=O)\C(=C)C)cc2)(C)C)\C(=C)C |
512.61 |
Slightly reactive (GSH) >> Methacrylates (MA) |
4,4'-Isopropylidenediphenol, oligomeric reaction products with 1-chloro-2,3-epoxy propane, reaction products with methacrylic acid |
Bis-GMA NLP (DSM/Akzo/+others) |
|
n.d |
Slightly reactive (GSH) >> Methacrylates (MA) |
Diethyleneglycol dimethacrylate |
DEGDMA |
CC(=C)C(=O)OCCOCCOC(=O)C(=C)C |
242.27 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Glycerol dimethacrylate |
GDMA |
O=C(OCC(O)COC(=O)\C(=C)C)\C(=C)C |
228.24 |
Slightly reactive (GSH) >> Methacrylates (MA) |
7,7,9-(resp. 7,9,9-)trimethyl-4,13-dioxo-3,14-dioxa-5,12-diazahexadecane-1,16-diol-dimethacrylate |
HEMATMDI |
O=C(OCCOC(=O)NCCC(C)CC(C)(C)CNC(=O)OCCOC(=O)\C(=C)C)\C(=C)C |
470,57 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Triethyleneglycol dimethacrylate |
TREGDMA |
O=C(OCCOCCOCCOC(=O)\C(=C)C)\C(=C)C |
286.32 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Tetraethyleneglycol dimethacrylate |
TTEGDMA/4EDMA |
CC(=C)C(=O)OCCOCCOCCOCCOC(=O)C(=C)C |
198.22 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2-hydroxyethyl methacrylate phosphate |
HEMA phosphate |
CC(=C)C(=O)OCCOP(=O)(O)O |
228.14 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Methacrylic anhydride |
MAAH |
CC(=C)C(=O)OC(=O)C(=C)C |
154.16 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Hydroxyethyl ethylene urea methacrylate |
MEEUW |
O=C1NCCN1CCOC(=O)\C(=C)C |
129.16 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Tetrahydrofurfurylmethacrylat |
THFMA |
O=C(OCC1OCCC1)\C(=C)C |
170.21 |
Slightly reactive (GSH) >> Methacrylates (MA) |
2,2-dimethyl-1,3-dioxolan-4-ylmethyl methacrylate |
|
CC(=C)C(=O)OCC1COC(O1)(C)C |
200.23 |
Slightly reactive (GSH) >> Methacrylates (MA) |
Polyethylengeglycol-200-dimethacrylate |
PEG200DMA |
for approximation see Tetraethyleneglycol dimathacrylate |
no data |
Slightly reactive (GSH) >> Methacrylates (MA) |
2,2,2-Trifluoroethyl methacrylate |
TFMEA 3FM |
CC(=C)C(=O)OCC(F)(F)F |
336 |
Slightly reactive (GSH) >> Methacrylates (MA) |
N-Trimethylammoniumpropyl methacrylamide-chloride |
MAPTAC |
CC(=C)C(=O)NCCC[N+](C)(C)C.[Cl-] |
220.74 |
Moderately reactive (GSH) >> 2-Vinyl carboxamides (MA) |
2-Trimethylammoniummethyl methacrylate-chloride |
TMAEMC |
CC(=C)C(=O)OCC[N+](C)(C)C.[Cl-] |
207.7 |
Slightly reactive (GSH) >> Methacrylates (MA) |
The model output reproduced the published total rat nose deposition data for MAA under unidirectional flow conditions. Comparisons of predicted olfactory tissue concentrations of MAA following simulated exposure of rat, mouse, and human nasal cavities indicated that under identical exposure conditions human olfactory tissue would have a 2 -3 fold lower concentration of MAA than comparable rodent tissue. Conducting the same comparison except using human physiology associated with light physical activity resulted in a range of values based on the extent to which human oral breathing is included in the evaluation. At a reported average of 40% oral breathing at this workload, the human olfactory tissue concentration would be approximately one-half of the concentration of the comparable rat tissue.
Description of key information
MAAH is rapidly hydrolysed to Methacrylic acid (MAA) either by passive physical processes (see chapter "Hydrolysis") and biological processes with the help of
ubiquiteous carboxylase enzymes. Based on studies of the toxicikinetic of methacrylic acid, which thus can be understood as the initial hydrolysis product and primary metabolite of methacrylic anhydride, methacrylic acid is readily absorbed by all routes and rapidly cleared from blood. As indicated by studies with methyl methacrylate(MMA), which functions as metabolite donor substance due to its rapid metablism to MAA, this metabolism is by standard physiological pathways, with the majority of the administered dose being exhaled as CO2.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
It has been demonstrated in a physicochemical hydrolysis study that methacrylic anhydride has a half-life of a few minutes under the conditions of passive hydrolysis. In addition MAAH is stuturally related to an ester which makes it a substrate for carboxylesterase-catalysed hydrolysis in vivo. As methacrylic acid (MAA) thus can be understood as the initial hydrolysis product and primary metabolite of methacrylic anhydride, evaluation of toxicokinetics and fate is primarily based on methacrylic acid. While the properties of the original substance are relevant for local effects (absorption, irritation, sensitisation), systemic effects are most likely the result of the primary metabolite, methacrylic acid.
There are extensive data available for the methyl ester (MMA) which has been reviewed in the EU Risk Assessment (2002). Sufficient data is available to confirm applicability of this data across all members of the category, including MAA, and this has been reviewed in the OECD SIAR (2009). Data on MAA, the common metabolite, has been reviewed in the EU Risk Assessment (2002). The following text relies on these reviews with any addition to the original documents is italicised. Due to the very short half-life of the parent ester in the body and ester hydrolysis being the first step in metabolism, several endpoints in the later parts of the assessment are satisfied by read-across to methyl methacrylate.
