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EC number: 202-784-1 | CAS number: 99-75-2
- 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
Reported oral LD50 values are 3300 mg/kg bw in rats, and 3800 mg/kg bw in mice. An ester mixture with 26 % submission substance showed an oral LD50 of 2987 mg/kg bw in rats.
For the inhalation route the LC50 in rats was above 0.49 mg/L, the highest concentration tested. A lethal concentration (40-60 % mortality) of 0.040-0.070 mg/L was reported in mice.
No mortality was observed after dermal exposure of rabbits to 5000 mg/kg bw. Therefore the LD50 is above 5000 mg/kg bw.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 3 300 mg/kg bw
- Quality of whole database:
- Results are formally RL4 as secondary source of an unavailable report, but the submitters of report to US EPA considered the results as reliable: "Data reported in a brief memo with limited description of protocol and results.Data were collected prior to GLP and OECD guidelines but by a method comparable to present guidelines/standards and under direction of a recognized research institute. Even though details are not available, the data are considered reliable." Further studies of low reliability support the findings of the selected study.
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Quality of whole database:
- The two available studies were considered to be not reliable
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 5 000 mg/kg bw
- Quality of whole database:
- The available study is formally RL4 as secondary source of an unavailable report, but the submitters of report to US EPA considered the results as reliable: "Data reported in a brief memo with limited description of protocol and results.Data were collected prior to GLP and OECD guidelines but by a method comparable to present guidelines/standards and under direction of a recognized research institute. Even though details are not available, the data are considered reliable."
Additional information
Oral:
Reported oral LD50 values are 3300 mg/kg bw in rats (US EPA HPV, 2001, RL4), and 3800 mg/kg bw in mice (IUCLID, 2000; RL4). An ester mixture with 26 % submission substance showed an oral LD50 of 2987 mg/kg bw in rats (Haskell, 1981; RL3).
The submitters of the report to the EPA considered the LD50 of 3300 mg/kg bw as reliable (formally it would be RL4). All values are clearly above 2000 mg/kg bw, the upper boundary for classification as acute toxic substance after oral exposure. Therefore no classification for acute oral toxicity is necessary.
Inhalation:
The available information is not reliable: Hoechst (1982) reported no mortality at a concentration of 0.49 mg/L. The study is reliable with respect to conceptual design and documentation, but the exposure concentration is too low for definite conclusions on classification.
The other information from secondary source only is a lethal concentration in mice (40 -60 % mortality) of 0.04 -0.070 mg/L. No details are provided. This is in clear contrast to the result of the well-performed study by Hoechst (1982), where no mortality was observed in rats at a 7 -12 fold higher concentration. A species-specific sensitivity difference of this magnitude is not plausible. Therefore, the effects in mice are disregarded.
Dermal:
The available study were rabbits were exposed topically to the test item reported no mortality at a dermal exposure of 5000 mg/kg bw (US EPA HPV, 2001). Though formally as secondary source not assignable, the result was considered to be reliable by the submitters of the report to the US EPA. Therefore no classification for acute dermal toxicity is necessary.
Justification for selection of acute toxicity – oral endpoint
Though formally (as secondary source) not assignable, the study is regarded as reliable in this secondary source
Justification for selection of acute toxicity – dermal endpoint
Though formally (as secondary source) not assignable, the study is regarded as reliable in this secondary source
Justification for classification or non-classification
Based on the available information, the submission substance has not to be classified with respect to oral and dermal exposure (CLP (Regulation (EC) No 1272/2008) and DSD-DPD (Council Directive 67/548/EEC)). No reliable data are available for inhalation exposure.
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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