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Diss Factsheets
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EC number: 400-830-7 | CAS number: 104810-48-2 EVERSORB 80; TINUVIN 1130; TINUVIN 213
- 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)
Description of key information
Short description of key information on bioaccumulation potential result:
Toxicokinetic and metabolism data using phenolic ring-U-14C-labelled test material is available for the analogue methyl ester. No bioaccumulation potential is derived from this data.
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
Additional information
This mixture is surface-active and the more insoluble diester components are dispersed via the monoesters and free PEG 300.
A representative monoester and diester component with n=6 (PEG monomer) were synthesized to allow determination of water solubility and log POW. For the monoester component, water solubility was 1.7 mg/L and log POWwas 5.9 (HPLC-method). For the diester component, water solubility is less than 0.2 mg/L and log POWis 4.6 (HPLC-method).
The log POW values are above four and might give rise of concern for bioaccumulation. However, esters are susceptible to enzymatic hydrolysis. In this case, experimental data is available for the analogue methylester (CAS 84268-33-7). Toxicokinetic and metabolism data using phenolic ring-U-14C-labelled test material is available for the analogue methyl ester (RCC project no. 904098, reported 1992 and Ciba-Geigy project no CB 91/02, reported 1991). The methylester is of lower molecular weight and may therefore be more easily cleaved than the ester group in the test item. However, the data shows that in principle this ester bond is susceptible to enzymatic hydrolysis. For the methyl ester, most radioactivity was excreted with the feces within the first 24 hours, whereas 4- 5 % were eliminated in the urine. Elimination was efficient and almost complete after 168 hours. In vitro studies with the analogue methylester showed that both 1 % rat serum and 1.25 % rat liver homogenate readily hydrolyzed the ester bond at neutral pH with hydrolysis half-times of 14 and 37 minutes, respectively. Slower turnover was observed with small intestine homogenate.
Systemic uptake and an adaptive response of the liver are obvious from the repeated-dose toxicity studies and the mechanistic investigations with the substance itself. Peroxisome proliferation was demonstrated. Effects on liver were reversible during the four-week recovery period of the subchronic toxicity study (CIT 1988).
Peroxisome proliferation was also reported for the methyl ester and for 3-[3-tert-butyl-5-(2H-benzotriazol-2-yl)-4-hydroxyphenyl]propionic acid itself (Ciba-Geigy 1989).
Based on the reversibility of liver effects and ester hydrolysis, the substance is not expected to have a potential for bioaccumulation.
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