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EC number: 265-512-0 | CAS number: 65140-91-2
- 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:
- 1982 - 1983
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study performed under GLP-like quality control. No data on purity were available. Dosing was performed from day 6 to 15 of gestation only.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 983
- Report date:
- 1983
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Version / remarks:
- (adopted 1983)
- Deviations:
- no
- GLP compliance:
- no
- Remarks:
- but QAU statement included
- Limit test:
- no
Test material
- Reference substance name:
- Calcium diethyl bis[[[3,5-bis(1,1-dimethylethyl)-4-hydroxyphenyl]methyl]phosphonate]
- EC Number:
- 265-512-0
- EC Name:
- Calcium diethyl bis[[[3,5-bis(1,1-dimethylethyl)-4-hydroxyphenyl]methyl]phosphonate]
- Cas Number:
- 65140-91-2
- Molecular formula:
- C17 H29 O4 P. 1/2Ca
- IUPAC Name:
- calcium diethyl bis[[[3,5-bis(1,1-dimethylethyl)-4-hydroxyphenyl]methyl]phosphonate]
- Details on test material:
- Physical appearance: solid
Storage conditions: room temperature
Purity: no data
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: Sprague-Dawley derived Tif:RAIf (SPF) rats
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: closed breeding colony, Ciba-Geigy WST
- Age at study initiation: 2 months
- Weight at study initiation: 180-200 g
- Housing: 5 per cage in Makrolon cages
- Diet: NAFAG No. 890, ad libitum
- Water: ad libitum
- Acclimation period: day 0 to day 6 post coitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21+/-2
- Humidity (%): 55+/-10
- Photoperiod: 12 hrs dark / 12 hrs light
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Remarks:
- 0.5%
- Details on exposure:
- The suspension of the test material was freshly prepared daily by homogenization and stirring (magnetic stirrer), and administered at a rate of 10 mL/kg of body weight.
- Details on mating procedure:
- The females were mated overnight with males of proven fertility in the ratio of 1 male / 3 females. The day on which spermatozoa were found in the vaginal smear or a vaginal plug was observed, was designated as day 0 of pregnancy.
- Duration of treatment / exposure:
- Day 6 to day 15 of pregnancy
- Frequency of treatment:
- Once daily.
- Duration of test:
- until day 21 of gestation
Doses / concentrations
- Remarks:
- Doses / Concentrations:
400, 1200, 2400 mg/kg bw/day
Basis:
actual ingested
- No. of animals per sex per dose:
- 25 pregnant rats
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale:
Doses were based on results of a preliminary study, where 10 rats were dosed with vehicle or 2000 mg/kg bw test substance. The dams of the experimental group (2000 mg/kg bw) reacted to the treatment by some reduction in body-weight gain and food intake in comparison with the vehicle control. Concerning the progeny, no abnormalities were revealed by the external examination; the average weight of the foetuses of the 2000 mg/kg bw dose group was not significantly diminished in comparison with the vehicle control (Student's t test, one-tailed, observed p < 0.01).
Examinations
- Maternal examinations:
- During the period of treatment, general bodily condition, weight gain and symptoms were checked daily. Food consumption was noted on days 6,
1 1 , 16 and 21 of pregnancy. The average body weight gain of the females was determined on the basis of the actual body weight as well as that on the first day of treatment and at the time of necropsy, corrected by subtracting the weight of the gravid uterus. - Ovaries and uterine content:
- Investigation of ovaries and uterus: mucosa and contents, including amniotic fluid and placentae as well as abortions and resorption sites.
- Fetal examinations:
- - Sex determination
- Careful external inspection
- Weighing
- Examination of the viscera according to the slicing technique of WILSON (J.G. Wilson and J. Warkany, eds.. The University of Chicago Press, Chicago and London, 1965, pp. 265-277). One third of the live foetuses per litter were fixed in a mixture of ethyl alcohol and formaldehyde solution to which acetic acid had been added.
- Skeletal assessment in two thirds of the foetuses per litter following clearing in potassium hydroxyde and staining with alizarine red S was carried out.
- Uterine horns showing no evident implantation sites were placed into a solution of ammonium sulfide to visualize possible haemorrhagic alterations in such sites. - Statistics:
- The numbers of embryonic and/or foetal deaths (resorptions) (Chi*-test, Yates' correction, observed p > 0.01).
The male to female ratios of the foetuses (Chi* -test, Yates' correction, observed p > 0.05). - Historical control data:
- Spontaneous data characteristic of the breed of rats used in the present study refer to a series of untreated controls ("historical" or cumulative control) observed over a period of 69 months (listed in the study report).
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Details on maternal toxic effects:
Body-weight gain was comparable for the dams of all groups. Food consumption of the experimental groups, however, showed some reduction during the treatment period (from day 6 of pregnancy) in comparison with the vehicle control. Female No. 32 (400 mg/kg) died on day 6 in consequence of an intubation error. Females No. 4 (vehicle control) and No. 78 (2400 mg/kg) delivered "spontaneously" (i.e. shortly before sacrifice on day 21 p.c.) and were not taken into further consideration of data. Signs of inflammation of the liver were found in one female of the vehicle control.
