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EC number: 240-344-0 | CAS number: 16215-49-9
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2017-09-22 to 2018-05-09
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- Activated sludge from the municipal wastewater treatment plant AZV Staufener Bucht was used as inoculum with a concentration corresponding to 30 mg dry solids per litre. The treatment plant clarifies predominantly domestic wastewater and has a capacity of 140,000 inhabitant equivalents. Sampling date of activated sludge was on 4 October 2017. The dry solid content of the activated sludge was 4.5 g/L. lt was determined by weight measurements after drying at 105 °C for 5 hours (mean of triplicate measurements). The activated sludge was washed one time with tap water and one time with mineral medium by settling the sludge, decanting the supernatant and re-suspending the sludge.
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 20 mg/L
- Based on:
- TOC
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- A solution of the test item in a mineral medium, corresponding to 20 mg TOC/L, is inoculated with activated sludge (30 mg d. s./L). The test vessels are aerated by the passage of carbon dioxide-free air and are incubated under aerobic conditions in diffuse light for 28 days. Degradation is followed by determining the carbon dioxide produced and absorbed to sodium hydroxide via lC-measurement (lC= inorganic carbon).
TEST CONDITIONS
- Composition of medium: refer to "Any other information on material and methods incl. tables" below
- Test temperature: 21.2 - 24.0 °C
- pH: 7.4
- pH adjusted: no
CONTROL AND BLANK SYSTEM
In total three reactors containing the test item, three reactors containing only inoculum (blank), three reactors containing the reference compound and one reactor containing test item and reference compound (toxicity control) were set up.
- Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 18.97
- Sampling time:
- 28 d
- Details on results:
- The degradation of the toxicity control after 14 days was 58.7%. Therefore, the test item had no inhibitory effect on the inoculum according to the criterion of the guideline.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- The degradation percentage of the test item at the end of the test showed values between 13.2 and 30.5 %. The mean degradation extent on day 28 of the three replicates was app. 19.0 %.
Under the experimental conditions, dibutyl peroxydicarbonate was therefore not readily biodegradable (60 % of ThCO2 within a 10-d window) in the 28-day modified Sturm test. - Executive summary:
The ready biodegradability of dibutyl peroxydicarbonate (containing isododecane as stabiliser) was evaluated in a 28-day modified Sturm test according to the OECD guideline 301 B at an initial test substance concentration of 20 mg/L TOC.
The degradation percentage of the test item at the end of the test showed values between 13.2 and 30.5 %. The mean degradation extent on day 28 of the three replicates was 19.0 %. Under the conditions of the CO2 evolution test, the test item dibutyl peroxydicarbonat is not readily biodegradable.
Reference
Table 1: Ultimate biodegradation after x days [% of ThCO2]
Reactor |
Day |
0 |
4 |
7 |
11 |
14 |
21 |
28 |
29 |
7 |
Test flasks |
0 |
23.2 |
31 |
38.5 |
37.4 |
37.1 |
31.2 |
30.5 |
8 |
0 |
17.2 |
26.7 |
29.1 |
25.6 |
20.8 |
12.8 |
13.2 |
|
9 |
0 |
14.4 |
24 |
29.1 |
25 |
23 |
12.6 |
13.2 |
|
4 |
reference flasks |
0 |
60.8 |
74.8 |
80.6 |
81.9 |
79.6 |
82.2 |
79.9 |
5 |
0 |
72.7 |
82 |
82.3 |
88.4 |
91.8 |
92.5 |
92.5 |
|
6 |
0 |
67.4 |
81.6 |
84.1 |
86.3 |
86.2 |
92.6 |
90.9 |
|
10 |
Toxicity control |
0 |
43.3 |
54.1 |
57.9 |
58.7 |
54.5 |
51.1 |
51.5 |
11 |
abiotic control |
0 |
4 |
7.1 |
7.8 |
9.5 |
13.4 |
16.4 |
38.6 |
Table 2: Mean CO2-evolution of blank flasks after x days
Day |
0 |
4 |
7 |
11 |
14 |
21 |
28 |
29 |
CO2-evolution [mg/l] |
0 |
10.4 |
15.5 |
22.3 |
25.8 |
39.3 |
51.9 |
52.7 |
Description of key information
The test item dibutyl peroxydicarbonat is not readily biodegradable under the conditions of the CO2 evolution test according to OECD 301B.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
- Type of water:
- freshwater
Additional information
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.
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