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EC number: 421-820-9 | CAS number: 192268-65-8 CD 28-0132; IRGALUBE 232
- 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
The substance is considered to be very persistent in the environment
Additional information
Based on biodegradation screening and simulation tests, the substance is considered to be persistent in the environment. The substance to register was found to be poorly biodegradable in a Closed bottle test according to OECD guideline 301D (Huntington 1996). In addition, several biodegradation data are available for the main component Triphenyl thiophosphate (structure A). 17.8 and 19.3% mineralization (CO2 evolution) was observed in 28 days in a modified Sturm test (OECD 301B). Further investigations during experimental phase using radiolabelled test item showed that only 51.5% and 60.8% of the radioactivity consisted of the test item, whereas the remaining radioactivity consisted of its degradation products. Thus, the test item is not completely biodegraded over a 28-day period under the test conditions but up to 19% is mineralized and additionally up to 48.5% of the test item is transformed into its transformation and degradation products. Phenol can be identified from the chromatogram of the degradation products. This is supported by the results of the hydrolysis study, which showed that different transformation products of the test substances are generated in parallel once hydrolysis has started. The results indicate that the test item cannot be classified readily biodegradable but well primarily degradable under conditions of the test. An inherent biodegradability test with Structure A according to OECD 302C confirmed this result. The test material showed up to 59.5 and 66.8 % biodegradation after 28 days. These results indicate that the test item can be degraded if sufficient degrading microorganisms are available; however, this is not necessarily be the case in surface water. A study investigating the biodegradation of O,O,O-triphenyl phosphorothioate under environmental conditions according to GLP and OECD guideline 309 using radiolabelled test material showed only very low mineralization of 3.1 – 3.7%. No organic volatiles were detected (≤ 0.1 % AR). The amount of parent after 61 days was in the range of 80.2 % to 90.5 % AR. The DT50 value is determined to be > 61 days. Reason for the low degradation are assumed to be low microorganism concentrations and adsorption of the components to DOC which might lower bioavailability of the substances to microorganisms.
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