The rates of implantation sites per female were comparable for all groups. The numbers of embryonic and/or foetal deaths (resorptions) were not increased at either dose. The male to female ratios of the foetuses were also comparable for all groups (Chi* -test, Yates' correction, observed p > 0.05).
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 2 400 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- NOAEL
- Effect level:
- 2 400 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: developmental toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
In comparison with the vehicle control, the average body-weight of the live foetuses was not diminished at either dose. A slight but significant increase was noted for the live foetuses of the intermediate and, at a lower extent, of the high-dose group. This finding, however, is not assumed to be of a biological relevance.
The gross and/or visceral examination of the live foetuses revealed one foetus with anasarca in the vehicle control, two foetuses from one litter with subpleural haemorrhage in the low-dose group, one foetus each displaying mandibular aplasia and partial aplasia of the lungs, respectively, in the intermediate dose and one foetus showing omphalocele in the high-dose group. These findings are considered to be of a spontaneous origin and not related to the treatment. The incidences of mandibular aplasia, omphalocele and anasarca were found to be 0.05%, 0.04% and 0.12%, respectively, in the historical control population of the breed of rats used for the present experiment.
The skeletal assessment revealed instances of irregular sternebral ossification in the dose groups and in the vehicle control. This occurrence of sternebral anomalies in all groups was not assumed to be of an experimental significance, the overall incidence of sternebral anomalies being 0.37% in the historical control. Concerning the status of skeletal maturation of the foetuses shortly before term, no delay of ossification could be found for the experimental groups in comparison with the vehicle control.
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Table 1: Summarized reproduction data of the main study.
Dose group (mg/kg d) |
0 |
400 |
1200 |
2400 |
Historical control |
Spontaneous deaths |
0/25 |
0/24 |
0/25 |
0/25 |
0/842 |
Body-weight gain (%) |
+10.3 |
+10.3 |
+13.0 |
+9.3 |
|
Females with deciduomata |
0/25 |
0/24 |
0/25 |
0/25 |
1/842 |
Females with implantations |
22/25 |
22/24 |
24/25 |
22/25 |
784/842 |
Implantations/female (mean, SD) |
15.4±2.0 |
15.7±2.9 |
14.5±1.9 |
15.0±2.7 |
13.09±2.33 |
Females with total abortion |
0 |
0 |
0 |
0 |
0/784 |
Females with partial abortion |
0 |
0 |
0 |
0 |
2/784 |
Embryonal deaths (resorptions) |
3.8 |
7.0 |
8.4 |
8.2 |
8.74 |
Foetal deaths (resorptions) |
0.3 |
0.3 |
0 |
0.3 |
0.28 |
Dead foetuses |
0 |
0 |
0 |
0 |
0.13 |
Number of live foetuses (males-females) |
155-170 |
166-154 |
160-158 |
146-155 |
4554-4765 |
Percent males of live foetuses |
47.7 |
51.9 |
50.3 |
48.5 |
48.9 |
Average weight of live foetuses (g) |
5.3±0.5 |
5.3±0.4 |
5.4±0.4 |
5.4±0.4 |
5.34±0.45 |
Applicant's summary and conclusion
- Conclusions:
- Based on the results and under the condition chosen, the test article is considered to be not teratogenic.
- Executive summary:
In a prenatal developmental toxicity study following OECD guideline 414, 25 pregnant Tif:RAIf (SPF) rats per dose group were treated daily with the test article by gavage at 400, 1200, 2400 mg/kg body weight from day 6 to 15 of gestation. Dams were killed on day 21 and fetuses removed by Caesarian section. Body-weight gain was comparable for the dams of all groups. Food consumption of the experimental groups, however, showed some reduction during the treatment period (from day 6 of pregnancy) in comparison with the vehicle control. One female of the low dose group died due to an intubation error. Females No. 4 (vehicle control) and No. 78 (2400 mg/kg) delivered "spontaneously" (i.e. shortly before sacrifice on day 21 p.c.) and were not taken into further consideration of data.
The rates of implantation sites per female were comparable for all groups. The numbers of embryonic and/or fetal deaths (resorptions) were not increased at either dose. The male to female ratios of the fetuses were also comparable for all groups. In comparison with the vehicle control, the average body-weight of the live fetuses was not diminished at either dose. A slight but significant increase was noted for the live fetuses of the intermediate and, at a lower extent, of the high-dose group. This finding, however, is not assumed to be of a biological relevance. The gross and/or visceral examination of the live fetuses revealed one fetus with anasarca in the vehicle control, two fetuses from one litter with subpleural haemorrhage in the low-dose group, one fetus each displaying mandibular aplasia and partial aplasia of the lungs, respectively, in the intermediate dose and one fetus showing omphalocele in the high-dose group. The skeletal assessment revealed instances of irregular sternebral ossification in the dose groups and in the vehicle control. Concerning the status of skeletal maturation of the fetuses shortly before term, no delay of ossification could be found for the experimental groups in comparison with the vehicle control. Based on the findings a NOAEL of 2400 mg/kg body weight (highest dose tested) was derived for maternal and developmental toxicity.
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