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EC number: 214-987-2 | CAS number: 1241-94-7
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1 June 1980 - 20 March 1981
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was conducted under GLP conditions and according to methods equivalent to those outlined in OECD guideline 414. The treatment period of the study was GD6-15, which is not in accordance with the current guideline (prescribes exposure during the entire gestation period). Due to this limitation and the limited reporting of foetal abnormalities, the study report was assigned a Klimisch 2 rating.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 981
- Report date:
- 1981
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 2-ethylhexyl diphenyl phosphate
- EC Number:
- 214-987-2
- EC Name:
- 2-ethylhexyl diphenyl phosphate
- Cas Number:
- 1241-94-7
- Molecular formula:
- C20H27O4P
- IUPAC Name:
- 2-ethylhexyl diphenyl phosphate
- Details on test material:
- - Name of test material (as cited in study report): Santicizer 141
- Physical state: Liquid
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: COBS CD
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: The Charles River Breeding Laboratories, Inc., Portage, Michigan
- Age at study initiation: 16 weeks (at time of mating)
- Weight at study initiation: 273-276 g (mean weights per group on gestation day 0)
- Housing: Individually, under standard laboratory conditions
- Diet (e.g. ad libitum): Ad libitum, rodent chow
- Water (e.g. ad libitum): Ad libitum, tap water
- Acclimation period: 42 days
ENVIRONMENTAL CONDITIONS
Animals were maintained in a temperature-, humidity-, and light-controlled environment, with a photoperiod (hrs dark / hrs light) of 12/12.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Test article was dispensed daily and administered orally undiluted at total dosage volumes of 0.275, 0.917 and 2.750 ml/kg. The control group received 2.750 ml/kg distilled water. - Analytical verification of doses or concentrations:
- no
- Details on analytical verification of doses or concentrations:
- No data
- Details on mating procedure:
- - Impregnation procedure: cohoused
- M/F ratio per cage: 1:1
- Verification of same strain and source of both sexes: yes
- Proof of pregnancy: vaginal plug or sperm in vaginal smear referred to as day 0 of pregnancy - Duration of treatment / exposure:
- 10 days (GD6-15)
- Frequency of treatment:
- Daily
- Duration of test:
- Approximately one month
- No. of animals per sex per dose:
- 25 (female)
- Control animals:
- yes
- Details on study design:
- - Dose selection rationale: No data
- Rationale for animal assignment: Block design
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Daily
- Cage side observations: Mortality and overt changes in appearance and behavior
BODY WEIGHT: Yes
- Time schedule: On GD 0, 6, 9, 12, 16 and 20
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day #20
- Examinations: Abdominal and thoracic cavities and organs for gross evident morphological changes. Tissues were preserved for microscopic esamination when deemed necessary by gross findings. - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: No
- Number of viable fetuses: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes - Fetal examinations:
- - External examinations: Yes: all per litter
- Soft tissue examinations: Yes: half per litter
- Skeletal examinations: Yes: half per litter - Statistics:
- - Chi-square test with Yates' correction for 2x2 contingency tables and/or Fisher's exact probability test
- Mann-Whitney U-test
- Bartlett's test for homogeneity of variances and the appropriate t-test using Dunnett's multiple comparison tables - Indices:
- Not relevant
- Historical control data:
- Available at the testing facility
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- not specified
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
No mortality was observd. Body weight (gain) was decreased for the mid (primarily caused by 3 animals) and high dose (caused by all animals) group during the treatment period, but this finding was not significant.
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 3 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: developmental toxicity
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
No biologically meaningful or statistically significant teratogenic or developmental effects were noted in any of the treatment groups.
