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EC number: 609-271-5 | CAS number: 36609-29-7
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Remarks:
- The study on a similar substance serves as data source for the endpoint study record "TARGET - Biodegradation in water: screening tests_Capa203" and the justification for read-across is provided there.
- Adequacy of study:
- key study
- Study period:
- Not reported
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Study conducted to OECD 301B, GLP compliant
- Justification for type of information:
- Study serves as data source; read-across justification is found in corresponding Target record.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- no
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- Secondary (biological) activated sludge was obtained from the RWZI Horstermeer in Nederhorst den Berg, The Netherlands on January 13, 1993. The RWZI Horstermeer was an activated sludge plant treating predominantly domestic waste water. The dry weight of this inoculum appeared to be 4.0 mg/ml.
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 20 mg/L
- Based on:
- test mat.
- Initial conc.:
- 10 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Reference substance:
- acetic acid, sodium salt
- Key result
- Parameter:
- % degradation (TOC removal)
- Value:
- ca. 60
- Sampling time:
- 7 d
- Remarks on result:
- other: initial conc. 10 mg/L
- Parameter:
- % degradation (TOC removal)
- Value:
- ca. 84
- Sampling time:
- 28 d
- Remarks on result:
- other: initial conc. 10 mg/L
- Parameter:
- % degradation (TOC removal)
- Value:
- ca. 42
- Sampling time:
- 7 d
- Remarks on result:
- other: initial conc. 20 mg/L
- Parameter:
- % degradation (TOC removal)
- Value:
- ca. 56
- Sampling time:
- 28 d
- Remarks on result:
- other: initial conc. 20 mg/L
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The test substance CAPA 203 was classified as readily biodegradable.
- Executive summary:
A study was conducted to guideline OECD 301B using the substance CAPA 203. The reference compound (sodium acetate) degraded to 60% within 28 days. The total CO2-evolution in the inoculum blank at the end of the test was 37 mg, which was below the maximum acceptable amount according to the guideline (40 mg CO2L). The substance CAPA 203 was 60% degraded within 7 days when incubated at a concentration of 10 mg/L and 42% degraded when incubated at a concentration of 20 mg/L. On the basis of this result, CAPA 203 was classified as readily biodegradable.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- Not reported
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Study conducted to OECD 301B, GLP compliant
- Justification for type of information:
- It is considered appropriate to address the ready biodegradability data requirement for 2-oxepanone, polymer with 1,6-hexanediol by applying read-across from available experimental study data on 2-oxepanone, polymer with 1,4-butanediol. The source and target substances are low molecular weight polyester diols terminated by primary hydroxyl groups and are structurally similar in that they both contain 6-hydroxyhexanoic acid repeating units. The linking unit is 1,4-butanediol in 2-oxepanone, polymer with 1,4-butanediol and 1,6-hexanediol in 2-oxepanone, polymer with 1,6-hexanediol. The diols differ by two carbons in the aliphatic chain and are therefore sufficiently structurally similar to support a read-across approach. The source and target substances share similar physico-chemical properties in that both are liquids at room temperature and have similar water solubility and log Pow values. The substances are therefore sufficiently similar in terms of basic physico-chemical properties to support a read-across approach. A read-across justification document is attached in section 13.
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Parameter:
- % degradation (TOC removal)
- Value:
- ca. 60
- Sampling time:
- 7 d
- Remarks on result:
- other: initial conc. 10 mg/L
- Parameter:
- % degradation (TOC removal)
- Value:
- ca. 84
- Sampling time:
- 28 d
- Remarks on result:
- other: initial conc. 10 mg/L
- Parameter:
- % degradation (TOC removal)
- Value:
- ca. 42
- Sampling time:
- 7 d
- Remarks on result:
- other: initial conc. 20 mg/L
- Parameter:
- % degradation (TOC removal)
- Value:
- ca. 56
- Sampling time:
- 28 d
- Remarks on result:
- other: initial conc. 20 mg/L
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The target substance 2-oxepanone, polymer with 1,6-hexanediol (Capa-2047A) is estimated to be readily biodegradable, based on read-across from a reliable study testing Capa-203 (2-oxepanone, polymer with 1,4-butanediol).
