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EC number: 202-830-0 | CAS number: 100-21-0
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Justification for type of information:
- Please refer to Section 13.2 for full read-across justification
Data source
Reference
- Reference Type:
- publication
- Title:
- Perinatal exposure to the phthalates DEHP, BBP, and DINP, but not DEP, DMP, or DOTP, alters sexual differentiation of the male rat
- Author:
- Gray LE, Ostby J, Furr J, Price M, Veeramachaneni DNR & Parks L
- Year:
- 2 000
- Bibliographic source:
- Toxicol Sci. 58(2):350-65
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- Assessment of the sexual development of male rat offspring following perinatal exposure
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- Dioctylterephthalate (DOTP / DEHT)
- IUPAC Name:
- Dioctylterephthalate (DOTP / DEHT)
- Reference substance name:
- Bis(2-ethylhexyl) terephthalate
- EC Number:
- 229-176-9
- EC Name:
- Bis(2-ethylhexyl) terephthalate
- Cas Number:
- 6422-86-2
- Molecular formula:
- C24H38O4
- IUPAC Name:
- bis(2-ethylhexyl) terephthalate
- Reference substance name:
- Bis(2-ethylhexyl) benzene-1,4-dicarboxylate
- IUPAC Name:
- Bis(2-ethylhexyl) benzene-1,4-dicarboxylate
- Details on test material:
- 98% purity; obtained from Aldrich
Constituent 1
Constituent 2
Constituent 3
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS- Source: Charles River, NC, USA- Age at study initiation: 90 days- Weight at study initiation: Not stated- Fasting period before study: Not stated- Housing: Individual, in polycarbonate cages with pine shavings (maternal)- Diet: Purina Rat Chow (5001), ad libitum- Water: Filtered Tap Water, ad libitum- Acclimation period: Time-mated rats were received at GD 2ENVIRONMENTAL CONDITIONS- Temperature (°C): 20-24- Humidity (%): 40-50- Air changes (per hr): Not reported- Photoperiod (hrs dark / hrs light): 14/10
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- Time-mated female rats were gavaged with the phthalate esters di(2-ethylhexyl) phthalate (DEHP), benzyl butyl phthalate (BBP), diisononyl phthalate (DINP), diethyl phthalate (DEP), dimethyl phthalate (DMP) or dioctyl terephthalate (DOTP / DEHT) were administered by oral gavage to maternal female rats at a dose level of 750 mg/kg bw from Gestation Day 14 to Postnatal Day 3.
- Analytical verification of doses or concentrations:
- not specified
- Details on mating procedure:
- 90-day old nulliparous females were time-mated overnight (mating confirmed by sperm-positive smear)
- Duration of treatment / exposure:
- Gestation Day 14 to Postnatal Day 3.
- Frequency of treatment:
- Daily
- Duration of test:
- Male offspring were necropsied at 3-5 or 4-7 months of age
Doses / concentrations
- Dose / conc.:
- 750 mg/kg bw/day
- No. of animals per sex per dose:
- 8 (DOTP)19 (control)
- Control animals:
- yes, concurrent vehicle
Examinations
- Maternal examinations:
- Signs of toxicity, bodyweights.
- Ovaries and uterine content:
- Not applicable - dams were allowed to litter normally
- Fetal examinations:
- Not applicable - dams were allowed to litter normally
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Treatment with DEHP and DNIP resulted in slight reductions in weight gain; mean maternal bodyweights were not significantly different to controls. Weight gain to PND3 was significantly reduced in DEHP-treated females.
Maternal developmental toxicity
- Number of abortions:
- no effects observed
- Details on maternal toxic effects:
- Maternal toxic effects:yesDetails on maternal toxic effects:There were no treatment-related deaths or overt signs of toxicity. Treatment with DEHP and DNIP resulted in slight reductions in weight gain; mean maternal bodyweights were not significantly different to controls. Weight gain to PND3 was significantly reduced in DEHP-treated females. All dams were pregnant and delivered live offspring.
Results (fetuses)
- Reduction in number of live offspring:
- effects observed, treatment-related
- Description (incidence and severity):
- The litter from one dam treated with BBP did not survive to PND 2; a further BBP-treated dam did not have any male pups at weaning.
- External malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- Treatment with DINP, DEHP and BBP was shown to induce malformations in male offspring (84%, 92% and 7% incidence, respectively). Findings included retained nipple, cleft phallus, undescended testes, hypospadias and vaginal pouch; affected offspring often showed multiple malformations. Some males treated with DEHP or BBP showed complete agenesis of the prostate, seminal vesicles, bulbourethral and/or coagulating glands
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- Anogenital distance in male pups was significantly reduced in BBP- and DEHP-treated groups. The reduction in AGD (~30%) was associated with reduced pup weight (~15%); anogenital index was not assessed. Male offspring from these groups also showed a significant (~35%) reduction in testis weight. At PND 8-9, males from the DEHP-treated group showed an increased incidence of haemorrhagic testes; a similar finding was seen in one male from the DINP-treated group. Histopathology of the testes from male offspring in the DEHP-treated group showed focal interstitial haemorrhage, granulomas (associated with focal haemorrhage) or infarcted areas (associated with more widespread haemorrhage and coagulative necrosis. Treatment with BBP, DEHP and DINP significantly induced areolae in male offspring.
