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EC number: 601-419-7 | CAS number: 1162-60-3
- 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:
- 12 Jan 2018 - 22 Jan 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Version / remarks:
- 2006 (Annex 5 corrected 28 July 2011)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Guidance document on aquatic toxicity testing of difficult substances and mixtures, OECD series on testing and assessment number 23
- Version / remarks:
- 2000
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- (8R,9S,10R,13S,14S,17R)-17-ethynyl-17-hydroxy-13-methyl-1,2,8,9,10,11,12,14,15,16-decahydrocyclopenta[a]phenanthren-3-one
- EC Number:
- 608-630-3
- Cas Number:
- 31528-46-8
- Molecular formula:
- C20H24O2
- IUPAC Name:
- (8R,9S,10R,13S,14S,17R)-17-ethynyl-17-hydroxy-13-methyl-1,2,8,9,10,11,12,14,15,16-decahydrocyclopenta[a]phenanthren-3-one
- Test material form:
- solid: particulate/powder
- Details on test material:
- Appearance: Off-white powder
Test item storage: At room temperature
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: Control and all test concentrations
- Sampling method: 2.0 mL from the approximate centre of the test vessels at t=0 h, t=24 h and t=72 h
- Sample storage conditions before analysis: Samples were stored in a freezer (≤-15°C) until analysis at the analytical laboratory of the Test Facility.
- At the end of the exposure period, the replicates with algae were pooled at each concentration before sampling.
- Compliance with the quality criteria regarding maintenance of actual concentrations was checked by running a test vessel at the limit concentration (i.e. the undiluted SS prepared at 100 mg/L) but without algae and samples for analysis were taken at the start, after 24 hours of exposure and at the end of the test period.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Preparation of test solutions started with a loading rate of 100 mg/L applying a three-day period of magnetic stirring to ensure maximum dissolution of the test item in test medium. Thereafter, the aqueous Saturated Solution (SS) was collected by filtration through a 0.45 µm membrane filter (RC55, Whatman) and used as the highest test concentration. Lower test concentrations were prepared by subsequent dilutions of the SS in test medium. All test solutions were clear and colorless at the end of the preparation procedure.
After preparation, volumes of 50 mL were added to each replicate of the respective test concentration. Subsequently, 1 mL of an algal suspension was added to each replicate providing a cell density of 10^4 cells/mL.
- Controls: Test medium without test item or other additives
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Pseudokirchneriella subcapitata
- Strain: NIVA CHL 1
- Source: In-house laboratory culture
- Age of inoculum (at test initiation): 3 days
- Method of cultivation: Algae stock cultures were started by inoculating growth medium with algal cells from a pure culture on agar. The suspensions were continuously aerated and exposed to light in a climate room at a temperature of 21-24°C.
- Pre-culture: Three days before the start of the test, cells from the algal stock culture were inoculated in culture medium at a cell density of 1 x 10^4 cells/mL. The pre-culture was maintained under the same conditions as used in the test. The cell density was measured immediately before use.
- Stock culture medium: M1, according to NPR 6505 (“Nederlandse Praktijk Richtlijn no. 6505”)
- Pre-culture medium and test medium: M2, according to OECD 201
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
Test conditions
- Hardness:
- 0.24 mmol/L (24 mg CaCO3/L)
- Test temperature:
- 21 - 23 °C
- pH:
- At t=0 h: 8.1
At t=72 h: 8.3-8.4 - Nominal and measured concentrations:
- Nominal: 1.0, 10 and 100% of a saturated solution prepared at a loading rate of 100 mg/L
Measured concentration in undiluted satured solution: 1.2 mg/L (stable throughout the test duration). Effect parameters were based on initially measured concentrations. - Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL, all-glass, containing 50 mL of test solution
- Capped vessels were distributed at random in the incubator and daily repositioned. During incubation the algal cells were kept in suspension by continuous shaking.
- Initial cell density: 1 x 10^4 cells/mL
- Control end density (mean): 300 x 10^4 cells/mL
- 3 replicates of each 1.0 and 10% of saturated solution
- 6 replicates of the control and undiluted saturated solution
- 1 extra replicate of each test group for sampling purposes after 24 hours of exposure
- 1 or 2 replicates of each test concentration without algae.
GROWTH MEDIUM
- Standard medium used: yes, M2
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: M2, formulated using tap water purified by reverse osmosis
- Intervals of water quality measurement: pH: at the beginning and at the end of the test, for control and undiluted SS. Temperature: continuously in a temperature control vessel.
- Appearance of the cells: at the end of the final test, microscopic observations were performed on the highest test concentration to observe for any abnormal appearance of the algae compared to the control.
OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: no
- Photoperiod, light intensity and quality: Continuously using TLD-lamps with a light intensity of 86 µE/m^2/s
EFFECT PARAMETERS MEASURED
- Cell density at t=24, 48 and 72 h in the control and limit concentration. Intermediate concentrations were measured only at the end of the exposure period.
