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EC number: 278-355-8 | CAS number: 75980-60-8
- 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
Additional information
There are no studies available for the determination of toxicokinetics or dermal absorption.
Diphenyl(2,4,6 -trimethylbenzoyl)phosphine oxide is a powder with a molecular weight of 348 g/mol and a very low vapour pressure of 3x10e6Pa at 20 °C. In agreement with its logPow of 3.1, only 12mg can be dissolved in one liter of water. Due to its low vapour pressure, exposure to vapor is unlikely. The combination of a molecular weight below 500g/mol and moderate lipophilicity (logPoW between 1 and 4) favor oral as well as dermal uptake. Though acute dermal and oral toxicity tests did not show signs of systemic toxicity, sensitization was observed, hinting to dermal uptake of at least small amounts. In several repeated dose oral toxicity studies damage of testes, liver and kidneys was observed. From the logPoW below 4 it is expected, that the substance does not bioaccumulate. This is confirmed by the repeated dose studies. For the 28day and 90day study almost the same doses were used, which showed well-comparable effects, independent of exposure time. For example, the mid dose of 250mg/kg (28day) or 300mg/kg (90day) showed increased liver and kidney weights, that worsened to partly histopathologically confirmed organ damage in the high dose group in both studies. Testes atrophy was detected in the high dose of both groups and in the mid dose in rats treated for 90days. Reduced testes size was palpable after 7 weeks in this dose group, which is after the 4 week time frame in the sub-acute study. Since testes damage was observed app. 2 -3 weeks after signs of liver and kidney damage were detected, this effect might require functional impairment of metabolism and excretion. In any case, the strong effects on liver and kidney suggest good oral uptake, metabolism in the liver and excretion via urine.
No mutagenicity or chromosomal aberration was observed (Ames, HPRT, CA), so no reactivity with macromolecules is expected prior to excretion.
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