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Diss Factsheets
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EC number: 201-297-1 | CAS number: 80-62-6
- 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
Biodegradation in soil
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in soil
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Remarks:
- GLP, similar to OECD-guideline, analytical monitoring.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: EPA, title 40 Code of Federal Regulations Part 160 (1983, 1989)
- GLP compliance:
- yes
- Test type:
- laboratory
- Specific details on test material used for the study:
- - Radiochemical purity: HPLC (on day of application): 85.4 % (radiolabelled test substance)
- Methacrylic acid was presented as an impurity in the applied methyl methacrylate and was detected in the zerotime soil extracts. - Radiolabelling:
- yes
- Oxygen conditions:
- aerobic
- Soil no.:
- #1
- Soil type:
- sandy loam
- % Clay:
- 16
- % Silt:
- 30
- % Sand:
- 54
- % Org. C:
- 3.2
- pH:
- 7.7
- CEC:
- 22.2 meq/100 g soil d.w.
- Parameter followed for biodegradation estimation:
- radiochem. meas.
- Soil No.:
- #1
- Temp.:
- 25 °C
- Humidity:
- 17.3 other: % by weight
- Details on experimental conditions:
- The metabolism of 14C-methyl methacrylate in a Milton sandy loam soil has been studied after application under aerobic conditions after application of 100 and 1000 mg MMA/l dry weight. Soil samples were incubated in the dark at ca. 25 degree C.
- Soil No.:
- #1
- % Degr.:
- > 99
- Parameter:
- radiochem. meas.
- Sampling time:
- 2 d
- Soil No.:
- #1
- DT50:
- < 1 d
- Type:
- (pseudo-)first order (= half-life)
- Transformation products:
- yes
- No.:
- #1
- No.:
- #2
- Evaporation of parent compound:
- yes
- Volatile metabolites:
- yes
- Details on results:
- Already after 2 days < 1 % of the radioactivity was presented as MMA in soil extracts, at either rate of application. About 60 - 70 % of the radioactivity was lost due to evaporation of the parent compound at both concentration levels. Of the total volatiles measured, 28.2 (low level) and 15.7 (high MMA level) of applied compound over the 28-day study period was accounted to CO2 emissions. The indications are that MMA is rapidly lost from soil either by evaporation or degradation. The estimated half-life for methyl methacrylate in soil was less than one day at both concentration levels.
- Executive summary:
The aerobic degradation of 14C-methyl methacrylate after application to a Milton sandy loam soil has been studied at two application rates (100 and 1000 mg/kg dry weight soil). After application at either rate,
methyl methacrylate was rapidly lost from the soil by a combination of evaporative and degradative processes. The estimated half-life for methyl methacrylate in soil was less than one day.
Volatile radioactivity, other than that characterised as 14C02 , was assumed to be associated with the parent compound. Although the study was designed to minimise evaporation of methyl methacrylate, it was still
expected to be significant in view of the highly volatile nature of the compound. After application at 100 and 1000 mg/kg, evaporation of unchanged methyl methacrylate was estimated to account for about 60%
and 70 % of the applied radioactivity respectively. Almost all of this evaporation occurred during the first day after application.
Mineralisation to 14CO2 accounted for 28% of the 100 mg/kg application and 16% of the 1000 mg/kg application after 28 days. Production of 14C02 occurred mostly during the first three days after
application and was more rapid (in terms of % applied radioactivity) after application at 100 mg/kg.
Degradation to non-volatile, non-extractable material accounted for about 5 % of the low level application and 2 % of the high level application after 28 days.
Methacrylic acid was present as an impurity in the applied methyl methacrylate and was detected in the zerotime soil extracts. Tue proportion of methacrylic acid in soil declined rapidly suggesting that it also was degraded or volatilised.
- Endpoint:
- biodegradation in soil: simulation testing
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because the substance is readily biodegradable
Referenceopen allclose all
Description of key information
Key value for chemical safety assessment
Additional information
In a guideline study in accordance to U.S.-EPA already after 2 days < 1 % of the radioactivity was left as methyl methacrylate in soil extracts, at either rate of application. About 60 - 70 % of the radioactivity was lost due to evaporation of the parent compound at both concentration levels. Of the total volatiles measured, 28.2 (low level) and 15.7 (high methyl methacrylate level) of applied compound over the 28-day study period was accounted to CO2 emissions. The indications are that methyl methacrylate is rapidly lost from soil either by evaporation or degradation. The estimated half-life for methyl methacrylate in soil was less than one day at both concentration levels. In addition, the test substance shows low adsorptive properties (log Koc 1.1) and is readily biodegradable.
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