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EC number: 231-838-7 | CAS number: 7758-29-4
- 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
- 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
Carcinogenicity
Administrative data
Description of key information
Although STPP is subject to widespread dispersive use, it is not classified as a mutagen or genotoxin. The basic structure has no structural alerts for carcinogenicity or genotoxicity. Inorganic phosphate is a naturally-occurring nutrient essential for mammalian survival.
Key value for chemical safety assessment
Justification for classification or non-classification
Taken together, all three chronic toxicity/carcinogenicity studies indicate a common toxicity profile for all three salts: (1) no treatment-related increase in tumour incidence at the highest dose or any dose tested; (2) no increased mortality due to treatment; (3) some growth retardation at the highest dose tested, occasionally at the mid-dose level; (4) only minor effects on some red cell haematological parameters and organ weights and (5) target organ generally identified as the kidney, though effects were not observed with STMP.
Due to the common structural features as inorganic phosphate salts of sodium ion, the evaluation for the same endpoints on all three salts and the same or similar findings in all three studies on chronic toxicity/carcinogenicity, it is concluded that STPP is not expected to be carcinogenic in rats and that the current study on STPP(Hodge 1959, 1964) and the studies on STHP and STMP provide adequate data to support this conclusion.
Additional information
The major effect of feeding high doses of STPP for two years is toxicity to the kidneys and reduced red blood cell counts and haemoglobin concentration in the blood. The Hodge study (1959, 1964) was conducted prior to the institution of good laboratory practice guidelines and to the currenct OECD Guideline 453. Therefore, the study has deficiencies when examined according to today’s standards. The study is considered a Klimisch Code 2, reliable with restrictions. The conclusions regarding the hazard identification of STPP are supported by data on sodium hexametaphosphate (SHMP) and sodium trimetaphosphate (STMP), both of which are structurally similar to STPP. All three inorganic phosphate salts exhibited a lack of carcinogenicity when tested in two year chronic toxicity/carcinogenicity studies.
In theManual for Investigation of HPV Chemicals, Chapter 3: Data Evaluation (2005), Section 3.1.6 Weight-of-the-Evidence Analysis, requires the use of a weight-of-the-evidence analysis during the assessment of data quality and adequacy. The guidance permits the pooling of several studies, one or more of which may be inadequate, to satisfy a specific SIDS element. In the current case, available data exist on two other sodium inorganic phosphate salts which are similar in structure to STPP. In a chronic toxicity/carcinogenicity study on sodium hexametaphosphate (SHMP), no treatment-related increase in tumour incidence was observed at any dose in rats administered the salt at doses of 0.05, 0.5 and 5.0% in the diet for 24 months (IUCLID Robust Study Summary included as supplemental information). Similarly, in a chronic toxicity/carcinogenicity study on sodium trimetaphosphate (STMP), no treatment-related increase in tumour incidence was observed at any dose in rats administered the salt at doses of 0.1, 1.0 and 10.0% in the diet for 24 months (IUCLID Robust Study Summary included as supplemental information). For both compounds the studies were conducted prior to good laboratory practice guidelines and OECD Guideline 453; thus, these studies have similar deficiencies to the study on STPP.
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