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EC number: 204-112-2 | CAS number: 115-86-6
- 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
Acute toxicity after oral and dermal administration of triphenyl phosphate is very low. Acute oral administration in rats, mice, rabbits and guinea pigs produced LD50 values in a range of 3000 mg/kg body weight to above 20000 mg/kg body weight. After dermal application an LD50 >7900 mg/kg body weight was established in rabbits. No valid studies are available regarding inhalation exposure to TPP. A number of studies are available using other routes of exposure such as subcutaneous, intraperitoneal and intramuscular injections which confirm the low level acute toxicity of triphenyl phosphate.
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Short report. Main features of study design given. Also assessed by OECD.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Principles of method if other than guideline:
- Similar to limit test but higher dose is used.
- GLP compliance:
- not specified
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Wistar derived
- Weight at study initiation: 200-300 grams
- Fasting period before study: 24hours
- Housing: mesh bottom cages
- Diet (e.g. ad libitum): Available after dosage
Water (e.g. ad libitum): Available after dosage
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on oral exposure:
- VEHICLE
- Concentration in vehicle: 25% in aqueous solution - Doses:
- Single dose of 20,000 mg/kg of the test material.
- No. of animals per sex per dose:
- 5 males, 5 females (10).
- Control animals:
- no
- Details on study design:
- Ten young adult albino rats weighing between 200-300 grams equally distributed into five males and five females were housed in mesh-bottom cages and fasted 24 hours prior to administrating a single dose of 20,000 mg/kg of the test material. Food and water were available ad libitum after dosage. The animals were observed daily for 14 days following adminsitration of the test material and deaths were recorded.
- Preliminary study:
- No mortality was observed at the dosage level of 20,000 mg/kg of body weight. Gross examination at autopsy revealed sporadic visceral hemorrhage.
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 20 000 mg/kg bw
- Mortality:
- None
- Clinical signs:
- other: No information on clinical signs.
- Gross pathology:
- Gross examination at autopsy revleaed sporadic visceral hemorrhage.
- Interpretation of results:
- not classified
- Conclusions:
- The approximate acute oral LD50 for TPP in rats is >20,000 mg/kg of body weight.
- Executive summary:
In an acute oral toxicity test in rats, ten young adult albino rats weighing between 200-300 grams equally distributed into five males and five females were housed in mesh-bottom cages and fasted 24 hours prior to administrating a single dose of 20,000 mg/kg of the test material TPP (in 25% aqueous solution). The dose was administered via intragastric intubation. Food and water were available ad libitum after dosage. The animals were observed daily for 14 days following administration of the test material and deaths were recorded. No mortality was observed at the administered dose. Gross examination at autopsy revealed sporadic visceral hemorrhage. The approximate acute oral LD50 obtained for the test material TPP is >20,000 mg/kg of body weight.
Reference
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 3 000 mg/kg bw
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Short report, few details. Also assessed by OECD
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Principles of method if other than guideline:
- Method: other: as described in 16 CFR 1500.40
- GLP compliance:
- not specified
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rabbit
- Strain:
- other: Albino
- Sex:
- not specified
- Type of coverage:
- not specified
- Vehicle:
- not specified
- Details on dermal exposure:
- This study was conducted according to US Federal Hazardous Substances Act Regulations study guideline 16 CFR 1500.40. 5 rabbits were tested with intact skin and 5 with abraded skin. Observation period of 14 days.
- Doses:
- 10000 mg/kg
- No. of animals per sex per dose:
- 10
- Sex:
- not specified
- Dose descriptor:
- LD50
- Effect level:
- > 10 000 mg/kg bw
- Mortality:
- None
- Clinical signs:
- other: No data
- Gross pathology:
- No data
- Interpretation of results:
- not classified
- Conclusions:
- Dermal LD50 is > 10,000 mg/kg body weight.
- Executive summary:
2 groups of 5 albino rabbits were treated each with a dose of 10 000 mg/kg body weight on either intact or abraded skin. No adverse effects nor mortality were observed during 14 -days post-exposure. The LD50 is >10,000 mg/kg body weight.
Reference
MORTALITY: none
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 7 900 mg/kg bw
Additional information
Non-guideline toxicity studies were performed mainly in rats and hens, but mice, rabbits, cats and guinea pigs were also used. Nevertheless, the acute toxicity could be evaluated from the available evidence.
There are also a number of studies using subcutaneous, intraperitoneal and intramuscular injections. The studies considered valid confirm the low level of toxicity. These routes of administration are not considered relevant for triphenyl phosphate exposure in man and are therefore not included in the overall chemical assessment. The data available on toxicity via oral dermal routes is sufficient (rated 2) and is listed in table.
Study Type | Species | Endpoint | Exposure | Result | Reference |
Acute oral | Rat | LD50 | single; dose level 20000 mg/kg bw | >20000 mg/kg bw | Mackellar DG, 1976 |
Acute oral | Rat | LD50 | single; maximum dose level 15800 mg/kg bw | 10800 mg/kg bw | Johannsen FR et al., 1977 |
Acute oral | Rat | LD50 | single; dose levels 2500 - 5000 mg/kg bw | >5000 mg/kg bw | Ciba-Geigy, 1954 |
Acute oral | Mouse | LD50 | single; dose levels 2500 - 5000 mg/kg bw | >5000 mg/kg bw | Ciba-Geigy, 1954 |
Acute oral | Guinea pig | LD0 | single; dose levels 3000 -4000 mg/kg bw | >4000 mg/kg bw | Sutton WL et al., 1960 |
Acute oral | Hen | Neurotoxicity | single; undiluted, dose level 1000 mg/kg bw | No signs of neurotoxicity; >1000 mg/kg bw | Hine CH et al., 1956 |
Acute oral | Hen | Neurotoxicity | single; dose level 500 mg/kg bw in arachis oil | No signs of neurotoxicity; >500 mg/kg bw | Aldridge WN et al., 1961 |
Acute oral | Hen | Neurotoxicity | single; dose level 30g/kg in olive oil as gelatine capsules | No signs of neurotoxicity; >10000 mg/kg bw | Henschler D et al., 1958 |
Acute oral | Hen | LD0 | single; dose level 5000 mg/kg bw in gelatine capsules | >5000 mg/kg bw | Johannsen FR et al., 1977 |
Acute oral | Hen | NOEL | single; dose level 2, 3, 5, 8, 12.5 g/kg in arachis oil | > 12500 mg/kg bw | Ciba-Geigy, 1980 |
Acute oral | Hen | NOEL | single; dose level 12000 mg/kg bw | > 12000 mg/kg bw | Ciba-Geigy, 1981 |
Dermal | Rabbit | LD50 | single; dose level 10000 mg/kg bw | >10000 mg/kg bw | Mackellar DG, 1976 |
Dermal | Rabbit | LD50 | sinlge; dose level 7900 mg/kg bw | >7900 mg/kg bw | Johannsen FR et al., 1977 |
Justification for classification or non-classification
The level of acute toxicity after oral and dermal administration is low and the LD50 values suggest that no classification is required for these routes of exposure.
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