Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 213-059-4 | CAS number: 920-66-1
- 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:
- 24 - 27 Jul 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2017
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Version / remarks:
- 28 Jul 2011
- Qualifier:
- according to guideline
- Guideline:
- other: OECD 23 "Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures"
- Version / remarks:
- 23 Sep 2000
- GLP compliance:
- yes
Test material
- Reference substance name:
- 1,1,1,3,3,3-hexafluoropropan-2-ol
- EC Number:
- 213-059-4
- EC Name:
- 1,1,1,3,3,3-hexafluoropropan-2-ol
- Cas Number:
- 920-66-1
- Molecular formula:
- C3H2F6O
- IUPAC Name:
- 1,1,1,3,3,3-hexafluoropropan-2-ol
- Test material form:
- liquid
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Remarks:
- gas chromatography
- Details on sampling:
- - Concentrations: All concentration levels at the start of exposure, after 24 and 48 h, and at the end of exposure.
- Sampling method: Two additional replicates were prepared for sampling and analytical chemistry at 24 and 48 h. At the start of exposure as well as after 24 and 48 h, samples (100 mL) were taken from the separate replicates prepared for analytics. At the end of the test, samples (90 mL) were directly taken from the test vessels.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Test item solutions were prepared by measuring volume and taking account of the density of the test item (1.62 g/mL). A 100 mg/L stock solution was prepared by adding 0.065 mL test item below the surface of 1053 mL medium.
- Differential loading: No. The final test solutions were prepared by diluting the stock solution with medium. For the 100 mg/L concentration level, the test vessels were filled with undiluted stock solution.
- Controls: Medium without test item
- Evidence of undissolved material: The test solutions of all exposure levels were colorless and clear.
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: green freshwater microalga
- Strain: ATCC 22662
- Source: American Type Culture Collection (supply date: 30 Jun 1995)
- Age of inoculum: The inoculum was a 3 d old pre-culture, prepared under the same conditions as the test.
- Method of cultivation: Passage cultured under sterile conditions in the laboratory of the testing facility.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
Test conditions
- Test temperature:
- 22.5 - 23.0 °C
- pH:
- 7.8 - 8.0 (test start)
9.0 - 9.9 (test end) - Nominal and measured concentrations:
- Control, 1.00, 3.16, 10.0, 31.6, and 100 mg/L (nominal)
Control, 0.976, 3.06, 9.26, 30.4, and 97.2 mg/L (geometric mean measured) - Details on test conditions:
- TEST SYSTEM
- Test vessel: Sterilized 500 mL Erlenmeyer flasks
- Type: Closed, without headspace in order to avoid volatilisation of the test item.
- Initial cell density: 0.5E+04 cells/mL
- Control end cells density: 32E+04 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: Yes, OECD medium according to guideline
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Purified water
- Culture medium different from test medium: Culture medium same as test medium
- Intervals of water quality measurement: The pH was measured in a separate replicate at test start and in one test vessel of every test level at the end of the test. Incubation temperature and light intensity were measured at test start and then daily.
OTHER TEST CONDITIONS
- Light intensity: 88 - 91 µmol*m^-2*s^-1
- Other: Incubation with rotary shaking (approximately 100 rpm)
EFFECT PARAMETERS MEASURED:
- Determination of cell concentrations: Determination of biomass at the start and then every 24 h with a particle counter (Coulter Z2, Beckman Coulter, Inc.)
- Other: Appearance of cells (biological microscope, BX41 Olympus Corp.)
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 3.16
- Range finding study: Yes
- Test concentrations: 0.10, 1.00, 10.0, and 100 mg/L
- Results used to determine the conditions for the definitive study: Yes, from the results of the preliminary study, the definitive study was carried out with nominal test item concentrations ranging from 1.00 to 100 mg/L. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- 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
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 97.2 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- - Exponential growth in the control: Yes, the number of cells in the control increased by a factor of 60 or more by the end of the test.
- Observation of abnormalities: The condition of the cells in all exposure levels and in the control was normal.
- Effect concentrations exceeding solubility of substance in test medium: No - Results with reference substance (positive control):
- - Results with reference substance valid? Yes. The value is within the normal range (mean ± S.D. = 1.0 ± 0.20 mg/L, n = 31).
- ErC50 (0-3 d): 1.3 mg/L
- Other: The algae growth inhibition test with the reference substance and test organism is periodically conducted by the test facility. The last test dates from 22 - 25 May 2017 - Reported statistics and error estimates:
- Bartlett's test was used to determine the homogeneity of variance of the data.
A one-way ANOVA and Dunnett's multiple comparison test were used to determine the significant difference between the control and the exposure levels.
Statistical analysis was performed in Excel (Microsoft).
Any other information on results incl. tables
VALIDITY CRITERIA
The test fulfills the validity criteria defined by the guideline (Table 1).
