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EC number: 200-821-6 | CAS number: 74-90-8
- 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:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: This study was conducted to assess teratogen effects before establishment of a guideline. Sufficient data is provided to determine that its conclusion is valid.
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 982
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 983
- Report date:
- 1983
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Principles of method if other than guideline:
- Method: other. Predates guideline
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 2-hydroxy-2-methylpropionitrile
- EC Number:
- 200-909-4
- EC Name:
- 2-hydroxy-2-methylpropionitrile
- Cas Number:
- 75-86-5
- Molecular formula:
- C4H7NO
- IUPAC Name:
- 2-hydroxy-2-methylpropanenitrile
- Details on test material:
- IUCLID 4 Test Substance: as prescribed by 1.1 - 1.4
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
Administration / exposure
- Route of administration:
- oral: gavage
- Details on exposure:
- Rats were dosed at a constant volume of 5 ml/kg.
- Frequency of treatment:
- daily (gd 6 through 15)
- No. of animals per sex per dose:
- 25
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- sex: female
duration of test: 9 days
Examinations
- Maternal examinations:
- Clinical observations were performed daily and body weights recorded on gd 0, 6, 10, 12, 16 and 20.
- Ovaries and uterine content:
- At scheduled necropsy on gd 20, dams were sacrificed and the implantation sites evaluated (number and location of viable and non-viable fetuses, early and late resorptions and number of total implantations and corpora lutea), abdominal and thoracic cavities were examined for grossly evident morphological changes.
- Fetal examinations:
- Fetuses were removed, weighed, sexed, tagged and examined for soft tissue malformations using the method of Wilson (Teratology-Principles and techniques Univ. Chicago Press, Chicago, IL 262-277 1965). Remaining fetuses were eviscerated, fixed and stained for subsequent skeletal
examination by a method similar to that described by Dawson (Stain Technol. 1 123-124, 1926).
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
observed at 1 mg/kg bw/d
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 1 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 10 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: teratogenicity
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Key result
- Developmental effects observed:
- no
Any other information on results incl. tables
Survival of the dams was 100% for the control and all
treatment groups. The antemortem and necropsy observations
for treated groups was comparable to those for control
groups. Signs of maternal toxicity was evident by slight
reduction in body weight gain, during the overall treatment
and gestation periods (days 6 to 15 and 0 to 20
respectively), in the 3 and 10 mg/kg/day group.
Statistically significant differences in corpora lutea/dam
and total implantation/dam ratios occurred between the 10
mg/kg/day and control groups. However, because these were
pretreatment parameters they were not considered compound related.
Fetal deaths
at 10 mg/kg/day. The viable
fetus/dam, post implantation losses/dam, mean fetal body
weight and fetal sex distribution in the 10 mg/kg/day group
and all cesarean section observation parameters for the 1
and 3 mg/kg/day dosage groups were comparable with controls.
The incidence of fetal malformations and developmental
variations was comparable between test and control groups.
Acetone cyanohydrin did not elicit a teratogenic response
when administered by the oral route to Charles River rats at
10 mg/kg/day.
Applicant's summary and conclusion
- Conclusions:
- Timed-pregnant rats were dosed with acetone cyanohydrins (0, 1, 3 and 10 mg/kg bw/d, at a constant volume of
5 ml/kg. Group sizes consisted of 25 animals and 25 litters were examined per group (no premature deaths). Clinical
observations were performed daily and body weights recorded on gd 0, 6, 10, 12, 16 and 20. At scheduled necropsy on gd
20, dams were sacrificed and the implantation sites evaluated (number and location of viable and non-viable fetuses, early
and late resorptions and number of total implantations and corpora lutea), abdominal and thoracic cavities were
examined for grossly evident morphological changes. Fetuses were removed, weighed, sexed, tagged and examined for soft
tissue malformations using the method of Wilson (1965). Remaining fetuses were eviscerated, fixed and stained for subsequent skeletal
examination by a method similar to that described by Dawson (1926).
Survival of the dams was 100% for the control and all treatment groups. The antemortem and necropsy observations
for treated groups were comparable to those for control groups. Signs of maternal toxicity was evident by slight
reduction in body weight gain, during the overall treatment and gestation periods (days 6 to 15 and 0 to 20
respectively), in the 3 and 10 mg/kg/day group. Statistically significant differences in corpora lutea/dam
and total implantation/dam ratios occurred between the 10 mg/kg/day and control groups. However, because these were
pretreatment parameters they were not considered compound related. Fetal deaths at 10 mg/kg/day. The viable
fetus/dam, post implantation losses/dam, mean fetal body weight and fetal sex distribution in the 10 mg/kg/day group
and all cesarean section observation parameters for the 1 and 3 mg/kg/day dosage groups were comparable with controls.
The incidence of fetal malformations and developmental variations was comparable between test and control groups.
Acetone cyanohydrin did not elicit a teratogenic response when administered by the oral route to Charles River rats at
10 mg/kg/day.
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