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EC number: 269-122-1 | CAS number: 68187-75-7
- 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
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- from 20-OCT-2009 to 05-FEB-2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: the study was performed according to OECD guideline and GLP
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- yes
- Remarks:
- The concentration of NaHCO3 was increased to be twice of that indicated in the Guideline 201. This concentration has been found to be optimal.
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Oils, fish, oxidized
- EC Number:
- 269-122-1
- EC Name:
- Oils, fish, oxidized
- Cas Number:
- 68187-75-7
- Molecular formula:
- Not necessary
- IUPAC Name:
- Triglycerides C12-24, even, saturated and unsaturated, oxidized
- Details on test material:
- - Name of test material (as cited in study report): Triglycerides, C12-24, saturated and unsaturated, oxidized- Substance type: UVCB- Physical state: liquid- Stability under test conditions: stable- Storage condition of test material: at room temperature, protected from light
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 0, 100 mg/L- Sampling method: data not available- Sample storage conditions before analysis: data not available
Test solutions
- Vehicle:
- no
- Details on test solutions:
- The test item was introduced into the test solutions using aqueous extracts („WAFs“) from the test item as follows: First, a stock solution of the test item was prepared in dichloromethane. An aliquot of this stock solution was given into the the glass vessel for preparation of the aqueous extracts. After evaporation of the solvent the respective amount of ultrapure water was added. Then, the suspension was shaken on a shaking machine for 24 h at ≈130 rpm at room temperature, respectively. During that time an equilibration between the test item and the water was considered to be achieved. After 24h, shaking was stopped, and the suspensions were filtered through glass fibre filter. The eluates („WAFs“) were used directly without any further dilution steps.
Test organisms
- Details on test organisms:
- TEST ORGANISM- Common name: green alga- Strain: Desmodesmus subspicatus CHODAT- Source (laboratory, culture collection): Sammlung von Algenkulturen, Pflanzen¬physiologi¬sches Institut der Universität Göttingen [SAG], Strain-No. 86.81- Age of inoculum (at test initiation): 3 days- Method of cultivation: The algae are cultivated under aseptic conditions.ACCLIMATION- Acclimation period: - Culturing media and conditions (same as test or not): same as test- Any deformed or abnormal cells observed: data not available
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
- Post exposure observation period:
- none
Test conditions
- Hardness:
- data not available
- Test temperature:
- The temperature was constant at 25°C
- pH:
- See table 1
- Dissolved oxygen:
- data not available
- Salinity:
- not applicable (freshwater)
- Nominal and measured concentrations:
- nominal concentrations: 0 and 100 mg/Lmeasured concentrations: 0 and 25.2 mg/L at T0, 0 and 21.9 at T72See table 2
- Details on test conditions:
- TEST SYSTEM- Test vessel: 50 mL-glass-cylinders, heat sterilized- Material, size, headspace, fill volume: filled with 50 mL- Aeration: In order to assure the input of CO2, the test solutions were stirred by means of a magnetic stirrer for the duration of 15 minutes per hour- Initial cells density: 2.64*10E3 cells/mL- Control end cells density: 7.11*10E5 cells/mL- No. of vessels per concentration (replicates): 7- No. of vessels per control (replicates): 7GROWTH MEDIUM- Standard medium used: yesOTHER TEST CONDITIONS- Sterile test conditions: yes- Adjustment of pH: no- Photoperiod: 24/24h under constant light- Light intensity and quality: illumination rate of >=120 μE/m2s ([~8000 Lux]EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :- Determination of cell concentrations: the increase in biomass was determined using a spectrophotometer after 24, 53.25, and 72 h . As a measure for the biomass the absorbance of the test solutions measured at 578 nm was used.TEST CONCENTRATIONS- Spacing factor for test concentrations: not applicable- Justification for using less concentrations than requested by guideline: limit test at 100 mg/L- Range finding study- Test concentrations: 0 1, 10, 100 mg/L- Results used to determine the conditions for the definitive study: no effect observed at 100 mg/L