The pH of the control varied more than the range indicated in the guideline (not more than 1.5). However, it was decided that the increase of pH in the control was due to the limit of the algae growth and the absence of gas exchange between outside and inside of the test vessel due to the closed test system. All other environmental condictions (except pH) were within the suitable range. Therefore, it was concluded that this study complied with the test guidelines.
Table 1: Validity criteria
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
The biomass in the control cultures should have increased exponentially by a factor of at least 16 within the 72-hour test period. |
The number of cells in the control increased by a factor of 60 or more by the end of the test. |
Yes |
The mean coefficient of variation for section-by-section specific growth rates (days 0-1, 1-2 and 2-3, for 72-hour tests) in the control cultures must not exceed 35% |
The mean coefficient of variation for section-by-section specific growth rates in the controls was 23%. |
Yes |
The coefficient of variation of average specific growth rates during the whole test period in replicate control cultures must not exceed 7% in tests with Pseudokirchneriella subcapitata and Desmodesmus subspicatus. For other less frequently tested species, the value should not exceed 10%. |
The coefficient of variation of specific growth rates in replicate controls was 1.2% and therefore does not exceed 7%. |
Yes |
ANALYTICAL RESULTS
The measured concentration of the test item in the test solutions were 0.998 – 102 mg/L (96.0 – 102% of nominal concentration) at the start of exposure, 1.00 – 98.5 mg/L (94.4 – 100% of nominal concentration) at 24 h, 0.956 – 94.8 mg/L (90.6 – 95.7% of nominal) at 48 h and 0.944 – 94.8 mg/L (89.9-94.8% of nominal concentration) at the end of exposure (Table 2). The measured concentrations of the test item were within ± 20% of the nominal concentration.
Table 2. Measured concentrations of test item in test solutions.
Nominal concentration [mg/L] |
Measured concentration [mg/L] (percentage of measured concentration versus nominal concentration %) |
||||
At the start |
24 h |
48 h |
At the end |
Geometric mean |
|
Control |
n.d. |
n.d. |
n.d. |
n.d. |
- |
1.00 |
0.998 (99.8) |
1.00 (100) |
0.956 (95.6) |
0.944 (94.4) |
0.976 (97.6) |
3.16 |
3.18 (101) |
3.09 (97.8) |
3.02 (95.7) |
2.98 (94.2) |
3.06 (96.9) |
10.0 |
9.60 (96.0) |
9.44 (94.4) |
9.06 (90.6) |
8.99 (89.9) |
9.26 (92.6) |
31.6 |
31.7 (100) |
30.5 (96.6) |
30.0 (95.0) |
29.7 (93.9) |
30.4 (96.2) |
100 |
102 (102) |
98.5 (98.5) |
94.8 (94.8) |
94.8 (94.8) |
97.2 (97.2) |
n.d.: < 0.247 mg/L
BIOLOGICAL RESULTS
The algal growth rate in the 100 and 31.6 mg/L exposure levels were significantly higher compared to the control. Algae growth in the other exposure levels were almost the same as in the control (Table 3).
Table 3. Growth rate and growth inhibition rate.
Nominal concentration [mg/L] |
No |
Growth rate [0 – 3d] |
Growth inhibition rate [%] |
Control |
A |
1.41 |
- |
B |
1.38 |
- |
|
C |
1.38 |
- |
|
D |
1.40 |
- |
|
E |
1.41 |
- |
|
F |
1.37 |
- |
|
Mean |
1.39 |
- |
|
S.D. |
0.0168 |
- |
|
1.00 |
A |
1.42 |
-2.2 |
B |
1.35 |
3.0 |
|
C |
1.38 |
0.70 |
|
Mean |
1.38 |
0.47 |
|
S.D. |
0.0362 |
2.6 |
|
3.16 |
A |
1.37 |
1.5 |
B |
1.38 |
0.59 |
|
C |
1.36 |
2.1 |
|
Mean |
1.37 |
1.4 |
|
S.D. |
0.0108 |
0.78 |
|
10.0 |
A |
1.40 |
-0.96 |
B |
1.42 |
-2.4 |
|
C |
1.45 |
-4.6 |
|
Mean |
1.43 |
-2.7 |
|
S.D. |
0.0255 |
1.8 |
|
31.6 |
A |
1.45 |
-4.5 |
B |
1.47 |
-5.4 |
|
C |
1.47 |
-5.8 |
|
Mean |
1.46 |
-5.2 |
|
S.D. |
0.00875 |
0.63 |
|
100 |
A |
1.48 |
-6.7 |
B |
1.51 |
-8.7 |
|
C |
1.47 |
-5.9 |
|
Mean |
1.49 |
-7.1 |
|
S.D. |
0.0202 |
1.4 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- For further details please refer to "Any other information on results incl. tables".
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.