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EC number: 938-989-4 | CAS number: -
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
In an OECD 203 study (Madsen 2000), performed under GLP conditions, with the surrogate substance Monoammonium Phosphate no mortality was observed and the 96-hour LC50 value was determined to be >85.9 mg/L (>100 mg/L nominal), the highest treatment concentration tested.
In an OECD 203 study (under GLP conditions) calcium sulfate dihydrate was tested for acute toxicity to Oryzias latipes. As no mortalities were observed at the test concentration of 100 mg/L the LC50 was determined to be >100 mg/L. Also, in a study according to EU method C.1 (GLP) with potassium humate no mortality or other signs of toxicity were observed in guppy fish . The LC50 in this study was >128 mg/L.
Key value for chemical safety assessment
Additional information
The following information on constituents of the submission substance and components of the humate-complexed superphosphate are available:
Phosphate (monoammonium phosphate):
In an OECD 203 Guideline study (Madsen 2000), performed under GLP conditions, acute toxicity to fish of the surrogate substance Monoammonium Phosphate at nominal test concentrations of 6.25, 12.5, 25.0, 50.0, and 100 mg/L (measured concentrations: 5.72, 11.9, 23.5, 46.6, and 85.9 mg/L) was tested. No deviations from guideline were noted and the study was considered to be valid and of high quality, but information on purity of the test item is lacking (reliability 2).
No mortality was observed under the conditions of the test. Based on mean calculated total product test concentrations of Monoammonium Phosphate in test water, the 96-hour LC50 value was determined to be >85.9 mg/L (>100 mg/L nominal), the highest treatment concentration tested. The 96-hour NOEC was 85.9 mg/L, based on the absence of any mortality and sublethal effects at this and all lower treatment concentrations. On a phosphate basis this amounts to an equal concentration of Ca(H2PO4)2.
Potassium humate:
In a guideline study according to EU method C.1 (Roupcova 2007), performed under GLP conditions, acute toxicity to fish of the surrogate substance humic acid, potassium salt was investigated. No mortality or signs of abnormal behaviour were observed in guppies up to the highest concentration tested. Therefore, the LC50 - 96 h in this study was > 128 mg/L.
Ca sulfate:
In the publication by Mount et al. (1997) various solutions of inorganic salts were tested towards fish (fathead minnows, Pimephales promelas) and daphnids. The study is well documented and followed US EPA guidelines. An 96 h LC50 of >1970 mg/L was obtained for Ca-sulfate with Pimephales promelas.
In a study (limit test) according to OECD 203 (under GLP conditions) calcium sulfate dihydrate was tested for acute toxicity to Oryzias latipes. As no mortalities were observed at the test concentration of 100 mg/L the LC50 was determined to be >100 mg/L.
Taken these data together this shows that the submission substance, consisting of the humate phosphate complex and Ca sulfate does not possess aquatic toxicty to fish. An LC50 of > 86 mg/L can be deduced from the data.
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