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EC number: 229-175-3 | CAS number: 6422-83-9
- 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
Hydrolysis:
- OECD gudieline 111 study, GLP, moderate to fast hydrolysis in dependence of pH
Biodegradation:
- OECD guideline 301B study, GLP: not readily biodegradable, degradation was not > 60% within a 10-day window after achieving 10% degradation (day 14: 8% degradation ; day 28: 17 % degradation).
Transport and distribution
- Adsorption/desorption: log Koc(estimated from logKow): 0.8743 at 25°C, log Koc (estimated from MCI): 2:7051 at 25°C, QSAR estimation using EPISuiteTM Software/ KOCWIN v.2.00.
- Henry´s Law constant: 1.39E-11 Pa-m³/mol at 25°C, value obtainbed from the SRC database, the reported values are based on a QSAR prediction performed with anadequate QSAR model.
Additional information
Hydrolysis:
In a study conducted according to OECD guideline 111 (2004), 30 mg/L of the test substance 2,4 -Bismaleimidotoluene were dissolved in three buffers, pH 4, 7 and 9 and incubated at different temperatures (5, 10, 20, 30, and 50°C). The test item showed a moderate hydrolysis rate (2.4 h ≤ t1/2 ≤ 30 d) for pH 4 at 20 and 30 °C as well as for pH 7 at 20 °C and a fast hydrolysis rate (t1/2 ≤ 2.4 h) for the remaining test conditions (pH 4 at 50 °C, pH 7 at 30 and 50 °C as well as for pH 9 at 5, 10 and 20°C), with the higher half-lives at acidic conditions. Major transformation products were observed at all pH values and temperatures.
Biodegradation:
The test item was not readily biodegradable under the conditions of the Modified Sturm Test presently performed. Degradation failed to reach 60% within a 10-day window after achieving 10% degradation (day 14: 8% degradation ; day 28: 17 % degradation).
Adsorption/desorption:
According to the available data obtained from QSAR estimation, the soil sorption coefficient Koc for the test item was determined to be in the range between 7.487 L/kg and 507.1 L/kg and 95. According to the classification of Blume & Ahlsdorf, 2,4 -Bismaleimidotoluene can be regarded as a substance with either low or high binding strength to organic matter of soil and sediments based on these results. However, currently there is no defined, universally accepted applicability domain but according to the model description estimation of loc Koc from log Kow is more reliable due to interim measured log Kow from training set substances which substantiates the applicability of the model used. However, due to missing information about the applicability of the model with respect to the substance under investigation the results and the conclusions thereoff should be treated with care.
Henry´s Law constant:
The value obtained from the SRC database is based on a QSAR prediction performed. The QSAR prediction was made using EPISuiteTM HenryWin (model) and revealed a value of 1.39E-11 Pa-m³/mol at 25°C.
References: Blume, H. P., & Ahlsdorf, B. (1993). Prediction of pesticide behavior in soil by means of simple field tests.Ecotoxicology and environmental safety,26(3), 313-332.
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