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EC number: 216-059-2 | CAS number: 1484-84-0
- 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
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2016
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 2-piperidin-2-ylethanol
- EC Number:
- 216-059-2
- EC Name:
- 2-piperidin-2-ylethanol
- Cas Number:
- 1484-84-0
- Molecular formula:
- C7H15NO
- IUPAC Name:
- 2-piperidin-2-ylethanol
- Test material form:
- not specified
Constituent 1
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, non-adapted
- Details on inoculum:
- Inoculum of the aqueous phase of non-adapted activated sludge.
- Duration of test (contact time):
- 28 d
- Details on study design:
- The activated sludge was washed twice with chlorine free tap water. After the second washing the settled sludge was resuspended in mineral salts medium and was maintained in an aerobic condition by aeration for 2 hours. Thereafter the sludge was homogenized with a blender. After sedimentation the supernatant was decanted and maintained in an aerobic condition by aeration with CO2 free air until test start. 10 mL/L of this mixture were used to initiate inoculation.
Results and discussion
% Degradation
- Sampling time:
- 28 d
- Remarks on result:
- readily biodegradable based on QSAR/QSPR prediction
- Details on results:
- The adaptation phase of the functional control changed within 4 days into the degradation phase (degradation 10 %). The course of the degradation was rapid and the functional control reached the pass level of 60 % within 11 days and a maximum biodegradation of 82 % on day 28. The validity criterion degradation k 60 % after 14 days is fulfilled.In the toxicity control containing both test and reference item a biodegradation of 58 % was determined within 14 days and it came to 89 % after 28 days. The biodegradation of the reference item was not inhibited by the test item in the toxicity control.
The biodegradation of the test item is shown graphically in Figure 1 in comparison to the readily degradable functional control and the toxicity control. The mean of test item replicates reached the 10 % level (beginning of biodegradation) within 8 days. The 60 % pass level was reached by both test item replicates within 25 days. The mean biodegradation after 28 days was 97 %.
Under the test conditions the test item is classified as readily biodegradable within the 28 day period of the study, but without complying to the 10-day-window.In the inoculum control the total CO2 production was 26.8 mg CO2/L after 28 days.
Any other information on results incl. tables
Table 2:CO2-Production and Biodegradation after 28 Days
CO2-Production |
Functional Control |
Test 1 |
Item 2 |
Toxicity Control |
Net [mg/3 L] |
104.2 |
110.2 |
112.8 |
215.4 |
[mg/L] |
34.7 |
36.7 |
37.6 |
71.8 |
Theor. [mg/3 L] |
127.8 |
114.7 |
242.5 |
|
[mg/L] |
42.6 |
38.2 |
80.8 |
|
Degradation [%] |
82 |
96 |
98 |
89 |
Table 3:CO2-Production and Biodegradation in the Inoculum Control, the Functional Control and the Toxicity Control
Study |
Date |
Inoculum [mg CO2/3 L] mv |
[mg CO2/3 Gross |
Functional L] Net Sum |
Control Degr. [%] |
[mg CO2/3 Gross |
Toxicity Control L] Net Sum |
Degr. [%] |
1 |
2016-04-01 |
4.1 |
4.8 |
0.7 |
1 |
12.7 |
8.6 |
4 |
4 |
2016-04-04 |
12.2 |
36.4 |
24.9 |
19 |
53.9 |
50.3 |
21 |
6 |
2016-04-06 |
8.1 |
35.1 |
51.9 |
41 |
41.4 |
83.6 |
34 |
8 |
2016-04-08 |
6.6 |
23.1 |
68.4 |
54 |
22.8 |
99.8 |
41 |
11 |
2016-04-11 |
7.6 |
20.6 |
81.4 |
64 |
21.9 |
114.1 |
47 |
14 |
2016-04-14 |
7.7 |
14.6 |
88.3 |
69 |
34.7 |
141.1 |
58 |
18 |
2016-04-18 |
7.5 |
12.8 |
93.6 |
73 |
27.6 |
161.2 |
66 |
21 |
2016-04-22 |
9.8 |
13.4 |
97.2 |
76 |
32.1 |
183.5 |
76 |
25 |
2016-04-25 |
5.6 |
7.9 |
99.5 |
78 |
25.5 |
203.4 |
84 |
28 |
2016-04-28 |
6.9 |
8.6 |
101.2 |
79 |
15.7 |
212.2 |
88 |
29* |
2016-04-29 |
4.3 |
7.3 |
104.2 |
82 |
7.5 |
215.4 |
89 |
Degr. = degradation mv = mean value *) results of last two gas wash bottles
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Under the test conditions the test item is classified as
readily biodegradable
within the 28 day period of the study, but without complying to the 10-day-window.
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