- Executive summary:
A study was conducted to guideline OECD 301B using the substance Capa-203 (2-oxepanone, polymer with 1,4-butanediol). The reference compound (sodium acetate) degraded to 60% within 28 days. The total CO2-evolution in the inoculum blank at the end of the test was 37 mg, which was below the maximum acceptable amount according to the guideline (40 mg CO2L). The substance Capa-203 was 60% degraded within 7 days when incubated at a concentration of 10 mg/L and 42% degraded when incubated at a concentration of 20 mg/L. On the basis of this result, Capa-203 was classified as readily biodegradable.
The basic physico-chemical properties and chemical structural of the source substance Capa-203 and the target substance Capa-2047A (2-oxepanone, polymer with 1,6-hexanediol) are considered to be sufficiently similar to support a read-across approach. Therefore, the target substance CAPA 2047A is also concluded to be readily biodegradable.
Referenceopen allclose all
Table 1: Results of the biodegradation test with CAPA 203 and sodium acetate. The results are expressed as CO2 mg (cumulative) formed after 7, 14, 21, 28 and 29 days (n=2)
Concentration CAPA 203 (mg/L) |
Concentration Sodium acetate (mg/L) |
mg CO2 produced |
||||
7 days |
14 days |
21 days |
28 days |
29 days |
||
|
|
|
|
|
|
|
0 |
100 |
44.0 |
56.9 |
60.8 |
59.4 |
59.8 |
20 |
100 |
37.6 |
61.5 |
71.4 |
73.1 |
72.9 |
10 |
0 |
28.6 |
35.7 |
38.6 |
40.0 |
40.2 |
20 |
0 |
39.9 |
50.8 |
52.4 |
53.2 |
53.2 |
Table 2: Percentage degradation of 100 mg/L sodium acetate, 20 mg/L CAPA 203 in the presence of 100 mg/L sodium acetate and CAPA 203 at a concentration of 10 and 20 mg/L
|
% biodegradation |
||||
7 days |
14 days |
21 days |
28 days |
29 days |
|
|
|
|
|
|
|
sodium acetate (100 mg/L) |
44 |
57 |
61 |
60 |
60 |
|
|
|
|
|
|
CAPA 203 (20 mg/L) in the presence of sodium acetate (100 mg/L) |
-7 |
5 |
11 |
14 |
14 |
|
|
|
|
|
|
CAPA 203 (10 mg/L) |
60 |
75 |
81 |
84 |
84 |
|
|
|
|
|
|
CAPA 203 (20 mg/L) |
42 |
53 |
55 |
56 |
56 |
|
|
|
|
|
|
Table 3: Results of the biodegradability test
Concentration CAPA 203 (mg/L) |
Concentration Sodium acetate (mg/L) |
mg CO2 of absorbed in the period |
||||
0-7 days |
7-14 days |
14-21 days |
21-28 days |
28-29 days |
||
|
|
|
|
|
|
|
0 |
|
15.3 |
8.6 |
4.9 |
1.3 |
1.1 |
0 |
|
15.8 |
10.7 |
8.2 |
7.4 |
1.1 |
average |
|
15.6 |
9.7 |
6.6 |
4.4 |
1.1 |
|
|
|
|
|
|
|
|
100 |
80.3 |
22.1 |
10.2 |
3.1 |
1.9 |
|
100 |
38.8 |
23.0 |
10.8 |
2.8 |
1.1 |
|
average |
59.6 |
22.6 |
10.5 |
3.0 |
1.5 |
|
|
|
|
|
|
|
20 |
100 |
53.2 |
33.6 |
16.5 |
6.1 |
0.9 |
|
|
|
|
|
|
|
10 |
|
43.4 |
18.5 |
11.1 |
9.5 |
1.4 |
10 |
|
44.9 |
15.0 |
7.9 |
2.1 |
1.1 |
average |
|
44.2 |
16.8 |
9.5 |
5.8 |
1.3 |
|
|
|
|
|
|
|
20 |
|
74.8 |
19.6 |
3.7 |
1.9 |
1.1 |
20 |
|
36.2 |
21.6 |
12.7 |
8.5 |
1.1 |
average |
|
55.5 |
20.6 |
8.2 |
5.2 |
1.1 |