Males from the DINP-, DEHP- and BBP-treated groups showed small testes, unilateral or bilateral testicular agenesis. Testes were flaccid, fluid-filled and devoid of sperm. Weights of the reproductive organs/tissues were significantly reduced in males from the DEHP- and BBP-treated groups.
Reduced mating behaviour was seen in DEHP-treated rats. - Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:not examined
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
The litter from one dam treated with BBP did not survive to PND 2; a further BBP-treated dam did not have any male pups at weaning.
Litter size was comparable in all groups. Pup weights were significantly lower in the DEHP- and BBP-treated groups.
Anogenital distance in male pups was significantly reduced in BBP- and DEHP-treated groups. The reduction in AGD (~30%) was associated with reduced pup weight (~15%); anogenital index was not assessed. Male offspring from these groups also showed a significant (~35%) reduction in testis weight. At PND 8-9, males from the DEHP-treated group showed an increased incidence of haemorrhagic testes; a similar finding was seen in one male from the DINP-treated group. Histopathology of the testes from male offspring in the DEHP-treated group showed focal interstitial haemorrhage, granulomas (associated with focal haemorrhage) or infarcted areas (associated with more widespread haemorrhage and coagulative necrosis. Treatment with BBP, DEHP and DINP significantly induced areolae in male offspring. Mean age at puberty (preputial separation) was not affected by treatment in any group, with the exception of extremely malformed males in the BBP- and DEHP-treated groups. Treatment with DINP, DEHP and BBP was shown to induce malformations in male offspring (84%, 92% and 7% incidence, respectively). Findings included retained nipple, cleft phallus, undescended testes, hypospadias and vaginal pouch; affected offspring often showed multiple malformations. Some males treated with DEHP or BBP showed complete agenesis of the prostate, seminal vesicles, bulbourethral and/or coagulating glands. Males from the DINP-, DEHP- and BBP-treated groups showed small testes, unilateral or bilateral testicular agenesis. Testes were flaccid, fluid-filled and devoid of sperm. Weights of the reproductive organs/tissues were significantly reduced in males from the DEHP- and BBP-treated groups; bodyweights and non-reproductive organ weights were not affected by treatment. Reduced mating behaviour was seen in DEHP-treated rats.
Applicant's summary and conclusion
- Conclusions:
- As dioctyl terephthalate (DOTP / DEHT) is shown to be rapidly hydrolysed to terephthalic acid, it can also be concluded that terephthalic acid will similarly not affect the sexual differentiation of male rats.
- Executive summary:
In this study, the authors examined a number of phthalate esters to determine any effects on the sexual differentiation of male rat offspring due to anti-androgenic properties. The substances di(2-ethylhexyl) phthalate (DEHP), benzyl butyl phthalate (BBP), diisononyl phthalate (DINP), diethyl phthalate (DEP), dimethyl phthalate (DMP) or dioctyl terephthalate (DOTP / DEHT) were administered by oral gavage to maternal female rats at a dose level of 750 mg/kg bw from Gestation Day 14 to Postnatal Day 3. None of the substances tested caused overt maternal toxicity or reduced litter size. Dams administered DEHP showed reduced maternal weight gain over the dosing period by about 15 g; DEHP and DINP reduced gestation weight gain by 24 g and 14 g, respectively. Treatment with DEHP and BBP treatments reduced pup weight at birth (15%). Male pups from dams treated with DEHP and BBP showed reduced (~30%) anogenital distance and reduced (~35%) testis weight. A high proportion of male offspring of dams administered DEHP, BBP and DINP displayed feminine areolas/nipples (87%, 70% and 22%, respectively). A significant incidence of reproductive malformations was also apparent in male offspring of these groups (82%, 84% and 7.7%, respectively. Perinatal maternal exposure to the phthalate esters DEHP, BBP and DINP was therefore shown to alter the sexual differentiation of male offspring, suggesting an anti-androgenic mode of action. Similar effects were not seen with the phthalate esters DOTP, DEP and DMP. DEHP and BBP were shown to be of approximately equivalent potency; DINP exhibited potency an order of magnitude lower.
As dioctyl terephthalate (DOTP / DEHT) is shown to be rapidly hydrolysed to terephthalic acid, it can also be concluded that terephthalic acid will similarly not affect the sexual differentiation of male rats.
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