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EC number: 211-063-0 | CAS number: 628-96-6
- 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Subacute and chronic toxicity studies of trinitroglycerin in dogs, rats, and mice
- Author:
- Ellis III, H.V., Hong, C.B., Lee, C.C., Dacre, J.C. and Glennon, J.P.
- Year:
- 1 984
- Bibliographic source:
- Fundamental and Applied Toxicology, 4(2): 248-260
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 452 (Chronic Toxicity Studies)
- Principles of method if other than guideline:
- Solubility and hydrolysis characteristics, f.pt., and m.pt. of glycerol trinitrate were not determined for this study. They are published. Food intake was measured weekly for the first four weeks and for one week / month, thereafter. Body weights were measured weekly until the body weight leveled off, and biweekly thereafter. Blood was collected for hematology analyses from tail tips of (where possible) the same four males and four females before the test started, and at the end of 3, 6, 9, 12, 18, and 24 months. Interim blood chemistry analyses were performed at twelve months. There were no urinalyses. Rectum, femur and aorta were not routinely examined microscopically. At the end of 12 months and 24 months, four males and four females from each group were taken off the test diet, put on "control" diets, and maintained as recovery groups under conditions otherwise identical to those of the test and control groups. These two sets of "recovery" rats were sacrificed at the end of months 13 and 25, respectively, and subjected to the same clinical, hematological, macroscopic, and microscopic examinations as the animals sacrificed at 12 and 24 months, those sacrificed in extremis, and the unscheduled deaths. Also, after 12 months on test, abdominal aortal blood was taken for hematology and clinical chemistry from four males and four females from each group. These animals were then sacrificed, necropsied, and their organs examined for histopathologic effects. In addition, four males and four females from each group were scheduled for sacrifice at each of 3, 6, 9, and 18 months for the same 1) blood hematologic and chemical, 2)gross whole-body and organ, and 3) histopathologic examinations. Any remaining survivors at 24 months were scheduled for the same examinations.
- GLP compliance:
- no
- Remarks:
- study pre-dated 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
- IUPAC Name:
- propane-1,2,3-triyl trinitrate
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: Charles River CD
- Sex:
- male/female
- 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 weeks
ENVIRONMENTAL 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)
- Details on oral exposure:
- DIET PREPARATION:
- Rate of preparation of diet (frequency): Diets were prepared weekly.
- Mixing appropriate amounts with (Type of food): 10% concentrate was mixed with feed in a rotating box on a modified mixer to provide the diet mixture by successive dilutions. The control rodents received a mixture containing 10% dried feed in ordinary feed. With the rodents, dosage levels of 0,01% (100 ppm), 0,1% (1000 ppm) and 1% (10 000 ppm) in the diet were used. - Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 24 hours/day (continuous) for two years
- Frequency of treatment:
- daily in the diet
Doses / concentrations
- Remarks:
- Doses / Concentrations: 0.0, 0.01, 0.1 1.0% (w/w) of diet. Corresponds to male and female daily intakes of 0.0, 3.04 ± 0.16, 31.5 ± 1.6, 363 ± 10 and 3.99 ±0.18, 38.1 ±1.6, and 434 ± 11 mg NG / kg day, respectively (means ± standard errors of 24 monthly measurements). Basis:actual ingested
- No. of animals per sex per dose:
- The begining number of rats was 38 of each sex per group.
- Control animals:
- yes
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: YES
- Time schedule: daily
- Cage side observations were included: behavioral changes
DETAILED CLINICAL OBSERVATIONS: YES
- Time schedule: daily
- All animals were observed for toxic signs.
BODY WEIGHT: YES
- Time schedule for examinations: weekly for the first 6 months, after weight gain leveled off, they were weighed biweekly.
FOOD CONSUMPTION AND COMPOUND INTAKE: YES
- Food consumption was measured during the first 4 weeks and then during the last week of each month.
HAEMATOLOGY: YES
- Time schedule for collection of blood: After 12 months dosing
- Number of animals: 4 males/4 females from each dosage group were bled from their aortas.
- Parameters examined: erythrocyte, reticulocyte, leucocyte, and platelet counts; hematocrit, hemoglobin, erythrocyte indices, methemoglobin, Heinz bodies, and c lotting time.
