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Diss Factsheets
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EC number: 700-990-0 | 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
Key value for chemical safety assessment
Additional information
- Water solubility – 3.2 mg/L
- Molecular weight – 382 g/mol
- Log Kow – 4.68
- Vapour pressure - 0.00108 Pa (20°C)
No studies on toxicokinetics are available for tBuTPP. The available toxicity studies provide no or little information. Therefore the assessment is primarily based on physicochemical properties, supported by some toxicological indications.
Physical/chemical properties
The physical/chemical properties that are of importance to assess the toxicokinetics behaviour of tBuTPP are:
Absorption
Based on log Kow, t-BuTPP is relatively highly lipophilic and therefore oral/GI-absorption by passive diffusion is expected to be limited. Reasonably micellular solubilisation will be the major mechanism for absorption, also because it has a low water solubility and a moderate low molecular weight. Oral acute toxicity studies indicate some visible adversal effects in GI-tract, adrenals, testes and lungs. This indicate that absorption has occurred, although it gives no indication of the amount of absorbed substance.
Due to the low vapour pressure of tBuTPP, respiratory exposure is unlikely to occur on a large scale. However, when respiratory exposure has occurred, absorption will be similar to oral absorption.
Because of its highly lipophilic character the dermal penetration of t-BuTPP into the stratum corneum will be high. Because of its low water solubility the rate of penetration from the stratum corneum into the epidermis is likely to be low. This would be supported by the outcome of the skin sensitization study (LLNA), in which the SI was >3 in all concentrations tested, however, no dose-response was observed. One theoretical explanation might be that the majority of the dermal applied substance stays in the local stratum corneum and only a small fraction has been absorbed into the epidermis.
Distribution, metabolism and excretion
Based on the physical chemical properties the substance will be distributed into cells and to a lower extent into the extracellular spaces. Since it’s highly lipophilic character it is anticipated that it tends to be accumulated in adipose tissues and in lipophilic layers like the stratum corneum. In one study (SE Hastings, Sauerhoff, 1981) a significantly higher concentration of phosphates was found in the urine of exposed animals. This was theoretically clarified by excretion of metabolites. There is no indication of metabolism rate and excretion rates.
Conclusion:
T-BUTPP can be absorbed after oral and respiratory exposure, but the amount of absorption cannot be predicted. Dermal absorption is considered to be very low, but accumulation in the stratum corneum is expected. No information is available about the distribution, metabolism and excretion.
For risk assessment purposes, absorption via the oral and inhalation route are assumed to be similar, based on the absence of effects in 90-day studies via both routes. For dermal absorption, it was assumed as a worst-case that absorption was similar to oral absorption.
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