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EC number: 946-682-1 | CAS number: -
- 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
This toxicokinetic study (OECD 417) in Sprague-Dawley rats revealed:
- a low bioavailability, no accumulation and an inter-individual difference.
- C12-C12 and C9-C12 only detected in GI tract. C9-C9 detected in several tissues of almost all animals and absorbed into circulation to some degree.
- rapid elimination and metabolization in the digestive tract of rats.
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
Additional information
In accordance with the section 8.8.1 of Annex VIII in REGULATION (EC) No 1272/2008, the toxicokinetic profile of the substance (i.e. absorption, distribution, metabolism and elimination) was derived from the relevant available data. A toxicokinetic study (OECD 417) in Sprague-Dawley rats has been performed and described below.
Toxicokinetic study (OECD 417, 2019, iPhase Biosciences, K, RS)
ADME properties of the test substance (CAS: 2166089-27-4), dodecanoic acid mixed diesters with dipropylene glycol and nonanoic acid was tested in the Sprague-Dawley rats based on OECD guideline 417. Bio-analytical methods (LC-MS/MS) were developed and validated to determine the test substance in biological samples of SD rats. Potential metabolites of the test substance were identified using full ion scanning mode. A total of nine experimental groups (Groups #1~9) were designed in thein vivostudies as follows: a single intravenous dose group (#1), a low single oral dose group combined with initial exposure (#2), a high single oral dose group (#3), a trough repeated oral dose group (#4), a repeated oral dose group with last exposure (#5), a feces and urine excretion group (#6), a biliary excretion group (#7), a tissue distribution group (#8) and a gastrointestinal residual group (#9). In addition, threein vitrostudies were conducted on the test item, including plasma protein binding test, liver microsomal metabolism test, and recombinant CYP 450 enzymes metabolism test.
The test substance is composed of three components of C12 -C12 at 26.43%, C9 -C12 at 50.82%and C9 -C9 at 22.75%. In rats administrated intravenously with the test substance, the Apparent Volume of Distribution (Vz) of C12 -C12 was 0.24±0.040 L/kg, and the elimination half-life(t1/2z) of C12 -C12 was 1.02±0.18 h. C9 -C12 in plasma was also rapidly eliminated in rats. After single-dose oral exposure tothe test substance, only a small amount of C12 -C12 was absorbed into the blood. C9 -C12 was barely absorbed into circulation, and C9 -C9 was absorbed into the circulation. After single-dose oral exposure of the test substance, the 72-h cumulative excretion of C12-C12 and C9-C12 in feces only accounted for 3.88% and 1.04% of the dose administrated, and the percentage of C12 -C12 and C9 -C12 at 0.5 h was only 15.92% and 13.62% of the dose administrated, indicating that C12 -C12 and C9 -C12 were rapidly eliminated in the digestive tract. Results of in vitro studies showed that C12 -C12 and C9 -C12 were not metabolized by liver microsomes and recombinant CYP450 enzymes. C12 -C12 and C9 -C12 was almost completely bound to plasma protein with binding rate of 100%. The test substance was rapidly metabolized in the digestive tract of rats. As metabolites found in this study varied greatly in molecular weights via different administration routes, it is speculated that the diester bond of the test substance is easily broken into fragments, and new esters will be formed in the digestive tract and body by binding to fatty acids of various carbon chain lengths.
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