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EC number: 213-860-9 | CAS number: 1038-28-4
- 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 microorganisms
Administrative data
- Endpoint:
- toxicity to microorganisms
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Feb 1996
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: According to DIN guideline under GLP
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 999
- Report date:
- 1999
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- DIN 38412-8 (Pseudomonas Zellvermehrungshemmtest)
- Deviations:
- no
- Principles of method if other than guideline:
- Not relevant
- GLP compliance:
- yes
Test material
- Reference substance name:
- (±)-13-ethyl-3-methoxygona-2,5(10)-dien-17β-ol
- EC Number:
- 213-860-9
- EC Name:
- (±)-13-ethyl-3-methoxygona-2,5(10)-dien-17β-ol
- Cas Number:
- 1038-28-4
- Molecular formula:
- C20H30O2
- IUPAC Name:
- 11a-ethyl-7-methoxy-1H,2H,3H,3aH,3bH,4H,5H,6H,9H,9bH,10H,11H,11aH-cyclopenta[a]phenanthren-1-ol
- Details on test material:
- - Name of test material (as cited in study report): Ethyldienol
- Analytical purity: 80.9 - 93.9%
- Lot/batch No.: 15003801-07 (mix of 7 batches)
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
Test solutions
- Vehicle:
- no
Test organisms
- Test organisms (species):
- Pseudomonas putida
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 16 h
Results and discussion
Effect concentrations
- Duration:
- 16 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 200 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Remarks on result:
- other: saturated solution
Any other information on results incl. tables
Table 1: Mean values of turbidity (expressed as TE/F) and growth inhibition of Pseudomonas putida as a function of the
concentration (n=3) of ZK 47569
Dilution of ZK 47569 | TE/F [mean value (16 hours)] | Growth inhibition (%) |
Control | 93 | 0 |
1:160 | 98 | -5 |
1:80 | 91 | 2 |
1:40 | 76 | 18 |
1:20 | 55 | 41 |
1:10 | 64 | 31 |
1 :5 | 53 | 43 |
1:2,5 | 43 | 54 |
Saturated | 45 | 52 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Since the growth inhibition was not concentration-related at dilutions of 1:10 and the higher
concentration, it was difficult to interpret the results. Therefore, another test with ZK 47569 was
performed. No inhibition of growth was observed in that study (Schering report X 131) which was
considered valid. Therefore, the results of this test are not further evaluated. - Executive summary:
The purpose of this study was to determine the growth inhibition of Pseudomonas putida under
exposure to Ethyldienol. The test was conducted in agreement with the DIN standard 38412, L8,
"Wachstumshemmtest mit dem Bakterium Pseudomonas putida".
200 mg of the test substance were suspended in 1000 ml demineralized water under constant stirring tor
24 hours. In order to prepare the test solutions, this suspension was filtered. This solution was
used as the highest test concentration and was further diluted 1 :2.5, 1 :5, 1: 10, 1 :20, 1 :40, 1 :80
and 1 :160. Additionally, one control without the test substance was used. All test solutions including the control were incubated in triplicate. Furthermore, for each test concentration one test vessel was incubated without addition of the
inoculum in order to analyse the inherent turbidity of the test compound.
The concentrationof the saturated, filtered solution was estimated by a TOC-analysis and
subsequent calculation based on the molecular formula.
According to the results of a TOC-analysis, the saturated, filtered solution has a concentration of < 1 mg/L.
As a parameter for the growth of the bacterial population, theturbidity of the test and control
solutions was analysed photometrically at a wave-Iength of 436 nm.
The measurements showed a growth decrease in all solutions except the 1 :160 dilution in
comparison with the control group.
However, the control growth exceeded the required minimum of the DIN standard only by
3% and therefore, it is doubtful, whether the observed reduction of growth was compound related,
since it was not concentration-related at dilutions of 1:10 and lower.
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