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EC number: 233-332-1 | CAS number: 10124-37-5
- 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:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Non GLP; study was performed with a substance analogue and the data are read across.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Ten cultures of benthic diatoms were isolated from field samples from Eems Dollard Estuary (The Netherlands). The growth rate was determined as % chlorophyll a in diatoms grown in an artificial sea water medium containing increasing amounts of potassium nitrate. The test substance concentration was controlled using an auto-analyzer. The salinity of the test medium was kept constant at 15 or 37% depending on the algal strain tested. The climate room was maintained at 12ºC, with a quantum irradiance of 85 NE.m-2.sec-1 (4000 lux) from extra cool-white fluorescent tubes and a light period of 16 hours/day. In addition, the pH of the medium increased with a maximum of 0.4 after 24 hours incubation, most likely due to photosynthesis.
- GLP compliance:
- no
- Analytical monitoring:
- yes
- Vehicle:
- no
- Test organisms (species):
- other: several benthic diatoms; see results
- Details on test organisms:
- TEST ORGANISM
- Strain: benthic diatoms
- Source (laboratory, culture collection): isolated from field samples from Eems Dollard Estuary (The Netherlands). - Test type:
- static
- Water media type:
- saltwater
- Limit test:
- no
- Total exposure duration:
- 10 d
- Test temperature:
- The climate room was maintained at 12ºC.
- Salinity:
- The salinity of the test medium was kept constant at 15 or 37% depending on the algal strain tested.
- Nominal and measured concentrations:
- Nominal nitrate concentrations: 0.1, 0.68, 3.38, 6.75 and 16.9 mmol/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL Erlenmeyers with a thin layer of analytical clean sand
- Material, size, headspace, fill volume: 40 mL
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Artificial seawater, prepared according to Provasoli et al (1957), medium U
0.2 g/L NaHCO3
0.5 g/L tris buffer pH 8.0)
"minor elements"
26 mg/L HBO4
Vitamins, silicates and trace elements were added as in "f" medium described by Guillard and Ryther (1962)
OTHER TEST CONDITIONS
- Adjustment of pH: the pH of the medium increased with a maximum of 0.4 after 24 hours incubation, most likely due to photosynthesis.
- Photoperiod: quantum irradiance of 85 NE.m-2.sec-1 (4000 lux) from extra cool-white fluorescent tubes and a light period of 16 hours/day.
- Salinity (for marine algae): The salinity of the test medium was kept constant at 15 or 37% depending on the algal strain tested.
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Chlorophyll measurement: the growth rate was determined as % chlorophyll a - Key result
- Duration:
- 10 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 700 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- Most of the species (8 out of 10 tested, e.g. Navicula arenaria, Nitzschia dubiformis etc.) grew well at nitrate concentrations up to 16.9 mmol/L (=1.7 g/L). Nitrate was only clearly inhibitory to Nitzschia dubiformis and Amphiprora c.f. paludosa only at the highest test concentration.
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- Most of the species grew well at nitrate concentrations up to 16.9 mmol/L (=1.7 g/L). Nitrate was clearly inhibitory to Nitzschia dubiformis and Amphiprora c.f. paludosa only at the highest test concentration.
Reference
Relative rates (as % chlorophyll a) were:
Nitrate concentration (mmol/L)
Species 0.1 0.68 3.38 6.75 16.9
Navicula arenaria 80 95 100 107 94
Nitzschia c.f. dissipata 84 94 100 83 67
Nitzschia dubiformis 67 84 100 100 34
Nitzschia closterium 54 65 65 85 100
Amphiprora c.f. paludosa 71 89 86 100 39
Stauroneis constricta 52 92 98 102 100
Navicula cryptocephala 61 82 73 100 84
Navicula salinarum 65 73 89 100 86
Gyrosigma spencerii 76 100 100 91 70
Nitzschia sigma 92 75 100 98 58
Description of key information
No reliable study with calcium nitrate is available. Based on a reliable study with potassium nitrate, it was shown that the substance was not at all or only slightly inhibitory at the highest concentration tested (10 different algae tested). The read-across rationale can be found in the document attached in the target record and is fully incorporated in the CSR (see Appendix A).
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 1 700 mg/L
- EC10 or NOEC for freshwater algae:
- 1 700 mg/L
Additional information
No reliable study with calcium nitrate is available. A reliable study with ten cultures of benthic diatoms was performed with potassium nitrate. Diatoms were isolated from field samples from Eems Dollard Estuary (The Netherlands). The growth rate was determined as % chlorophyll a in diatoms grown in an artificial sea water medium containing increasing amounts of potassium nitrate. The test substance concentration was controlled using an auto-analyzer. The salinity of the test medium was kept constant at 15 or 37% depending on the algal strain tested. The climate room was maintained at 12ºC, with a quantum irradiance of 85 NE.m-2.sec-1 (4000 lux) from extra cool-white fluorescent tubes and a light period of 16 hours/day. In addition, the pH of the medium increased with a maximum of 0.4 after 24 hours incubation, most likely due to photosynthesis. Most of the species (8 out of 10 tested, e.g. Navicula arenaria, Nitzschia dubiformis etc.) grew well at nitrate concentrations up to 16.9 mmol/L (=1.7 g/L). Nitrate was only clearly inhibitory to Nitzschia dubiformis and Amphiprora c.f. paludosa only at the highest test concentration.
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