CLINICAL CHEMISTRY: YES
- Time schedule for collection of blood: After 12 months dosing
- Number of animals: 4 males/4 females from each dosage group
- Parameters examined: fasting blood glucose, serum SGOT, serum SGPT, APase, and BUN. Special tests, e.g., serum electrolytes were to be performed whenever indicated - Sacrifice and pathology:
- GROSS PATHOLOGY: YES
ORGAN AND OTHER WEIGHTS: Brain, heart, liver, kidneys, spleen and gonads.
HISTOPATHOLOGY: YES - Statistics:
- In general, standard methods (Steel & Torrie, 1960), with p<0.05 considered significant. Continuous variables were analysed by Dunnett'smultiple comparison procedure after an analysis of variance or Student's t test. Enumeration data, such as tumor incidence, were analysed by Fisher's exact probability test. In some of the histopathologic incidence analyses the CHI square test or exact probabilities on contingency tables with p<0.05 were considered significant.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Haematological findings:
- effects observed, treatment-related
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Details on results:
- CLINICAL SIGNS AND MORTALITY: Rough fur, matted appearance
BEHAVIOUR: A lack of grooming
BODY WEIGHT AND WEIGHT GAIN: High dose: depressed weight gain
FOOD CONSUMPTION: High dose: decrease feed consuption
HAEMATOLOGY: High dose: methemoglobinemia, elevated erythrocyte, hematocrit and hemoglobinSmall amounts of methemoglobin were occasionally seen in other dose groups.
CLINICAL CHEMISTRY: Abnormal values for glucose, alkaline phosphate, SGOT, SGPT
ORGAN WEIGHTS: Remarkably large livers
High dose: high kidney weights were normal variation, increase in spleen weights were normal variation
GROSS PATHOLOGY AND HISTOPATHOLOGY:
High dose:
- Liver: 1) cholangiofibrosis, proliferace of the bile ducts, fibrous tissue, white patches of various sites, cystic, adenomatoid, 2) development of hepatocellular carcinoma, occasional metatatstic nodules in the lungs
- Testis: Cell tumors in the testis (pressure on the tubules, aspermatogeneisis)
- Spleen and renal epithelium: Pigment deposit (hemosiderin)
The most common tumors in the high dose rats: Pituitary adenoma (males/females), Mammary (females), Primarily fibroadenomas (females).
These tumors were the most common causes of death.
Effect levels
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 3.04 mg/kg bw/day (actual dose received)
- Sex:
- male
- Basis for effect level:
- other: The low dose ( 24 month ave. in males = 3.04 ± 0.16 mg glycerol trinitrate / kg /day; in was a "no-effect" dose in males by any of the criteria used.
- Dose descriptor:
- NOAEL
- Effect level:
- 3.99 mg/kg bw/day (actual dose received)
- Sex:
- female
- Basis for effect level:
- other: The low dose ( 24 month ave. in females = 3.99 ± 0.18 mg glycerol trinitrate / kg / day) was a "no-effect" dose in femalesby any of the criteria used.
- Dose descriptor:
- LOAEL
- Effect level:
- 31.5 mg/kg bw/day (actual dose received)
- Sex:
- male
- Basis for effect level:
- other: The middle dose (24 month ave. in males = 31.5 ± 1.6 mg glycerol trinitrate / kg / day was an effect dose in males.
- Dose descriptor:
- LOAEL
- Effect level:
- 38.1 mg/kg bw/day (actual dose received)
- Sex:
- male/female
- Basis for effect level:
- other: The middle dose (24 month ave. in females = 38.1 ± 1.6 mg glycerol trinitrate / kg / day) was an effect dose in females.
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- The high dose with glycerol trinitrate intake of 363 mg/kg/day in males and 434 mg/kg/day in females was toxic, decreased feed consumption and depressed weight gain. The target organs included the blood (methemoglobin), liver (cholangiofibrosis and hepatocellular carcinoma) and testis (intersticial cell tumor). There was a decrease in the naturally occurring tumors of the pituitary and mammary gland, which decreased the death rate in females.
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