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EC number: 237-048-9 | CAS number: 13597-46-1
- 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
Endpoint summary
Administrative data
Description of key information
- In an in-vitro skin irritation study according to OECD 439 (Human Skin Model Test), sodium selenate and sodium selenite were found to be irritating to the human skin.
- In an in vitro skin irritation study according to OECD 439 (), zinc selenite was found to be non-irritating to the human skin.
- In an in-vitro skin irritation study according to OECD 431 (Human Skin Model Test), sodium selenate and sodium selenite were found to be non-corrosive to the human skin.
- In an in-vitro bovine corneal opacity and permeability test for identifying ocular corrosives and severe irritants according to OECD 437, sodium selenate was found to be non-corrosive and/or no eye irritant.
- In an in-vitro bovine corneal opacity and permeability test for identifying ocular corrosives and severe irritants according to OECD 437, sodium selenite was found to be an eye irritant
- In an in vivo OECD 405 test with rabbits, zinc selenite was found to be non-corrosive and/or no eye irritant
Key information:
All studies are GLP-compliant and of high quality (Klimisch 1).
Key value for chemical safety assessment
Additional information
- Se-metal (massive, powder)
- Disodium selenate
- Disodium selenite
- Selenium dioxide / selenious acid
- Zinc selenite
- Barium selenite
Background
A read-across category-approach is used for the assessment of the toxicological properties of selenium and selenium compounds. The following Se-substance are included in the category:
A detailed rationale for the read-across hypothesis has been outlined in the read-across report that was generated according to the principles laid out in the Read-Across Assessment Framework (RAAF). In summary, the physico-chemical behavior of elemental selenium (once it has formed an ion-from its metal state), disodium selenite, disodium selenate and selenium dioxide/selenious acid is the same with regard to their metabolic fate. All selenium compounds (organic and inorganic, including elemental selenium), do share the very same metabolic fate in that after their resorption, reduction to the selenide moiety [Se2-], which is the single common precursor for its further metabolic conversion, takes place.
Therefore, there seems to be good evidence that different selenium moieties will behave very similar also for their ability to form reactive species which may play a decisive role in the generation of cytotoxicity followed likewise by unspecific and secondary clastogenicity and read-across can be made from the available data for disodium selenite. It is concluded that additional testing for each individual member of the proposed Se-category is not necessary and scientifically not meaningful.
In the case of inorganic salts like barium selenite and zinc selenite, uptake is always associated with a dissolution of the substance, i.e. dissociation into the metal cation (Zn2+, Ba2+) and the selenite anion (SeO32-). It can safely be assumed that the selenium/selenite moiety of barium/zinc selenite is generally of higher toxicological relevance than the zinc/barium cations. Therefore, the subsequent assessment of the toxicity of barium/zinc selenite focuses on the selenium moiety. As no in vivo toxicokinetic data or in vitro bioaccessibility data are available for a comparative assessment of relative bioavailability of various selenite substances, water solubility is adopted as a surrogate for bioavailability. Disodium selenite is readily soluble, with a water solubility of 800-900 g/L at 20°C. Barium selenite and zinc selenite, on the other hand, are poorly soluble salts (water solubility at 20°C of 66.7 mg/L and 16 mg/L, respectively, i.e. a difference of four/five orders of magnitude). Based on that, an intrinsically very conservative read-across from highly soluble forms to the poorly soluble barium/zinc selenite is proposed as the latter are assumed to have a lower solubility. It should also be noted that selenite anions in the tests with disodium selenite are formed under most physiological relevant conditions (i.e. neutral pH), thus facilitating unrestricted read-across between the various substances. In slightly acid conditions (pKa:8.32) the hydrogen selenite ion (HSeO3-) is formed whereas in more acidic conditions (pKa:2.62) the formation of selenious acid is observed (H2SeO3). Based on such existing equilibrium conditions, read-across between selenites, hydrogen selenites and selenious acid (solubility of 1670 g/L at 20°C) is justified.
In-vitro skin corrosion/irritation and in-vivo eye irritation testing has been performed since no reliable literature data were available on irritation properties of various Se-compounds.
Skin irritation:
In vitro studies were conducted with sodium selenate, sodium selenite and zinc selenite, using the human skin model EpiDermTM/ EpiSkinTM
Studies were conducted according to OECD guideline 439 to evaluate skin irritating effects. After the treatment with 25 mg of the solid test items sodium selenate or sodium selenite for 60 minutes, the relative absorbance values were reduced to 4.5% and 2.5%, respectively. This value is well below the threshold for irritation potential (50%). Therefore, both sodium selenate and sodium selenite are considered as irritant in the Human Skin Model Test. The relative adsorbance values for zinc selenite were reduced to 78.6%. This value is well above the threshold for irritancy (50%). Therefore this substance is not considered to possess an irritant potential. Zinc selenite has a significant lower solubility (compared to disodium selenate and disodium selenite), and it is therefore expected that the fraction dissolved selenite was too limited to cause any adverse irritating effects.
Eye irritation:
The in vivo rabbit test (OECD 405) with zinc selenite showed conjunctival redness (grade 1) as well as secretion in all animals 1 hour after instillation. Chemosis was observed in one animal 1 hour after instillation. Corneae and the irises were not affected by instillation of zinc selenite. The fluorescein test performed 24 hours after instillation did not reveal any changes. There were no systemic intolerance reactions. Bases on these results and taking into account the classification criteria according to regulation (EC) No. 1272/2008, a classification for causing eye damage or eye irritation is not required for zinc selenite. This substance has a significant lower solubility (compared to disodium selenite), and it is therefore expected that the fraction dissolved selenite was too limited to cause any adverse irritating effects.
Respiratory irritation:
In an acute toxicity study with zinc selenite (Leuschner, 2010) the gross pathological changes were recorded for each animal with particular attention to any changes in the respiratory tract. However, no abnormalities were detected at necropsy. As zinc selenite is not irritating to skin/eye, and shows no strong pH-effect upon dissolution in aqueous media, it is concluded that zinc selenite is no respiratory irritant.
Justification for classification or non-classification
- Skin corrossion/irritation: not classified
- Eye damage/irritation: not classified
Based on the available data, and taking into account the harmonised classifications, the following substance-specific classification is determined for zinc selenite:
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