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EC number: 232-480-4 | CAS number: 8050-28-0
- 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
Ecotoxicological Summary
Administrative data
Hazard for aquatic organisms
Freshwater
- Hazard assessment conclusion:
- PNEC aqua (freshwater)
- PNEC value:
- 0.005 mg/L
- Assessment factor:
- 1 000
- Extrapolation method:
- assessment factor
- PNEC freshwater (intermittent releases):
- 0.048 mg/L
Marine water
- Hazard assessment conclusion:
- PNEC aqua (marine water)
- PNEC value:
- 0 mg/L
- Assessment factor:
- 10 000
- Extrapolation method:
- assessment factor
STP
- Hazard assessment conclusion:
- PNEC STP
- PNEC value:
- 3.2 mg/L
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
Sediment (freshwater)
- Hazard assessment conclusion:
- PNEC sediment (freshwater)
- PNEC value:
- 865.47 mg/kg sediment dw
- Extrapolation method:
- equilibrium partitioning method
Sediment (marine water)
- Hazard assessment conclusion:
- PNEC sediment (marine water)
- PNEC value:
- 86.55 mg/kg sediment dw
- Extrapolation method:
- equilibrium partitioning method
Hazard for air
Air
- Hazard assessment conclusion:
- no hazard identified
Hazard for terrestrial organisms
Soil
- Hazard assessment conclusion:
- PNEC soil
- PNEC value:
- 172.55 mg/kg soil dw
- Extrapolation method:
- equilibrium partitioning method
Hazard for predators
Secondary poisoning
- Hazard assessment conclusion:
- no potential to cause toxic effects if accumulated (in higher organisms) via the food chain
Additional information
Acute studies are available for fish, Daphnia and algae for various members of this category. Differences have been observed between substances reacted with fumaric acid and substance reacted with maleic anhydride when tested in ecotoxicological studies. Therefore, read across between fumarated and maleated substances has not been conducted for ecotoxicity endpoints.
Environmental classification is assessed based on data for the substance itself, where available, or using read across from another fumarated or maleated substance where data on the substance itself is not available.
However, PNECs have been derived based on pooled data, with one set of PNECs derived to cover all maleated substances within the category and one set to cover all fumarated substances. The most sensitive result for any maleated rosin substance has been used as the key value for PNEC derivation.
Conclusion on classification
The available ecotoxicity results indicate that there may be differences in environmental toxicity between substances reacted with fumaric acid and substances reacted with maleic anhydride, although the reasons for this are not clear. Therefore, although maleated and fumarated substances are structurally similar and it is appropriate for these substances to be considered within a single category, for ecotoxicity endpoints read across is not conducted between fumarated and maleated substances.
The ecotoxicity of maleated substances is affected by the solubility of the test item, with more soluble substances rosin, maleated and resin acids and rosin acids, maleated sodium salts showing higher aquatic toxicity compared to the poorly soluble substance resin acids and rosin acids, maleated calcium salts. Therefore, ecotoxicity endpoints and environmental classification of resin acids and rosin acids, maleated calcium salts are completed based on data for the substance itself rather than using read across from more rosin, maleated or resin acids and rosin acids, maleated sodium salts.
Environmental classification of each of the maleated rosin substances is outlined below.
Rosin, maleated
Two acute Daphnia studies and one acute fish study are available for rosin, maleated. The lowest EC50 value for this substance is 9.3 mg/L. As this result is >1 mg/L an acute environmental classification is not appropriate for this substance. However, a chronic category 2 classification is assigned to this substance as it is not readily biodegradable and has an EC50 value between 1 and 10 mg/L.
Resin acids and rosin acids, maleated sodium salts
Acute fish,Daphniamagnaand algal studies are available for resin acids and rosin acids, maleated, sodium salts. The lowest EC50 from these studies is 4.8 mg/L, for fish. As this result is >1 mg/L an acute environmental classification is not appropriate for this substance. However, a Chronic category 2 classification is assigned to this substance as it is not considered to be readily biodegradable and has an EC50 value between 1 and 10 mg/L.
Resin acids and rosin acids, maleated calcium salts
Acute fish, Daphnia magna and algal studies are available for resin acids and rosin acids, maleated, calcium salts. EL50 values from these studies are all >100 mg/L. However, as this substance is of low solubility, is not readily biodegradable and has a log Kow value of >4 a "safety net" classification of Chronic Category 4 is assigned to resin acids and rosin acids, maleated, calcium salts.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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