Effect levels (fetuses)
- Remarks on result:
- other: information not available
- Remarks:
- information not available
Fetal abnormalities
- Abnormalities:
- not specified
- Description (incidence and severity):
- information not available
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
RESULTS OF TEST | DOSING GROUPS | |||
Control | Low (300 mg/kg bw/day) | Medium (1000 mg/kg bw/day) | High (3000 mg/kg bw/day) | |
MATERNAL TOXIC EFFECTS BY DOSE LEVEL | ||||
Number of animals | 25 | 25 | 25 | 25 |
Mortality | x | x | x | x |
Clinical signs | x | Increase in hair loss | Increase in hair loss, yellow staining and/or matting on the ventral, anogenital and/or inguinal areas | Increase in hair loss, yellow staining and/or matting on the ventral, anogenital and/or inguinal areas, fissuring on primarily the inguinal area and dry red matter on the forelimbs and/or head |
Body weight | x | x | x | Mean weight loss during first 6 days of treatment |
Body weight gain | x | x | Slightly reduced over the entire treatment period (GD6-15), primarily caused by 3 of the dams | Severe reduction over entire treatment period |
Number pregnant per dose level | 19 | 22 | 21 | 21 |
Number that delivered | 0 | 0 | 0 | 1 |
Number of corpora lutea (mean per dam) | 16.1 | 16.5 | 15.7 | 16.1 |
Number of implantations (mean per dam) | 13.4 | 14.6 | 13.6 | 14.0 |
Post-implantation loss (mean per dam) | 0.8 | 0.6 | 0.8 | 0.8 |
Number of resorptions (early, mean per dam) | 0.8 | 0.6 | 0.6 | 0.8 |
Number of resorptions (late, mean per dam) | 0 | 0 | 0 | 0 |
Duration of pregnancy | Caesarian section on GD20 | Caesarian section on GD20 | Caesarian section on GD20 | Caesarian section on GD20 (one female with delivery on GD20) |
Number of litters | 19 | 22 | 21 | 21 |
FETAL DATA (preferably per litter) | ||||
Litter size (mean per dam) | 12.6 | 14.0 | 12.8 | 13.2 |
Number viable (mean per dam) | 12.6 | 14.0 | 12.8 | 13.2 |
Sex ratio (M/F) | 1:1.14 | 1:0.96 | 1:1.04 | 1:0.85 |
Litter weights (mean per dam) | 3.6 | 3.7 | 3.8 | 3.7 |
Grossly external abnormalities | x | x | Increase in number of fetuses with malformations (not dose-related) | Increase in number of fetuses with malformations (not dose-related) |
Visceral abnormalities | x | x | x | x |
Skeletal abnormalities | x | Increase in number fetuses with 14th rudimentary ribs and sternebrae #5 and/or #6 unossified (in range of historical control) | Increase in number fetuses with 14th rudimentary ribs and sternebrae #5 and/or #6 unossified (in range of historical control) | Increase in number fetuses with 14th rudimentary ribs and sternebrae #5 and/or #6 unossified (in range of historical control) |
x = no treatment related effects (as compared to control group) |
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of this study, no developmental effects were observed as a result of treatment with Santicizer 141 from GD6-15. A severe (but not significant) reduction in body weight gain was noted in dams during treatment. Based on these results, a NOAEL of 3000 and 1000 mg/kg bw/day was established for developmental and maternal toxicity, respectively.
- Executive summary:
This study was performed according to methods equivalent to those outlined in OECD guideline 414 (prenatal developmental toxicity study). Dams were exposure to Santicizer 141 during GD6-15, which is not in line with the current guideline that prescribes exposure throughout the entire gestation period. Mortality, clinical signs and body weight of the dams were recorded and several teratogenic parameters and malformations were evaluated.
No mortality was observed. Body weight (gain) was decreased for the mid and high dose group during the treatment period, but this change was not significant. No biologically meaningful or statistically significant teratogenic effects or malformations were noted in any of the treatment groups.
Under the conditions of this study, no teratogenic or developmental effects were observed as a result of treatment with Santicizer 141. A severe (but not significant) reduction in body weight gain was noted in dams during treatment. Based on these results, a NOAEL of 3000 and 1000 mg/kg bw/day was established for developmental and maternal toxicity, respectively.
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