- Determination of cell concentrations: At the beginning of the test, cells were counted using a microscope and a counting chamber. Thereafter, cell densities were determined by spectrophotometric measurement of samples at 680 nm using a spectrophotometer with immersion probe (path length = 10 mm). Algal medium was used as blank and the extra replicates, without algae, as background for the treated solutions. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate (performed Jan 2018)
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1.2 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- growth rate
- Remarks on result:
- other: Measured concentration of 1.2 mg/L is considered the maximum soluble concentration of the test item in test medium at a loading rate of 100 mg/L
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- > 1.2 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- < 1.2 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- growth rate
- Remarks on result:
- other: Based on statistical significance
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1.2 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- growth rate
- Remarks on result:
- other: Based on biological relevance
- Details on results:
- - Exponential growth in the control: yes
- Observation of abnormalities: Microscopic observations at the end of the test revealed a normal and healthy appearance of the algal cells exposed to the undiluted SS when compared to the control.
- All water quality parameters remained within the requirements as laid down in the study plan throughout the test. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- EC50 for growth rate inhibition (72h-ErC50) was 0.86 mg/L (95% confidence interval 0.84 - 0.88 mg/L). The historical ranges for growth rate inhibition lie between 0.82 and 2.3 mg/L. The observed 72h-ErC50 for the algal culture tested corresponds with this range. - Reported statistics and error estimates:
- Statistical significance: Two-Sample T-Test, α=0.05, one-sided, smaller
The calculations were performed with ToxRat Professional v. 3.2.1. (ToxRat Solutions® GmbH, Germany).
Any other information on results incl. tables
Table 1: Test Samples
Time of sampling |
Date of sampling |
Date of |
Percentage of SS (b) |
Analyzed concentration |
Relative to |
0 |
15 Jan 2018 |
22 Jan 2018 |
0 |
n.d. |
|
|
|
|
100 |
1.21 |
|
|
|
|
100 (c) |
1.27 |
|
24 |
16 Jan 2018 |
22 Jan 2018 |
0 |
n.d. |
n.a. |
|
|
|
100 |
1.22 |
101 |
|
|
|
100 (c) |
1.29 |
102 |
72 |
18 Jan 2018 |
22 Jan 2018 |
0 |
0.000083 (d) |
n.a. |
|
|
|
100 |
1.20 |
99 |
|
|
|
100 (c) |
1.19 |
94 |
(a) Samples were stored in the freezer (≤ -15°C) until the day of analysis.
(b) Percentage of a saturated solution (SS) prepared at a loading rate of 100 mg/L.
(c) Without algae.
(d) Estimated value, calculated by extrapolation of the calibration curve.
n.a. Not applicable.
Table 2: growth Rate And Percentage Inhibition For The Total Test Period
Test item |
Mean |
Std. Dev. |
n |
%Inhibition |
Control |
1.901 |
0.0281 |
6 |
|
1.0 |
1.896 |
0.0287 |
3 |
0.251 |
10 |
1.871 |
0.0072 |
3 |
1.51 |
100 |
1.746 |
0.0148 |
6 |
8.1 *# |
* effect was statistically significant;#effect
biologically not relevant (<10%);
1effect was statistically not compared against the control.
Table 3: Growth Rate And Percentage Inhibition At Different Time Intervals
Test item |
n |
0 – 24 h |
24 – 48 h |
48 – 72h |
|||
Mean |
%Inhibition |
Mean |
%Inhibition |
Mean |
%Inhibition |
||
Control |
6 |
2.341 |
|
1.764 |
|
1.597 |
|
10 |
6 |
2.439 |
-4.2 |
1.473 |
16 |
1.326 |
17 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- See 'Overall remarks' for details on validity criteria.
- Conclusions:
- No biologically relevant inhibition of growth rate was recorded at any of the concentrations tested. The EC50 for growth rate inhibition (72h-ErC50) was beyond the range tested, i.e. exceeded a measured concentration of 1.2 mg/L being considered the maximum soluble concentration of the test item in test medium at a loading rate of 100 mg/L. The 72h-ErC10 was >1.2 mg/L. The 72h-NOEC for growth rate inhibition was 1.2 mg/L based on biological relevance and <1.2 mg/L based on statistical significance.
- Executive summary:
In a 72 h toxicity study conducted according to OECD guideline 201 and GLP principles, freshwater algae (Pseudokirchneriella subcapitata) were exposed to 1.0, 10 and 100% of saturated solutions prepared at a loading rate of 100 mg/L and an untreated control (triplicates for 1.0 and 10% of SS, 6 replicates for control and 100% of SS). Measured concentrations in the undiluted SS were stable throughout the test at 1.2 mg/L. Therefore, effect parameters were based on initially measured concentrations. The EC50 and EC10 for growth rate inhibition (72h-ErC50 and 72h-ErC10) were >1.2 mg/L being considered the maximum soluble concentration of the test item in test medium at a loading rate of 100 mg/L. The 72h-NOErC was 1.2 and <1.2 mg/L based on biological relevance and statistical significance, respectively. The study met all validity criteria, and is considered reliable without restriction.
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