Table 1: Results of the biodegradation test with CAPA 203 and sodium acetate. The results are expressed asCO2mg (cumulative) formed after 7, 14, 21, 28 and 29 days (n=2)
Concentration CAPA 203 (mg/L) |
Concentration Sodium acetate (mg/L) |
mg CO2 produced |
||||
7 days |
14 days |
21 days |
28 days |
29 days |
||
|
|
|
|
|
|
|
0 |
100 |
44.0 |
56.9 |
60.8 |
59.4 |
59.8 |
20 |
100 |
37.6 |
61.5 |
71.4 |
73.1 |
72.9 |
10 |
0 |
28.6 |
35.7 |
38.6 |
40.0 |
40.2 |
20 |
0 |
39.9 |
50.8 |
52.4 |
53.2 |
53.2 |
Table 2: Percentage degradation of 100 mg/L sodium acetate, 20 mg/L CAPA 203 in the presence of 100 mg/L sodium acetate and CAPA 203 at a concentration of 10 and 20 mg/L
|
% biodegradation |
||||
7 days |
14 days |
21 days |
28 days |
29 days |
|
|
|
|
|
|
|
sodium acetate (100 mg/L) |
44 |
57 |
61 |
60 |
60 |
|
|
|
|
|
|
CAPA 203 (20 mg/L) in the presence of sodium acetate (100 mg/L) |
-7 |
5 |
11 |
14 |
14 |
|
|
|
|
|
|
CAPA 203 (10 mg/L) |
60 |
75 |
81 |
84 |
84 |
|
|
|
|
|
|
CAPA 203 (20 mg/L) |
42 |
53 |
55 |
56 |
56 |
|
|
|
|
|
|
Table 3: Results of the biodegradability test
Concentration CAPA 203 (mg/L) |
Concentration Sodium acetate (mg/L) |
mg CO2 of absorbed in the period |
||||
0-7 days |
7-14 days |
14-21 days |
21-28 days |
28-29 days |
||
|
|
|
|
|
|
|
0 |
|
15.3 |
8.6 |
4.9 |
1.3 |
1.1 |
0 |
|
15.8 |
10.7 |
8.2 |
7.4 |
1.1 |
average |
|
15.6 |
9.7 |
6.6 |
4.4 |
1.1 |
|
|
|
|
|
|
|
|
100 |
80.3 |
22.1 |
10.2 |
3.1 |
1.9 |
|
100 |
38.8 |
23.0 |
10.8 |
2.8 |
1.1 |
|
average |
59.6 |
22.6 |
10.5 |
3.0 |
1.5 |
|
|
|
|
|
|
|
20 |
100 |
53.2 |
33.6 |
16.5 |
6.1 |
0.9 |
|
|
|
|
|
|
|
10 |
|
43.4 |
18.5 |
11.1 |
9.5 |
1.4 |
10 |
|
44.9 |
15.0 |
7.9 |
2.1 |
1.1 |
average |
|
44.2 |
16.8 |
9.5 |
5.8 |
1.3 |
|
|
|
|
|
|
|
20 |
|
74.8 |
19.6 |
3.7 |
1.9 |
1.1 |
20 |
|
36.2 |
21.6 |
12.7 |
8.5 |
1.1 |
average |
|
55.5 |
20.6 |
8.2 |
5.2 |
1.1 |
Description of key information
One key study is presented, which shows that the read-across substance 2-oxepanone, polymer with 1,4-butanediol is readily biodegradable. The target substance 2-oxepanone, polymer with 1,6-hexanediol is therefore concluded to be readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
The basic physico-chemical properties and chemical structural of the source substance 2-oxepanone, polymer with 1,4-butanediol and the target substance 2-oxepanone, polymer with 1,6-hexanediol are considered to be sufficiently similar to support a read-across approach. The read-across substance 2-oxepanone, polymer with 1,4-butanediol has been found to be readily biodegradable with 60% degradation within 7 days when incubated at a concentration of 10 mg/L and 42% degradation when incubated at a concentration of 20 mg/L. On the basis of this result the target substance was classified as readily biodegradable.
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.