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EC number: 229-194-7 | CAS number: 6425-39-4
- 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:
- 2011-08-19 to 2011-09-29
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Study performed according to internationally accepted test guidelines for toxicity to algae (OECD 201) and conform CLP requirements.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- GLP compliance:
- yes
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: PFW100113
- Expiration date of the lot/batch: 2012-12-01
- Analytical purity: 99.3 %
- Impurities (identity and concentrations): not reported
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: room temperature in the dark
- Stability under test conditions: not reported
OTHER SPECIFICS:
- Name of test material (as cited in study report): DMDEE (Morpholine, 4,4'-(oxydi-2,1-ethanediyl)bis-)
- Substance type: pale yellow liquid
- Physical state: liquid - Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: control and 100 mg/l
- Sample storage conditions before analysis: all 0-hour samples (and duplicate 72-hour samples) stored at approximately -20 °C prior to analysis - Vehicle:
- no
- Details on test solutions:
- - 100 mg of test item was dissolved directly in culture medium and the volume adjusted to 1 litre to give a 100 mg/l stock solution
- stock solution was inoculated with algal suspension (13.2 ml) to give the required test concentration of 100 mg/l
- all solutions were 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
- Common name: freshwater alga
- Strain: CCAP 278/4
- Source (laboratory, culture collection): Culture collection of algae and protozoa (CCAP-, SAMS Research services Ltd., Scottish Marine Institute, Oban, Argyll, Scotaland
- Method of cultivation:
* in culture medium (replenished periodically)
* under constant aeration
* illumination at 21 ± 1°C - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
- Hardness:
- Not reported.
- Test temperature:
- 24 ± 1 °C
- pH:
- at initiation of test: 8.0 in control and 8.3 in 100 mg/l
after 72 hours exposure: 8.3 in control and 8.0 in 100 mg/l - Dissolved oxygen:
- Not reported.
- Salinity:
- Not applicable.
- Nominal and measured concentrations:
- nominal concentrations: 0 and 100 mg/l
measured concentrations:- Details on test conditions:
- TEST SYSTEM
- Test vessel: conical flasks
- Type (delete if not applicable): closed: plugged with polyurethane foam bungs
- Material, size, headspace, fill volume: glass, 250 ml, headspace not defined, 100 ml
- Aeration: no, closed system to prevent evaporation
- Initial cells density and culture preparation: 5 x 10E+03 cells per ml
- Control end cells density: mean from six replicates: 9.28E+05 cells per ml
- No. of vessels per concentration (replicates): six
- No. of vessels per control (replicates): six
- constantly shaken at approximately 150 rpm for 72 hours
- incubation in INFORS Multitron® Version 2 incubator
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: deionised water (Elga optima 15+ or Elga Purelab Option R-15 BP)
- Culture medium different from test medium: no
- Intervals of water quality measurement: at test initiation and 72h
OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH of culture medium: yes, to 7.5 ± 0.1 with NaOH or HCl
- Photoperiod: continuous lighting
- Light intensity and quality: 7000 lux, warm white lighting (380-730 nm)
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: cell densities were measured using a Coulter® Multisizer Particle Counter at 0, 24, 48 and 72 hours
TEST CONCENTRATIONS
- Spacing factor for test concentrations: limit test
- Range finding study:
* Test concentrations: 0.10, 1.0, 10, 100 mg/l
* Results used to determine the conditions for the definitive study: no effect on growth at the test concentrations of 0.10, 1.0, 10 and 100 mg/l- Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- 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:
- - Colour differences: at start of test all control and test cultures were observed to be clear colourless solutions. After the 72-h test period all control and test cultures were observed to be pale green dispersions.
- Results with reference substance (positive control):
- - ErC50(72h): 1.32 mg/l, 95% C.I.: 0.98-1.4 mg/l
- EyC50(72h): 0.48 mg/l, 95% C.I.: 0.43-0.54 mg/l
- NOEC based on growth rate: 0.25 mg/l
- LOEC based on growth rate: 0.50 mg/l
- the results were within the normal ranges for this reference item- Reported statistics and error estimates:
- Differences between the control and 100 mg/l groups were tested by means of a Student's t-test incorporating Bartlett's test for homogeneity of variance (Sokal and Rohlf 1981).
There were no statistically significant differences (p >= 0.05), between the control and 100 mg/l test group.- Validity criteria fulfilled:
- yes
- Conclusions:
- In this study, the freshwater algae Pseudokirchnierielle subcapitata was exposed to 100 mg/l of test substance for 72 hours. Based on the growth rate, the EC50 was determined to be > 100 mg/l and the NOEC was 100 mg/l.
Reference
Description of key information
The key value for acute toxicity of algae was obtained from a study exposing Pseudokirchnerella subcapitata to a single concentration of the test substance during 72 hours under GLP conditions and according to OECD 201.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 100 mg/L
- EC10 or NOEC for freshwater algae:
- 100 mg/L
Additional information
The well-designed growth inhibition study (Klimisch 1) was performed by Harlan Laboratories (Vryenhoef and Mullee, 2011). Pseudokirchnerella subcapitata was exposed to 100 mg/l of test substance during 72 hours and growth rate was monitored. The ErC50(72h) of > 100 mg/l and NOEC of 100 mg/l was found.
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