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EC number: 231-635-3 | CAS number: 7664-41-7
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- see read across justification
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 4.77 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- NH3
- Basis for effect:
- growth rate
- Executive summary:
According to the test guideline, the OECD medium used for algae testing contains 15 mg NH4/l. This concentration is the concentrationin the test medium used for algae tests. Therefore, it must be assumed that this concentration is appropriate for good growth of the cultures and can be used as minimum concentration for the NOEC.
Applying the conversion factor from NH4Cl to NH3 the NOEC of > 15 mg NH4Cl/L corresponds to a NOEC of 4.77 mg NH3/L.
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- see read across justification
- Reason / purpose for cross-reference:
- read-across source
- Reference substance (positive control):
- no
- Duration:
- 18 d
- Dose descriptor:
- EC50
- Effect conc.:
- 2 700 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- not specified
- Basis for effect:
- cell number
- Conclusions:
- The effect of ammonia concentration on growth and physiology of a unicellular green alga, Chlorella vulgaris, was studied. Algal growth was accompanied by a decrease in nitrogen content in the medium, indicating that nitrogen removal was due to algal uptake and assimilation. Results demonstratethat C. vulgaris can tolerate high concentrations of ammonia. The 18 day EC50 was calculated to be 2700 mg/L.
Less growth was found in cultures containing either very low (10 mg/l) or very high (750 and 1000 mg/l) ammonia concentration. - Executive summary:
The effect of ammonia concentration on growth and physiology of a unicellular green alga, Chlorella vulgaris, was studied. Algal growth was accompanied by a decrease in nitrogen content in the medium, indicating that nitrogen removal was due to algal uptake and assimilation. Results demonstratethat C. vulgaris can tolerate high concentrations of ammonia. The 18 day EC50 was calculated to be 2700 mg/L.
Less growth was found in cultures containing either very low (10 mg/l) or very high (750 and 1000 mg/l) ammonia concentration.
Applying the conversion factor from NH3 -N to NH3, the EC50 of 2700 mg NH3-N/L corresponds to 3283.2 mg NH3/L
Referenceopen allclose all
In the control a lag-phase could be observed until day 11(decline of cell number to approx. 10x10e6 cells/mL). Logarithmic growth could be seen from day 11 - 18 (declineof cell number up to appr. 70x10e6 cells/mL). From day 18 -21 the cell number dropped back to 10x10e6 cells/mL. For this reason the calculation of EC50 is referred to the cellnumber at day 18. Growth occurred in all ammonia concentrations (10-1000 mgN/L), although less growth was found in cultures containingeither very low (10 mg N/L) or very high (750 and 1000 mgN/L) ammonia concentrations. Algal growth was accompanied by a decrease in nitrogen content in the medium, indicating that nitrogen removal wasdue to algal uptake and assimilation. Results demonstratethat C. vulgaris can tolerate high concentrations ofammonia.
In the first about 10 days after start, in all test concentration and in the control a lag phase was observed. Thereafter in the control and some test concentrations an exponential increase in cell number was observed up to day 17 or 18. There are no data available to calculate the 72-hEC50.
The 18 day EC50 was calculated to be 2700 mg N/L.
Description of key information
An EC50 of 3283.2 mg NH3/L is calculated for Chlorella vulgaris. The NOEC is >= 4.77 mg NH3/L (deduced from the NH4-concentration as requested in the OECD test medium).
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 3 283.2 mg/L
Additional information
The effect of ammonia concentration on growth and physiology of a unicellular green alga, Chlorella vulgaris, was studied by Tam & Wong (1996). Algal growth was accompanied by a decrease in nitrogen content in the medium, indicating that nitrogen removal was due to algal uptake and assimilation. Results demonstrate that C. vulgaris can tolerate high concentrations of ammonia. The 18 day EC50 was calculated to be 2700 mg/L. Algae appear to be of lower sensitivity to the toxicity of ammonia compared to other aquatic organisms including fish, consistent with the fact that ammonia represents a nitrogen source for algae, which is required for growth. According to the test guideline, the OECD medium used for algae testing contains 15 mg NH4/l. This concentration is the concentrationin the test medium used for algae tests. Therefore, it must be assumed that this concentration is appropriate for good growth of the cultures and can be used as minimum concentration for the NOEC. Applying the conversion factor from NH4Cl to NH3 the NOEC of > 15 mg NH4Cl/L corresponds to a NOEC of 4.77 mg NH3/L.
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