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Diss Factsheets
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EC number: 249-820-2 | CAS number: 29736-75-2
- 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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
The lowest valid NOEC for chronic toxicity to freshwater fish is 1.13 mg Sb/L for Pimephales promelas. (Kimball, 1978).
There are no valid chronic studies with marine fish.
Key value for chemical safety assessment
Additional information
Only two studies are considered to be valid (Kimball, 1978 and LeBlanc and Dean, 1984). However, only Kimball can be used to derive a PNEC since the NOECs reported by LeBlanc and Dean are unbounded.
LeBlanc and Dean (1984) exposed eggs from Pimephales promelas in a flow-through system, using two replicates, with five concentrations (range: 0.6 - 7.5 µg Sb/L) and two controls (one regular and one vehicle control (HCl)), with each replicate comprising 55 eggs. The tests were performed in well water with a hardness of 28-40 mg CaCO3/L. Since there were no statistically different effects (endpoints: mortality, larvae lengths and weights) when compared to the control, even at the highest concentration used (7.5 µg Sb/L), the resulting unbounded NOEC value was > 7.5 µg Sb/L.
A chronic test performed by Kimball (1978), used embryo-larvae of Pimephales promelas in a flow-through system, with four replicates and six concentrations (range: 0.52 – 19.11 mg Sb/L) and a control, with each group comprising 20 eggs. The tests were performed with hard well water. The lowest resulting NOEC from this study, using reduction of length as an indicator of toxicity, is 1.13 mg Sb/L. This value is also the lowest valid NOEC for freshwater fish from long-term toxicity tests.
There are studies by Birge and co-workers (Birge, 1978; Birge et al., 1980), which report NOECs below 1.13 mg Sb/l. However, even though these studies are well performed, with measured test concentrations etc., neither of them are considered to be valid. The reason for this is that the test concentrations used are never reported, which makes it impossible to determine whether the calculated NOEC values are included in the tested concentration range.
The reasons why the result by Doe et al.(1987) on Oncorhynchus mykiss is not considered reliable are presented in the section on acute toxicity above.
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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