- Reference substance (positive control):
- not specified
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- - Exponential growth in the control (for algal test): yes- Observation of abnormalities (for algal test): data not available
- Results with reference substance (positive control):
- not applicable
- Reported statistics and error estimates:
- not applicable
Any other information on results incl. tables
The following individual Cell Numbers were obtained:
Time t0 | Control | 100 mg/L | |
|
| 2.64*103 | 2.64*103 |
|
| 2.64*103 | 2.64*103 |
|
| 2.64*103 | 2.64*103 |
|
| 2.64*103 | 2.64*103 |
|
| 2.64*103 | 2.64*103 |
|
| 2.64*103 | 2.64*103 |
|
| 2.64*103 | 2.64*103 |
Mean Values: | 2.64*103 | 2.64*103 |
Time t24h | Control | 100 mg/L | |
|
| 2.08*104 | 2.28*104 |
|
| 2.47*104 | 1.30*104 |
|
| 2.28*104 | 2.67*104 |
|
| 2.08*104 | 1.49*104 |
|
| 2.47*104 | 1.49*104 |
|
| 2.28*104 | 1.49*104 |
|
| 2.08*104 | 1.49*104 |
Mean Values: | 2.25*104 | 1.75*104 |
Time t53.25h | Control | 100 mg/L | |
|
| 2.35*105 | 2.79*105 |
|
| 2.37*105 | 3.13*105 |
|
| 2.43*105 | 2.70*105 |
|
| 2.35*105 | 2.74*105 |
|
| 2.58*105 | 2.85*105 |
|
| 2.82*105 | 2.81*105 |
|
| 2.62*105 | 2.81*105 |
Mean Values: | 2.50*105 | 2.83*105 |
Time t72h | Control | 100 mg/L | |
|
| 9.51*105 | 1.01*106 |
|
| 7.84*105 | 1.20*106 |
|
| 8.50*105 | 1.10*106 |
|
| 7.84*105 | 1.06*106 |
|
| 8.28*105 | 1.12*106 |
|
| 1.02*106 | 1.07*106 |
|
| 8.39*105 | 1.07*106 |
Mean Values: | 8.65*105 | 1.09*106 |
Nominal Concentration of the Test Item [mg/L] | Growth Rates (day-1) | Inhibition of the Growth Rate after 72h [%] | Yield after 72h1) | Inhibition of the Yield after 72h [%] |
Control (0) | 1.930 | - | 8.62*105 | - |
100 | 2.008 | -4.02) | 1.09*106 | -26.12) |
2)negative values indicate activation of growth
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- The test is considered valid as all conditions for validity were met
- Conclusions:
- 72-hr EL50 (growth rate/yield) > 100 mg/L72-hr NOELR (growth rate/yield) > 100 mg/L
- Executive summary:
The chronic toxicity of“Triglycerides, C12-24, even, saturated and unsaturated, oxidized“ towards algae was tested according to OECD-Guideline No. 201, in the Version dated 23-March 2006. The toxic effect was investigated by determination of the inhibition of the growth rate of the algae and the yield during the exposure period of 72 h. As the test item is poorly water-soluble, it was tested using aqueous extracts (“WAFs”) from up to 100 mg test item/L (final concentration). The main test was performed as a limit test using 100 mg/L as the sole test concentration because within the screening-test there was no negative effect up to that concentration. As a conclusion of the analytical part of this study, recoveries of the concentrations determined after 72h were ≥ 80% of those determined after 72h, and therefore the effective concentrations are based on the nominal concentrations of the WAFs determined.
From the results of the main test, toxic effects were determined with the following values:
On the Basis of the Nominal Loading Rates1)tested
Yield (0 - 72 h)
EC10 >100
EC20 >100
EC50 >100
LOEC >100
NOEC ≥ 100
Growth rate (0 - 72h)
EC10 >100
EC20 >100
EC50 >100
LOEC > 100
NOEC ≥ 100
The test is considered valid as all conditions for validity were met.
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