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EC number: 275-156-8 | CAS number: 71048-82-3
- 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
Acute oral toxicity in mice: LD50 is 1400 mg/kg bw in an OECD 401
Acute dermal toxicity: LD50 => 1400 mg/kg bw based on the acute oral LD50. The dermal availability is not expected to exceed the oral availability. Therefore the LD50 via the dermal route can be estimated to be lower than the oral LD50, because we assume 10% absorption via the dermal route and 50% absorption via the oral route.
Acute inhalation toxicity: LC50 value of 14000 mg/m³ was calculated for acute inhalation toxicity exceeding the saturated vapour concentration of 215 mg/m³.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 1 400 mg/kg bw
- Quality of whole database:
- The available information is adequate for the dossier.
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
Additional information
Acute oral toxicity:
The oral acute toxicity of the test substance was evaluated in mice, performed similar to OECD Guideline 401, predating GLP. Five albino mice per sex per dose were administered the substance orally as a corn oil solution at a constant volume of 20 mL/kg bw at the following concentrations: 940, 1346, 1475, 1600, 1902, 2025, 2150, 2225, 2350, 2692 mg/kg bw. Animals were observed for 14 days following administration of the test material. Toxic effects and mortality were recorded throughout the duration of the test period. Clinical signs included: decrease of activity, ataxia, salivation, urinary incontinence, tremors. Mortality was observed at all dose levels (except at 1346 mg/kg bw). Macroscopic changes were evident in the lungs, spleen, kidneys, G.I. tract and stomach. The LD50's for males, females and the two sexes combined were calculated using the Litchfield-Wilcoxon method: males 1400 mg/kg bw; females 1850 mg/kg bw; combined 1625 mg/kg bw.
Acute inhalation toxicity
An acute inhalation toxicity study is not needed for substances for which acute oral and dermal toxicity values are available. Using route to route extrapolation the inhalation toxicity can be derived as follows: Incorporated dose = concentration x respiratory volume x exposure time: 1 mg/kg bw = 0.0052 mg/L/4h.Using a respiratory volume for a 250 g rat of 0.20 L/min and 100 % absorption and postulating 1 100% deposition and absorption (Guidance on IR/CSA, Chapter R7C, Table R.7.12-10). The LD50 was 1400 mg/kg bw for mice and therefore the LC50 is circa 14000 mg/m³ (using similar parameters for rat and mice). The maximum saturated vapour concentration for the substance is (2.72 x 192297 MW (mg/mol)) / (8.3 (R, gas constant) x 293 (°K)) = 215 mg/m³. This means that delta-damascone cannot reach a concentration higher than 215 mg/m³. Therefore the calculated LC50 for inhalation (14000 m³) cannot be reached and no classification and labelling is needed for the acute inhalation route.
Acute dermal toxicity based on acute oral LD50
The study is scientifically unjustified because the acute dermal toxicity can be derived from the acute oral toxicity using route to route extrapolation. Based on the toxico-kinetic information (see IUCLID section 7.1) the dermal availability is not expected to exceed the oral availability. Therefore we can make a worst case assumption that the LD50 via the dermal route can be estimated to be similar as or higher than the oral LD50. We assume 10% absorption via the dermal route and 50% absorption via the oral route. Based on this information it can be concluded that the performance of an acute dermal toxicity study will not add useful information on the hazard, the classification and labelling and the risk characterisation of the substance for workers and consumers. The information is thought to be sufficient to show that testing on vertebrate animals for acute dermal toxicity can be omitted, in accordance with Annex XI (1.2)
Justification for classification or non-classification
Based on an oral LD50 in mice of 1400 mg/kg bw, Delta-damascone has to be classified for Acute toxicity Cat 4:H302: Harmful if swallowed according to EU Classification, Labeling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008.
Based on an oral LD50 in mice of 1400 mg/kg bw, and the estimated dermal absorption of 10% compared to 50% absorption via the oral route, delta-Damascone does not need to be classified for acute oral toxicity according to EU Classification, Labeling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008.
The calculated inhalation LC50 of 14000 mg/m3 cannot be reached because the maximum saturated vapour pressure is 215 mg/m³, classification for acute inhalation is not warranted in accordance with EU Classification, Labeling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008.
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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