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EC number: 241-753-7 | CAS number: 17772-51-9
- 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
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
There are no experimental toxicokinetic data available for the substance and this statement is based on available data as physico-chemical data and toxicological data. This assumption follows the procedure indicated in the “Guidance on information requirements and chemical safety assessment chapter R.7c” of the ECHA guidance document (version 1.1, November 2012).
Available physico-chemical information taken into account:
Physical state:
The substance is a solid.
Particle size distribution:
According to OECD guideline 110, the particle size distribution of 3-Hydroxy-2-(3-hydroxy-2-quinolinyl)-1H-inden-1-one was determined by scanning electron microscopy method for the sieved fraction (< 100 µm, 7.40% of total sample) and presented on the basis of calculated mass fractions. The median diameter was 3.12 µm with the main fraction of 67.1% distributing in the range of 4 - 10 µm.
Molecular weight:
289 g/mol
Water solubility:
Determined by the column elution method at 20 °C was <0.000026 g/L.
Log Pow:
4.8 at 25°C.
Vapor pressure:
The QSAR determination of the vapour pressure of 3-hydroxy-2-(3-hydroxy-2-quinolyl)-1H-inden-1-one using the model MPBPWIN included in the Estimation Program Interface (EPI) Suite v4.11 revealed a value of 3.45E-11 Pa at 25 °C.
Estimation of oral absorption:
Oral absorption is considered to be low, based on the physico-chemical data: molecular weight 289 g/mol, insoluble in water, log Pow above 4.
There is no evidence of absorption of 3-hydroxy-2-(3-hydroxy-2-quinolyl)-1H-inden-1-one in an acute oral study and in an oral 28 day study.
In an acute oral toxicity study no deaths, no clinical signs and no gross pathological findings were reported after dosing of 5 male and 5 female rats with 5000 mg/kg.
Oral administration of 3-hydroxy-2-(3-hydroxy-2-quinolyl)-1H-inden-1-one to Wistar rats at doses of 100, 300 and 1000 mg/kg/day for 28 days resulted in no changes of toxicological relevance. The orange discoloration of the feces noted in all treated groups represents a typical finding in gavage studies with colored substances or dyestuffs.
Although the slight increase in the incidence of dark yellow urine implies that a minimal absorption cannot be excluded, no discoloration was noted in any organ and there were no correlating macroscopical or microscopical findings.
Based on the results of this study, the no-observed-effect-level (NOEL) and no-observed-adverse-effect-level (NOAEL) were considered to be 1000 mg/kg body weight/day of 3-hydroxy-2-(3-hydroxy-2-quinolyl)-1H-inden-1-one, the highest dose tested.
Overall: oral absorption is assumed to be low based on physicochemical properties and oral toxicity experiments.
Estimation of dermal absorption:
Dermal absorption is likely to be low because it is a solid with a molecular mass above 100, insoluble in water and a log Pow value above 4.
There is no evidence of absorption of 3-hydroxy-2-(3-hydroxy-2-quinolyl)-1H-inden-1-one in acute dermal study. In this study 5 male and 5 female rats received a single semiocclusive dermal dose of 2000 mg/kg of the test item for 24 hours. Rats tolerated the dose without toxicologically relevant clinical signs, mortalities, toxicological effects on body weight development and gross pathological findings.
Overall: dermal absorption is assumed to be low based on physicochemical properties and acute dermal toxicity data.
Estimation of absorption via inhalation:
The calculated vapor pressure is anticipated to be low; 3.45E-11 Pa at 25 °C. In humans, particles with aerodynamic diameters below 100 μm have the potential to be inhaled. The fraction of particles below 100 µm was reported to be only 7.4 % of total sample.
Consistent with the large, not inhalable, particle size of the compound, an acute inhalation toxicity study was aborted before any animal was exposed to the compound based on the low maximal technical producible concentration that could be achieved.
Overall: absorption by inhalation is assumed to be low based on physicochemical properties.
Overall estimation on absorption: absorption is anticipated to be similar and very low by oral, dermal and inhalation route.
Estimation of distribution:
Based on the high log Pow (4.8) and the insolubility in water it is not likely that the substance distributes into cells. This assumption is supported by the oral sub-acute toxicity study in which no relevant absorption or adverse effects were observed and the limit dose 1000 mg/kg/day.
Estimation of accumulation:
Poorly water soluble particles have the potential to accumulate in the lung. Based on the particle size distribution only 7.4% of the sample have a MMAD < 100 µm. Overall, the particle size distribution is not in favor of substantial accumulation.
Estimation of metabolism:
In vitro genotoxicity data do not indicate any genotoxic metabolites. The substance is negative in the absence and in the presence of S9 extracts (Ames test, in-vitro micronucleus test and gene mutation assay in mammalian cells (HPRT)).
Estimation of excretion:
Based on the low absorption potential of the compound excretion is anticipated mainly (exclusively) via the feces; this is supported by the sub-acute toxicity study.
Oral administration of 3-hydroxy-2-(3-hydroxy-2-quinolyl)-1H-inden-1-one to Wistar rats at doses of 100, 300 and 1000 mg/kg/day for 28 days resulted in no changes of toxicological relevance. The orange discoloration of the feces noted in all treated groups represents a typical finding in gavage studies with colored substances or dyestuffs.
Although the slight increase in the incidence of dark yellow urine implies that a minimal absorption cannot be excluded, no discoloration was noted in any organ and there were no correlating macroscopical or microscopical findings.
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