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EC number: 231-298-2 | CAS number: 7487-88-9
- 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
Ecotoxicological Summary
Administrative data
Hazard for aquatic organisms
Freshwater
- Hazard assessment conclusion:
- PNEC aqua (freshwater)
- PNEC value:
- 0.68 mg/L
- Assessment factor:
- 1 000
- Extrapolation method:
- assessment factor
- PNEC freshwater (intermittent releases):
- 6.8 mg/L
Marine water
- Hazard assessment conclusion:
- PNEC aqua (marine water)
- PNEC value:
- 0.068 mg/L
- Assessment factor:
- 10 000
- Extrapolation method:
- assessment factor
STP
- Hazard assessment conclusion:
- PNEC STP
- PNEC value:
- 10 mg/L
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
Sediment (freshwater)
- Hazard assessment conclusion:
- insufficient hazard data available (further information necessary)
Sediment (marine water)
- Hazard assessment conclusion:
- insufficient hazard data available (further information necessary)
Hazard for air
Hazard for terrestrial organisms
Soil
- Hazard assessment conclusion:
- insufficient hazard data available (further information necessary)
Hazard for predators
Secondary poisoning
- Hazard assessment conclusion:
- no potential for bioaccumulation
Additional information
PNEC aqua (freshwater)
For the 3 trophic levels (fish, invertebrates (Daphnia) and algae), several studies on the short-term toxicity are available. Therefore the lowest L(E)C50 observed from all conducted studies, a 96h-LC50 of 680 mg/L for Pimephales promelas is used for the derivation of the PNEC. An AF of 1000 is used in accordance with the “Guidance on information requirements and chemical safety assessment, Chapter R.10”.
PNEC aqua (freshwater): 0.68 mg/L
PNEC aqua (marine water)
For the 3 trophic levels (fish, invertebrates (Daphnia) and algae), several studies on the short-term toxicity are available. No studies with species in marine water are available, therefore the lowest L(E)C50 observed from all fresh water conducted studies, a 96h-LC50 of 680 mg/L for Pimephales promelas is used for the derivation of the PNEC. An AF of 10000 is then used in accordance with the “Guidance on information requirements and chemical safety assessment, Chapter R.10”.
PNEC aqua (marine water): 0.068 mg/L
PNEC (intermittent releases)
For the 3 trophic levels (fish, invertebrates (Daphnia) and algae), several studies on the short-term toxicity are available. Therefore the lowest L(E)C50 observed from all conducted studies, a 96h-LC50 of 680 mg/L for Pimephales promelas is used for the derivation of the PNEC. An AF of 100 is used in accordance with the “Guidance on information requirements and chemical safety assessment, Chapter R.10”.
PNEC (intermittent releases): 6.8 mg/L
PNEC STP
The substance is inorganic, therefore no ready biodegradability test is available. In addition, no study on toxicity to micro-organisms is available. However, In view of the use of the sulphate substances (fertilizer) and the available data on the other trophic levels (fish, invertebrates and algae) with the different inorganic sulphates, no toxicity is expected from magnesium sulphate. In addition, sulphates are known to be important for some microorganisms, e.g. some anaerobic microorganisms use sulphates as electron acceptors. Therefore, it is concluded that the EC50 >100 mg/L and NOEC is 100 mg/L for inorganic sulphates and thus no study need to be conducted. An AF of 10 is used in accordance with the “Guidance on information requirements and chemical safety assessment, Chapter R.10”.
PNEC STP: 10 mg/L
Conclusion on classification
Based on all the information available, both on magnesium sulphate itself as well as on other inorganic sulphates, the substance does not need to be classified according to Directive 67/548/EC and the CLP Directive for the environment. For inorganic substances no PBT or vPvB assessment is considered necessary (see Annex XIII of REACH).
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