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EC number: 500-099-5 | CAS number: 37625-56-2
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 4th September- 6th September 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted according to guidelines and GLP.
- Justification for data waiving:
- other:
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:
- 2 013
- Report date:
- 2013
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- Principles of method if other than guideline:
- N/A
- GLP compliance:
- yes
Test material
- Reference substance name:
- ε-Caprolactone, oligomeric reaction products with propylidynetrimethanol
- EC Number:
- 500-099-5
- EC Name:
- ε-Caprolactone, oligomeric reaction products with propylidynetrimethanol
- Cas Number:
- 37625-56-2
- Molecular formula:
- (C6H14O3)x.C6H10O2 (x=0-6)
- IUPAC Name:
- 2-Oxepanone, polymer with 2-ethyl-2-(hydroxymethyl)-1,3-propanediol
- Test material form:
- gas under pressure: refrigerated liquefied gas
- Details on test material:
- Clear, colourless liquid
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
N/A
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- pH and dissolved oxygen was monitored at the start and end of the test period (0 and 48h) in all of the test solutions. The test substance concentration was monitored for stability using the lowest and highest test concentrations at the start and at the end of the test (at 0 and 48h). A sample from the stock solution was also taken at test initiation. Immobilization was determined at 24h and 48h.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- A fresh stock solution was prepared on the day of the test start. 1000 mg of the test item was added to 1000 ml aerated reconstituted water and stirred for 10 minutes. To remove the nonwater soluble fraction of the test item from the test solution, the solution was filtered through a 0.45 um cellulose acetate filter (pre-boiled in order to remove any traces of external carbon). The acquired water phase (loading rate 1000 mg/l) was then used as a stock solution, from which the test concentrations were diluted using aerated M7-media. M7-media alone was used as the control solution.
M7-media was prepared according to OECD TG no. 202 (table 2 and 3). The M7-media had a pH of 7.8±0.2 and a theoretical hardness of 250±25 mg/I (expressed as CaC03).
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- The Daphnia magna culture is a Clone-A originating from the Norwegian Institute of Water Research (NIVA), Norway. The Clone-A has been identified by genotyping.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- N/A
Test conditions
- Hardness:
- 250±25 mg/I theoretical
- Test temperature:
- 20± 1 deg C
- pH:
- 7.7-7.9
- Dissolved oxygen:
- 85-101 %
- Salinity:
- N/A
- Nominal and measured concentrations:
- Nominal loading rate 28, 56, 113, 225, 450 and 900 mg/l. Measured concentrations at 0 hours for the stock solution, 28 and 900 mg/l were 230, 18, 200 mg/l respectively, at 28 hours measured concentrations were 17 and 200 mg/l (stock solution was not analysed).
- Details on test conditions:
- The animals were incubated in glass petri dishes (50 ml) with 25 ml test solution. Four replicates were used, both for the control and for the test concentrations, with 5 animals in each. The Petri dishes were placed in a thermo constant room at a temperature of 20± 1.0 C and with a light rhythm of 16 hours light: 8 hours darkness.
- Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 900 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: N/A
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 900 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: N/A
- Duration:
- 24 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 900 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: N/A
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 113 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: N/A
- Details on results:
- The criteria for validity of the tests according to OECD 202 were met.
- Results with reference substance (positive control):
- A reference test carried out with potassium dichrominate gave an EC50 of 1.3 mg/I, which confirmed that the culture was suitable as a test organism according to OECD guideline 202.
- Reported statistics and error estimates:
- None reported.
Any other information on results incl. tables
Table 1. Imobilised Daphnia magna at 24 and 48 hours
Conc. Loading rate/mg/l |
Number of immobilised Daphnia magna |
|
|
|
|
|||||||
24 and 48 hours |
|
|
|
|
||||||||
1 |
2 |
3 |
4 |
total |
total |
% immobilised |
% immobilised |
|||||
|
24 |
48 |
24 |
48 |
24 |
48 |
24 |
48 |
24 |
48 |
24 |
48 |
Control |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
0 |
10 |
28 |
0 |
0 |
0 |
1 |
1 |
1 |
0 |
0 |
1 |
2 |
5 |
10 |
56 |
0 |
2 |
0 |
0 |
0 |
1 |
1 |
1 |
1 |
4 |
5 |
20 |
113 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
225 |
1 |
1 |
0 |
0 |
0 |
0 |
0 |
2 |
1 |
3 |
5 |
15 |
450 |
0 |
1 |
0 |
1 |
0 |
1 |
0 |
0 |
0 |
3 |
0 |
15 |
900 |
0 |
0 |
1 |
4 |
0 |
1 |
0 |
1 |
1 |
6 |
5 |
30 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The toxicity of Capa 3050 to the water flea was determined in a static 48 hour study. Daphnia magna were exposed to nominal loading rates of Capa 3050 between 28 and 900 mg/l . The 48 hour EC50 was >900 mg/l based on nominal exposure loading rates.
- Executive summary:
The toxicity of Capa 3050 to the water flea, Daphnia magna, was determined in a 48 hour static acute immobilisation test conducted according to OECD guideline 202. The daphnids were exposed to Capa 3050 at nominal loading rates of 28, 56, 113, 225, 450 and 900mg/l. Stability of Capa 3050 in the test media was confirmed by TOC analysis at the lowest and highest concentration at the start and end of test period. The 48 hour EC50 was >900 mg/l based on nominal loading rates.
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