Trends/Results
Taken from the EU Risk Assessment on MAA: “Deposition of methacrylic acid vapours in the surgically isolated upper respiratory tract (URT) of anaesthetised rats was studied after inhalation of 450μg/l (133 ppm) using a unidirectional respiratory flow technique (cyclic flow studies were not possible due to vapour absorption on the cyclic flow pump) for 60 min (Morris and Frederick, 1995). Deposition of methacrylic acid was measured throughout exposure determining the difference in vapour concentration of methacrylic acid in the inspired and the URT expiring air. Deposition rates (from 30 to 60 min of exposure) of about 95% were observed under 200 ml/min unidirectional flow conditions. However, the degree of penetration to underlying cells could not be derived from this experiment. ”
Further from the EU Risk Assessment on MAA: “After a single oral administration of the sodium salt of methacrylic acid to Wistar rats (540 mg/kg bw) methacrylic acid was detected in the blood serum by means of HPLC. The maximum concentration was found after 10 min, whereas after 60 min no more methacrylic acid was detectable (Bereznowski et al., 1994).
As taken from the OECD SIAR: “Methacrylic acid and the corresponding alcohol are subsequently cleared predominantly via the liver (valine pathway and the TCA (TriCarboxylic Acid) cycle, respectively).”As methyl methacrylate (MMA) is rapidly degraded in the body to MAA, it can thus be understood as metabolite donor for MAA, with MAA as common metabolite of MAAH and MMA
Methacrylate esters can conjugate with glutathione (GSH) in vitro, although they show a low reactivity, since the addition of a nucleophile at the double bond is hindered by the alpha-methyl side-group (McCarthy & Witz, 1991). For MAA, by analogy with acrylic acid and its esters, it can be predicted that the free carboxyl group will reduce the already low reactivity of methacrylates with GSH even further, so that GSH conjugation will only play an insignificant role in MAA metabolism, and then possibly only when very high tissue concentrations are achieved. Morris (1992) did not find any effect on GSH concentrations in URT tissues up to inhaled MAA concentrations of 410 ppm, a concentration which causes tissue damage in the URT in inhalation experiments.
Table: Summary of the results for the peak rates of absorption of MMA through rat & human epidermis
|
Rat epidermis |
Human epidermis |
||||
Ester |
Peak rate of absorption (μg/cm²/hr) ±SEM |
Period of peak absorption rate (hours) |
% age of applied dose absorbed over x hours |
Peak rate of absorption (μg/cm²/hr) ±SEM |
Period of peak absorption rate (hours) |
% age of applied dose absorbed over x hours |
MAA |
23825±2839 |
0.5-4 |
93% / 24h |
812 |
- |
- |
MMA |
5888±223 |
2-8 |
46% / 16h |
453±44.5 |
4-24 |
10% / 24h |
Key: The values in normal type were obtained experimentally, whilst those in italics, are predicted values based on statistical analysis (single exponential fit) of the experimental data
Studies completed after the EU ESR on MAA indicate rapid absorption through skin and subsequent clearance from blood. Topically applied MAA absorbs rapidly through intact rat epidermis and viable whole skin in-vitro (Jones, 2002). In another study intravenous injection of MAA in rats demonstrated very rapid clearance from the blood (half-life <5mins), suggestive of rapid subsequent metabolism (Jones, 2002).
A comparison of measured blood concentration data after i. v. administration of 10 and 20 mg/kg MAA and a simulation based on a one-compartment model shows good agreement. Based on that information, the following kinetic parameters were determined from a simultaneous fit of the in vivo data to a one-compartment model with non-linear elimination (Vss = 0.039 L/SRW; Vmax = 19.8 mg/hr x SRW; Km = 20.3 mg/L; SRW: standard rat weight = 250 g) the half-life of MAA in blood was calculated to 1.7 min.
For methacrylic anhydride no in vivo absorption data exist. The rate of dermal absorption has been calculated with a human skin model (Heylings, 2012).
Chemical Class |
Test Chemical / Compound Identity |
Acronym |
Molecular Weight |
Log P |
Predicted Flux (µg/cm2/h) |
Relative Dermal Absorption |
Alkyl basic MA tier 1 |
Methyl methacrylate |
MMA |
100.12 |
1.38 |
64.422 |
Moderate |
Multi-func hydrophil spec / single |
Methacrylic anhydride |
MAAH |
154.16 |
1.23 |
0.019 |
Minimal |
In comparison, the predicted absorption rate for MAAH is substantially lower than that of the reference chemical methyl methacrylate in the same model. In relation, the predicted absorption rate for MMA is lower than the epidermal permeation rate shown above but is consistent with the only slightly lower absorption rate for human whole skin (33 µg/cm²/h) predicted from the experimental, epidermal data in the study by Jones(2002).
Conclusions
MAA is absorbed by all routes, while the actual absorption rates may be lower than for the reference chemicals methacrylic acid and methyl methacrylate. Due to the short half-life MAAH is rapidly converted to methacrylaic acid which, in turn, is rapidly cleared from blood and, as indicated by studies with MMA, this metabolism is by standard physiological pathways, with the majority of the administered dose being exhaled as CO2.
Local effects at the site of contact due to MAAH, but also because of the irritating/corrosive properties of MAA.
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