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EC number: 200-240-8 | CAS number: 55-63-0
- 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:
- key study
- Study period:
- 1976-1978
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Meets generally accepted scientific standards, well documented and acceptable for assessment.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 978
- Report date:
- 1978
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: FDA Guidelines (1966)
- Deviations:
- no
- Principles of method if other than guideline:
- Sexually mature virgin females were mated with experienced young adult male rats. The dams' F1c litter was used for this study. The dams were placed on test or control diets for gestation days 6-15, incl., and were sacrificed (CO2 inhalation) on gestation day 20.
- GLP compliance:
- no
- Remarks:
- Unlikely. Study pre-dated even USFDA GLPs
- Limit test:
- no
Test material
- Reference substance name:
- Glycerol trinitrate
- EC Number:
- 200-240-8
- EC Name:
- Glycerol trinitrate
- Cas Number:
- 55-63-0
- Molecular formula:
- C3H5N3O9 C3H5(NO3)3
- IUPAC Name:
- propane-1,2,3-triyl trinitrate
- Details on test material:
- - Name of test material (as cited in study report): Nitroglycerin, TNG
- Substance type: technical product
- Physical state: a 10 % mixture on lactose
- Analytical purity: 9.72% +/- 0.09%
- Lot/batch No.: D17-H3
- Source: Atlas Chemical Division, ICI America Inc., Wilmington, DE
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: Charles River CD
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS- Source: Charles River Breeding Laboratory, Wilmington, Massachusetts, USA- Age at study initiation: All animals were maturing- Fasting period before study: no data- Housing: plastic cages with metal lids, filter tops, 4 male or 5 female in each cage, some groups were subdivided to prevent fighting.- Identification of animals: ear-punches- Bedding: with hardwood chip- Diet: ad libitum, Diets were prepared weekly- Water: ad libitum- Acclimation period: 2 weeksENVIRONMENTAL CONDITIONS- Temperature (°F): 75+/-5- Humidity (%): 50+/-10%- Air changes (per hr): 10 air changes per hour- Photoperiod (hrs dark / hrs light):12 hour light/12 hour dark
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Test levels of diet were prepared fresh weekly by dilution of the concentrate with unheated feed and were analyzed after preparation. Control analyses were carried out over eight-day periods to measure evaporation of NG from the diet under cage conditions during the week. GC also was used for these analyses, but with a 63Ni detector. This information was used to calculate actual dosage received by the rats.
- Duration of treatment / exposure:
- 24 hours/day for 10 days (gestation days 6-15, incl.)
Examinations
- Maternal examinations:
- During pregnancy the dams were observed daily. Females were weighted day 0 and day 20 of pregnancy. The females were sacrificed (CO2 inhl.) on gestation day 20.
- Ovaries and uterine content:
- After necropsy the weight of uterus was recorded. The number of corpora lutea and number and position of live, dead and resorbed fetuses is recorded.
- Fetal examinations:
- Fetuses were then removed from the uterus, weighed, and examined for any external anomalies. Half the fetuses from each litter were then fixed inBouin's fluid, manually sectioned, and examined for soft tissue /internal organ anomalies by Wilson's method (Wilson, 1965). The remaining fetuses were fixed in 70% ethanol followed by 1% potassium hydroxide and then stained with alizarin red (Staples and Schnell, 1964). This was followed by differential decolorization and examination forskeletal anomalies
Results and discussion
Results: maternal animals
Effect levels (maternal animals)
- Remarks on result:
- not measured/tested
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yesDetails on embryotoxic / teratogenic effects:See attached document, Table-No. 1.
Effect levels (fetuses)
- Dose descriptor:
- NOEL
- Effect level:
- 6.4 mg/kg bw/day
- Basis for effect level:
- other: teratogenicity
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- The weights of the high-dose females at termination and their weight changes (excluding the uterus and contents) were significantly less than those of the control group and less than those of the two groups tested at lower doses, as indicated in the summary table above. In addition, their liver weights were significantly increased relative to their corrected body weight and increased relative to those of the two lower dose test groups. Diaphragmatic hernias occurred only in the high dose group and were believed, by the investigators, to be due to the test material. Their incidence was not significant (two-sample rank test), but they occurred in 4 / 19 of the high dose litters from this study. The incidences of unossified and incompletely ossified hyoid bones also were significantly increased compared to the controls and were increased compared to the two lower dose test groups. However, sternabrae, centra, and skull bones were not similarly affected.
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