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EC number: 231-391-8 | CAS number: 7529-22-8
- 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
- Study period:
- 2012-01-20 to 2012-04-27
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Samples were taken from the control and the 100 mg/L test group (replicates R1-R6 pooled) at 0 and 72 h for quantitative analysis of test substance concentration.
- Duplicate samples were taken.
- All samples were stored at approximately -20°C prior to analysis. - Vehicle:
- no
- Details on test solutions:
- - 200 mg test substance was dissolved in culture medium and the volume adjusted to 1 L to prepare the single 100 mg/L test solution to be used in the definitive test.
- The test solution was inverted several times to ensure adequate mixing and homogeneity. - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Strain: CCAP 278/4
- Source (laboratory, culture collection): Culture Collection of Algae and Protozoa (CCAP), SAMS Research Services Ltd, Scottish Marine Institute, Oban, Argyll, Scotland
- Master cultures were maintained in the lab by periodic replenishment of culture medium and were kept under constant aeration and illumination at 21°C.
- Age of inoculum (at test initiation): ~3 days (preculture, in log growth phase at the time of inoculation of the test)
- Initial cell density in test: 5E+03 cells/mL (nominal)
ACCLIMATION
- Acclimation period: none
- Culturing media and conditions (same as test or not): same as test
- Any deformed or abnormal cells observed: none noted - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
- Post exposure observation period:
- None
- Hardness:
- ca. 15 mg CaCO3/L (calculated)
- Test temperature:
- 24 +/- 1 °C
- pH:
- 7.4-8.3
- Dissolved oxygen:
- N/A
- Salinity:
- N/A
- Nominal and measured concentrations:
- Nominal: Control and 100 mg/L
Measured: 99-102% of nominal - Details on test conditions:
- TEST SYSTEM
- Test vessel: conical flask
- Type (delete if not applicable): plugged with polyurethane foam bungs
- Material, size, headspace, fill volume: glass, 250 mL, 100 mL fill volume
- Aeration: by shaking only
- Flasks were incubated using an INFORS Multitron Version 2 incubator and were constantly shaken at ca. 150 rpm
- Initial cells density: 5.84E+03 cells/mL (mean measured)
- Control end cells density: 1.33E+06 cells/mL (mean measured)
- No. of vessels per concentration (replicates): 6
- No. of vessels per control (replicates): 6
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reverse osmosis purified deionised water
- A standard test medium was used
- Culture medium different from test medium: no
- Intervals of water quality measurement: batch
- pH was measured at the start and end of testing. Temperature was recorded daily.
OTHER TEST CONDITIONS
- Adjustment of pH: not after addition of test item
- Photoperiod: continuous illumination
- Light intensity and quality: warm white light - 7000 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): cell density, at 0, 24, 48 and 72 h
- Determination of cell concentrations: Coulter Multisizer Particle Counter
TEST CONCENTRATIONS
- Range finding study: yes
- Test concentrations in range finding study: 0.1, 1.0, 10, 100 mg/L
- Results used to determine the conditions for the definitive study: yes - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- - Same results when based on yield
- Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): none - Results with reference substance (positive control):
- 72-h ErC50 = 1.4 mg/L (95% CI = 1.2-1.7 mg/L)
This result was within the normal range for this reference item. - Reported statistics and error estimates:
- Student's t-test incorporating Bartlett's test for homogeneity of variance was used to identify statistically significant differences (p < 0.05) between test and control groups.
- Validity criteria fulfilled:
- yes
- Conclusions:
- In this study a growth rate based 72-h EC50 of > 100 mg/L was obtained for the freshwater green alga Pseudokirchneriella subcapitata. No significant differences in growth rate nor yield were identified between the single test concentration and the control group. Therefore the 72-NOEC was >= 100 mg/L. Measured test substance concentrations were in agreement with nominal concentrations. The results of the test can therefore be considered reliable.
- Executive summary:
In a 72-h toxicity study, the freshwater alga Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) was exposed to N-methylmorpholine oxide in a limit test at 100 mg/l under static conditions in accordance with OECD guideline 201. Nominal concentrations were confirmed by analytical measurements. No effects on growth rate were observed. Therefore, the 72-h NOEC value was determined at >= 100 mg/L and the EC50value at >100 mg/L, both based on growth rate. No abnormalities were noted.
This toxicity study is classified as acceptable and satisfies the guideline requirement for OECD 201 toxicity study.
Results synopsis
Test organism: Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
Test type: Static
72 h EC50(growth rate): > 100 mg/L
72 h NOEC (growth rate): >= 100 mg/L
Reference
Description of key information
In a 72-h toxicity study, the freshwater alga Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) was exposed to N-methylmorpholine oxide in a limit test at 100 mg/l under static conditions in accordance with OECD guideline 201. Nominal concentrations were confirmed by analytical measurements. No effects of the test substance on growth rate were observed. Therefore, the 72-h NOEC value was determined at >= 100 mg/L and the EC50value at >100 mg/L, both based on growth rate.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 100 mg/L
Additional information
Short-term toxicity of NMMO to algae was investigated by exposing Desmodesmus subspicatus during 72 hours in a static test, according to the OECD guideline 201. This resulted in an EC50(72h) value of > 100 mg/L and an NOEC(72h) >= 100 mgL, both based on growth rate.
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