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EC number: 231-554-3 | CAS number: 7631-99-4
- 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
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- Nanomaterial pour density
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- 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

Carcinogenicity
Administrative data
Description of key information
Several carcinogenicity studies are present with sodium nitrate, which are evaluated by WHO and IARC. The data do not indicate carcinogenic potential of sodium nitrate.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Link to relevant study records
- Endpoint:
- carcinogenicity: oral
- Type of information:
- other: Evaluation by competent authority
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: This publication represents a peer-reviewed evaluation of all published data on carcinogenic potential of nitrates.
- Details on results:
- The monograph includes evaluation of all published data on sodium nitrate up to 2006.
- Conclusions:
- There is inadequate evidence in humans for the carcinogenicity of nitrate in food.
There is inadequate evidence in humans for the carcinogenicity of nitrate in drinking water.
There is inadequate evidence in experimental animals for the carcinogenicity of nitrate.
However, ingested nitrate or nitrite under conditions that result in endogenous nitrosation is probably carcinogenic to humans (Group 2A).
There is an active endogenous nitrogen cycle in humans that involves nitrate and nitrite, which are interconvertible in vivo. Nitrosating agents that arise from nitrite under acidic gastric conditions react readily with nitrosatable compounds, especially secondary amines and amides, to generate N-nitroso compounds. These nitrosating conditions are enhanced following ingestion of additional nitrate, nitrite or nitrosatable compounds.
Some of the N-nitroso compounds that could be formed in humans under these conditions are known carcinogens. - Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The reliability and summary were made based on the HPV program adopted during OECD SIAM 25 (October 2007).
- Qualifier:
- no guideline followed
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- special grade reagent; purity 99.5%
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 104-weeks
- Frequency of treatment:
- ad libitum
- Post exposure period:
- 21 weeks
- Remarks:
- Doses / Concentrations:
2.5%, 5.0% in the diet
Basis: - No. of animals per sex per dose:
- The animals were divided into groups comprising 50 male and 50 female rats.
- Control animals:
- yes, concurrent no treatment
- Dose descriptor:
- NOAEL
- Effect level:
- >= 5 other: %
- Sex:
- male/female
- Basis for effect level:
- other: no increase in the incidence of malignant tumours
- Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The reliability and summary were made based on the HPV program adopted during OECD SIAM 25 (October 2007). The information given is limited to the below mentioned.
- Qualifier:
- no guideline followed
- GLP compliance:
- no
- Species:
- rat
- Strain:
- not specified
- Sex:
- male
- Route of administration:
- oral: drinking water
- Vehicle:
- water
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 273 days
- Frequency of treatment:
- ad libitum
- Post exposure period:
- None.
- Dose / conc.:
- 4 other: g/L
- No. of animals per sex per dose:
- 18-34 males/group
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- Study was conducted as a limit test.
- Dose descriptor:
- NOAEL
- Effect level:
- >= 4 000 mg/L drinking water
- Basis for effect level:
- other: no hyperplastic changes in the urothelium or carcinomas were found when treated with sodium nitrate alone.
- Conclusions:
- Subsequent exposure via the drinking water to the carcinogen BBNA and sodium nitrate enhanced the urinary bladder carcinogenisis in rats most likely because of the promotional effect of sodium nitrate (or possibly of sodium by itself).
- Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- documentation insufficient for assessment
- Qualifier:
- no guideline followed
- GLP compliance:
- no
- Species:
- rat
- Strain:
- not specified
- Sex:
- male/female
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 2 year
- Frequency of treatment:
- daily
- Post exposure period:
- not indicated
- Remarks:
- 0, 0.1, 1, 5 or 10% in diet
- No. of animals per sex per dose:
- 20/sex/group
- Control animals:
- yes, concurrent no treatment
- Dose descriptor:
- NOAEL
- Effect level:
- >= 10 other: %
- Sex:
- male/female
- Basis for effect level:
- other: no effects on tumor incidence.
- Conclusions:
- NOEL = 1% (equivalent to 500 mg/kg bw/day).
Referenceopen allclose all
No. with tumors (0% ; male) = 47 (94%)
No. with tumors (0%; female) = 46 (92%)
No. with tumors (2.5%; male) = 50 (100%)
No. with tumors (2.5%; female) = 43 (86%)
No. with tumors (5%; male) = 48 (96%)
No. with tumors (5%; female) = 39 (80%)
No marked clinical signs were noted that could be related to a toxic effect. After 9 months, macrohaematuria had developed in 2 rats receiving BBNA and sodium nitrate as a consequence of tumour break up. Treatment with BBNA and sodium nitrate, tripled the percentage of carcinoma’s and altered the nature of pre-tumourous changes in the direction of greater malignancy. In the group with sodium nitrate alone no hyperplastic changes in the urothelium or carcinomas were found.
A slight growth inhibition was observed at the 5% level and lethargy at the 10% level. Complete histopathological examination, including tumour incidences, was performed. No abnormalities or increased tumour incidence were found. The NOEL in this study was 1%, which corresponds to 370 mg of nitrate per kilogram of body weight per day
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
The weight of evidence approach takes both available data (negative results) and the justification for the absence of data into account. Based on these data, sodium nitrate is not classified for carcinogenicity according to Annex I of Regulation (EC) No. 1272/2008.
Additional information
Several studies with sodium nitrate are available. The data are used in a weight-of-evidence approach, therefore no key study is selected. Published data were evaluated by WHO and IARC. It is concluded that there are no indications that sodium nitrate has carcinogenic properties.
Justification for selection of carcinogenicity via oral route endpoint:
No single study was selected as key study, the conclusion was derived based on weight-of-evidence.
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