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EC number: 271-846-8 | CAS number: 68609-97-2
- 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
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2006
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study performed according to OECD guideline
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
- Report date:
- 2006
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Details on test material:
- Alkyl (C12-C14) glycidyl ether
Label: Epoxide 8
51% C12 Glycidyl ether
21% C14 Glycidyl ether
5% C16 Glycidyl ether
13% N +1's
4% alpha addition Products
94% total active (Label claim)
- Physical state: Clear colorless
- Storage condition of test material: ambient
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- Samples of each test group were saved for dose verification analysis. HPLC was used to analyze these
samples. Results from these analyses indicated that very little detectable material dissolved into the
solution, likely due to the test material’s low solubility. The method indicated little difference in actual
concentration among all of the test groups. Overall, the test demonstrated a good dose-response;
therefore, the nominal test concentrations were used in data analysis.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- Algal stock culture medium (Woods Hole) with EDTA up to 0.300 mg/L
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Source (laboratory, culture collection): Stillmeadow, Inc. cultures
- Age of inoculum (at test initiation): Mass culture initiated 3 - 7 +/- 1 days prior to dosing
- Density: initial cell density was 10000 cells/mL
- Method of cultivation: six days prior to testing, 900 mL of autoclaved algal stock culture medium was inoculated. This mass culture was placed in a 21 - 25 +/- 2°C environemental chamber and maintained on continuous aeration.
Study design
- Test type:
- other: constant agitation (shaker table 100 cycles/minute)
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Post exposure observation period:
- none
Test conditions
- Test temperature:
- 21 - 25 +/- 2°C
- pH:
- 7.0 to 9.6 at termination
- Dissolved oxygen:
- Test containers received conctant aeration
- Nominal and measured concentrations:
- nominal concentrations: 500 mg/L, 1000 mg/L, 2000 mg/L, 4000 mg/L and 8000 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 250-mL sterile Erlenmeyer flasks with stoppers and aeration tubing
- Type (delete if not applicable): closed
- Material, size, headspace, fill volume: 250 mL sterile Erlenmeyer flasks
- Aeration: constant
- Initial cells density: 10000 cells/mL
- Control end cells density: increased by a factor greather than 16 for the vehicle control
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 3
- No. of vessels per vehicle control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes, Algal stock culture medium (Woods hole) with EDTA up to 0.300 mg/L
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Freshwater
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: No
- Photoperiod: Continuous lighting
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: daily using a hemacytometer
- Chlorophyll measurement: No
TEST CONCENTRATIONS
- Spacing factor for test concentrations: factor 2
- Range finding study
- Test concentrations: 0.1 mg/L, 1.0 mg/L, 10 mg/L, 100 mg/L, 500 mg/L and 1000 mg/L
- Results used to determine the conditions for the definitive study: No detailed results given for the dose range findings but 500 mg/L was selected as the lowest dose level to be used in the main study. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 72 h
- Dose descriptor:
- IC50
- Effect conc.:
- 843.75 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- cell number
- Remarks on result:
- other: 95% CL of 582.44 - 1097.71 mg/L
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 500 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- cell number
- Details on results:
- The mean cells counts of the test concentration containers were compared to the control counts. The test concentration that resulted in 50% inhibition (IC50) was determined to be 843.75 mg/L with 95% CL of 582.44 - 1097.71 mg/L. The NOEC was determined to be 500 mg/L.
HPLC was used to analyse the dose levels. Results indicated that very little detectable material dissolved into the solution, likely due to the test material's low solubility. The method indicated little difference in actual concentration among all test group. The nominal test concentrations were used in data analysis. Since the control density increased by a factor greater than 16 and the coefficient of correlation was < 20%, the test is considered to be valid. - Results with reference substance (positive control):
- All three replicates showed 0 cells/ml at 24, 48, and 72 hours
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- IC50 = 843.75 mg/L
NOEC = 500 mg/L
Since the water solubility of the substance was determined to be 0.483 mg/L, the IC50 is > solubility concentration. - Executive summary:
This study was conducted to determine the toxic effects of Alkyl (C12-C14) glycidyl ether; CAS RN
68609-97-2 (hereafter referred to as Alkyl glycidyl ether) on the growth of the freshwater algae
Selenastrum capricornutum in a 72-hour test.
The test substance concentrations of 500, 1000, 2000, 4000, and 8000 mg/L (based on a preliminary
range-finding test) were administered to the test system, Selenastrum capricornutum, in sterile medium.
For each test concentration, three test containers containing the freshwater algae (initial cell density of
10,000 cells/mL) were treated with the appropriate concentration of the test substance. A control group
consisted of six test containers containing sterile medium and the test culture only. A positive control
group consisted of three replicates treated with 10 mg/L potassium dichromate. The cell density in each
test and control container was measured daily using a hemacytometer. The pH of each test and control
container was determined at test termination. The test was terminated after 72 ± 2 hours of exposure.
The mean cell counts of the test concentration containers were compared to the control counts. The test
concentration that resulted in 50% inhibition (IC50) was determined to be 843.75 mg/L with 95%
confidence limits of 582.44-1097.71 mg/L. The NOEC (No Observed Effect Concentration) was
determined to be 500 mg/L.
HPLC was used to analyse the dose levels. Results indicated that very little detectable material dissolved into the solution, likely due to the test material's low solubility. The method indicated little difference in actual concentration among all test group. The nominal test concentrations were used in data analysis. Since the control density increased by a factor greater than 16 and the coefficient of correlation was < 20%, the test is considered to be valid.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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