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EC number: 233-267-9 | CAS number: 10102-18-8
- 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
Additional information
Added risk approach
Selenium is naturally present in all environmental compartments. The median baseline background concentration in unpolluted stream water in Europe is 0.32 µg Se/L (Vercaigne et al., 2010). These background concentrations are significant compared to the PNEC freshwater (2.67 µg Se/L). Moreover, toxicity due to dietary exposure to Se is more critical compared to direct exposure to dissolved Se, with a critical Se concentration in water for secondary poisoning of 0.21 µg Se/L (based on PNECoral of 1 mg Se/kg diet and a generic bioaccumulation factor of 4721 L/kg). Therefore, the added risk approach is employed and all NOEC and EC10 values are based on added selenium concentrations, without taking into account the natural background concentration in water. In essence this added risk assessment approach assumes that species are fully adapted to the natural background concentration and therefore that only the anthropogenic added fraction should be regulated or controlled (Appendix R.7.13-2 of the REACH guidance on “Environmental risk assessment for metals and metal compounds”). Because measured background concentrations in exposure media are generally below the detection limit (generally 1-2 µg Se/L) and chronic NOEC values vary between 10 and 11000 µg Se/L, these NOEC values can be considered as added dissolved Se concentrations.
Summary toxicity data
Reliable ecotoxicity results selected for the effect of selenium on aquatic organisms are available for H2SeO3, Na2SeO3, SeO2 Na2SeO4 and seleno-(D)L-methionine. All data were reported based on dissolved elemental Se concentrations. The data for Se-(D)L-methionine were not taken into account for the assessment of direct effects of selenite to aquatic organisms because there is some concern on different biochemical behaviour of this selenium containing amino acid compared to inorganic Se compounds. The data available for the inorganic Se compounds do not allow conclusions on the effect of water properties (pH, hardness, etc.) or Se substance on toxicity of selenium to aquatic organisms. Therefore, all reliable toxicity data for all inorganic Se substances, expressed on a dissolved selenium basis, were grouped for the effects assessment.
The table below presents an overview of the lowest reliable toxicity data for the various trophic levels of aquatic organisms.
Trophic level | Substance | Species | Parameter | Endpoint | Value (µg Se/L) | Reference |
Acute toxicity, freshwater | ||||||
Fish | SeO2 | Pimephales promelas | mortality | 96-h LC50 | 2060 | Cardwell et al., 1976 |
Invertebrates | Na2SeO3 | Daphnia magna | mortality | 48-h LC50 | 550 | Maier et al., 1993 |
Algae | Na2SeO3 | Selenastrum capricornutum | growth rate | 72-h EC50 | 44240 | LISEC, 1992 |
Acute toxicity, marine water | ||||||
Fish | Na2SeO3 | Morone saxatilis | mortality | 96-h LC50 | 3300 | Chapman, 1992 |
Algae | Na2SeO4 | Dunaliella viridis | growth rate | 96-h EC50 | 45000 | Brix et al., 2004 |
Chronic toxicity, freshwater | ||||||
Fish | Na2SeO3 | Lepomis macrochirus | prespawning mortality | 258-d NOEC | 10 | Hermanutz et al., 1992 |
Invertebrates | H2SeO3 | Daphnia magna | reproduction | 28-d NOEC | 70 | Kimball, 1978 |
Algae | Na2SeO4 | Chlamydomonas reinhardtii | growth | 96-h NOEC | 197 | Geoffroy et al., 2007 |
Plants | Na2SeO3 | Lemna minor | growth (%surface coverage) | 14-d NOEC | 80 | Jenner and Janssen-Mommen, 1993 |
Chronic toxicity, marine water | ||||||
Fish | Na2SeO3 | Pagrus major | growth | 28-d NOEC | 25 | Kim and Kang, 2014 |
Invertebrates | Na2SeO3 | Allorchestes compressa | reproduction | 28 -d NOEC | 44 | Ahsanullah and Brand, 1985 |
Algae | Na2SeO4 | Dunaliella viridis | growth rate | 72 -h NOEC | 11000 | Brix et al., 2004 |
Reliable short-term toxicity data for freshwater organisms are available for three trophic levels: aquatic invertebrates, fish and algae. Acute L(E)C50 values vary between 550 and 48200 µg Se/L, with the lowest acute effect value was a 48-h LC50 of for the effect of Na2SeO3 on mortality of Daphnia magna. Acute toxicity data are also available for marine fish and algae (3300-76000 µg Se/L).
Reliable long-term toxicity data are available for 11 freshwater organisms covering the three trophic levels. The lowest chronic NOEC, 10 µg Se/L, was observed for the effect of Na2SeO3 on pre-spawning mortality of Lepomis macrochirus after 238 days exposure. Reliable long-term toxicity data were also identified for the effect of Na2SeO3 and Na2SeO4 on a marine fish, a marine alga and two marine invertebrates with NOEC values between 25 and 11000 µg Se/L.
Data for dietary toxicity are also available for 6 freshwater fish species with NOECoral values between 2.2 and 89.8 mg/kg dw diet for growth and mortality based on studies with Na2SeO3, SeO2, Na2SeO4 and seleno-(D)L-methionine. Because after release in the environment, inorganic Se can be transformed into Se containing amino acids, data for seleno-methionine and seleno-cysteine are included for the assessment of secondary poisoning (through PNECoral and bioconcentration factors).
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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