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EC number: 204-211-0 | CAS number: 117-81-7
- 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
In experimental animals, DEHP exhibits low acute oral, dermal and inhalation toxicity.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- discriminating dose
- Value:
- 20 000 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- discriminating conc.
- Value:
- 10 620 mg/m³ air
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 19 800 mg/kg bw
Additional information
Acute oral toxicity
In rats:
Acute oral toxicity of DEHP in the rat has been estimated as a prerequisite to a carcinogenicity study by NTP (1982). Doses from 800 to 20,000 mg/kg of DEHP (99.5% pure) were administered in a single dose by gavage to groups consisting of 5 males and 5 females. The vehicle was corn oil. No deaths were observed during a 14-day observation period, giving an LD0 in excess of 20,000 mg/kg. No individual animal data are given.
Berman (1995) evaluated the acute oral toxicity of DEHP (>99% pure) in rats according to a protocol similar to the OECD N°425 guideline. Groups of 7-15 female Fischer 344 rats were given a single oral dose of DEHP at doses of 0, 150, 500, 1500, 5000 mg/kg and were then observed daily for 7 days. No mortality at the highest dose tested (5000 mg/kg). The oral LD0 of DEHP is higher than 5000 mg/kg in female Fischer 344 rats.
Groups of six male Sprague Dawley rats were administered single oral doses of Diethylhexylphthalate (DEHP) at 2000 mg/kg in 2% gum acacia and were observed clinically for seven days (Chu et al., 1981). No mortality and clinical signs were observed. Body weight and food consumption were not affected by treatment. The liver weight increased in the treated group. Hepatic microsomal aniline oxidase activity was not altered by treatment. The acute oral LD0 is higher than 2000 mg/kg in rats.
In mice:
Acute oral toxicity of DEHP in mice has also been estimated as a prerequisite to a carcinogenicity study by NTP (1982). Doses from 800 to 20,000 mg/kg of DEHP (99.5% pure) were administered as a single dose by gavage to groups consisting of 5 males and 5 females. The vehicle was corn oil. No deaths were observed during a 14-day observation period, thereby giving an LD0 value higher than 20,000 mg/kg. No individual animal data are given in the report.
Acute inhalation toxicity
In a study performed according to GLP principles, groups of 5 male and 5 female rats were exposed for 4 hours to clean air (control group) or DEHP (purity not specified) in concentrations of either 3.39, 6.82, or 10.62 mg/litre (3,390, 6,280, or 10,620 mg/m3) (Greenough, 1981). The highest dose was considered the technical limit of aerosol generation for the test material. The control group and the lowest dose group were exposed on the same day. The mid-dose group and the highest dose group were exposed on different days. The exposure was nose-only. The rats were observed for clinical signs throughout the exposure period and for the first 4 hours after dosing. During the subsequent 14-day observation period the rats were inspected twice daily. Body weights were measured before exposure and with regular intervals during the observation period. A detailed macroscopic examination was performed on all animals at sacrifice at the end of the observation period. No animals died during or after the exposure. All treated animals showed a slightly unkempt appearance for 1-2 days after exposure, those in the highest dose group had a yellowish staining on their fur. This group also had a reduced body weight gain on the second day after exposure, which subsequently returned to the normal pattern. In all groups, dark red foci and patches were observed in the lungs at post mortem inspection. These findings were more frequent in the treated animals. In conclusion, the LC0 of DEHP via inhalation was in this study found to be in excess of 10,620 mg/m3 for 4 hours.
Acute dermal toxicity
The acute dermal toxicity of DEHP has not been investigated in a study of guideline quality. In an older study, rabbits were exposed dermally for 24 hours with doses up to 20 ml/kg (Shaffer et al., 1945). That amount killed 2 of 6 rabbits. The LD50 by skin absorption is ca. 20 ml/kg (19800 mg/kg bw). However, details of the experimental design and original results are not presented in the report.
Justification for classification or non-classification
According to the criteria edicted in REGULATION (EC) No 1272/2008 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 16 December 2008, no classification is warranted for the acute toxicity.
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