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EC number: 252-669-5 | CAS number: 35674-68-1
- 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:
- 2002-02-08
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study with abridged report
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 002
- Report date:
- 2002
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Version / remarks:
- (vers. 1992)
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Zinc bis[12-hydroxyoctadecanoate]
- EC Number:
- 252-669-5
- EC Name:
- Zinc bis[12-hydroxyoctadecanoate]
- Cas Number:
- 35674-68-1
- Molecular formula:
- C18H36O3.1/2Zn
- IUPAC Name:
- zinc bis(12-hydroxyoctadecanoate)
- Test material form:
- other: solid
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not applicable
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): municipal sewage treatment plant (67435 Neustadt Wstr., Germany), aeration tank, sample from 2002-02-06
- Pretreatment: activated sludge was aerated continuously and wash with drinking water and OECD-media
- Concentration of sludge: the dry residue was determined to be 7.28 g suspended solids/L, the concentration for testing was 25 mg solids/L - Duration of test (contact time):
- 29 d
Initial test substance concentration
- Initial conc.:
- 20 mg/L
- Based on:
- other: calculated organic carbon content
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- TEST CONDITIONS
- Composition of medium: mineral medium acc. to OECD
- Solubilising agent (type and concentration if used): none
- Test temperature: room temperature (20 +/- 1°C)
- pH: no data
- pH adjusted: no data
- Suspended solids concentration: 25 mg solids/L
- Test vessels: "Woulffe'sche bottles" 5 L volume
- Test volume: 3000 mL each
- Continuous darkness: no data
TEST SYSTEM
- Sample preparation: the org. carbon content was calculated to be 68.7 %
- Culturing apparatus: aeration with clean, moistened CO2-free air during the test
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: aeration with clean, moistened CO2-free air for 24 h before testing
- Measuring equipment: IC measurement of the emitted CO2 wit a TOC 5050A;
- Test performed in closed vessels due to significant volatility of test substance: no data
- Test performed in open system: no data
- Details of trap for CO2 and volatile organics if used: discharched air was trapped in 0.25 M NaOH solution (one trap followed by a second one)
SAMPLING
- Sampling frequency: at day 2, 4, 6, 8, 10, 13, 17, 21, 28, and 29 of the study
- Sampling method: for the IC measurement 0.5 or 1 ml solution were sampled from the first of the two NaOH traps; on day 29 both bottles were sampled and the IC results were summed up
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes
- Abiotic sterile control: yes, without inoculum
- Toxicity control: testsubstance + aniline
STATISTICAL METHODS: according to guideline
Reference substance
- Reference substance:
- aniline
Results and discussion
- Preliminary study:
- no data
- Test performance:
- No unusual observations during test reported.
% Degradationopen allclose all
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 14.5
- Sampling time:
- 4 d
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 53.5
- Sampling time:
- 13 d
- Remarks on result:
- other: end of 10 d window
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 71.4
- Sampling time:
- 28 d
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 72
- Sampling time:
- 29 d
- Details on results:
- - The 10 day window begins at day 3 (graphically determined). At day 13 53 % was degraded. At the end of the test 72 % was degraded. Thus, the 60 % pass level within the 10 day window was failed.
- Abiotic degration was 4 %.
- Validity: The test is considered valid, as
- the difference of extremes of replicate values of the removal of the test item at the end of the test is less than 20%,
- the percentage degradation of the reference item has reached the pass level of 60% by day 14,
- the total CO2 production of the blind trial was 25 mg CO2/L (mean value)
- Toxicity: If the total degardation in the toxicity test is below 25 %, the test substance is regared as toxic. In this study the total degradation was 49 % in in the toxicity test. However, since the theoretical degradation (mean value of reference and test approach) is 75%, an inhibition of degradation by the test substance was assumed.
BOD5 / COD results
- Results with reference substance:
- The reference substance aniline was degraded to 72 % within 10 days.
Any other information on results incl. tables
Table 1: Emitted carbon in mg/L
Day |
Blind1 |
Blind2 |
Refer. |
Test 1 |
Test 2 |
abiot. |
Toxicity |
2 |
1.50 |
1.66 |
1.30 |
2.64 |
1.65 |
1.26 |
0.84 |
4 |
2.42 |
2.53 |
10.93 |
5.81 |
5.28 |
1.00 |
4.66 |
6 |
2.06 |
1.77 |
12.49 |
8.10 |
8.23 |
0.73 |
10.24 |
8 |
2.64 |
2.80 |
15.47 |
11.66 |
10.65 |
0.36 |
15.22 |
10 |
3.02 |
3.28 |
17.81 |
14.07 |
12.77 |
0.48 |
17.64 |
13 |
4.26 |
4.88 |
20.26 |
17.16 |
14.58 |
1.19 |
21.67 |
17 |
4.28 |
5.00 |
21.50 |
19.55 |
18.49 |
0.98 |
24.20 |
21 |
4.34 |
5.11 |
21.10 |
19.51 |
19.30 |
1.53 |
24.77 |
28 |
4.11 |
4.77 |
21.05 |
20.04 |
19.02 |
0.86 |
25.93 |
29 |
6.25 |
7.42 |
22.78 |
22.56 |
21.53 |
0.79 |
27.07 |
Table 2: Degradation in %
Day |
Refer. |
Test 1 |
Test 2 |
Mean |
abiot. |
Toxicity |
2 |
-1.4 |
5.0 |
0.3 |
2.7 |
6.0 |
-1.8 |
4 |
41.5 |
15.7 |
13.3 |
14.5 |
4.8 |
5.3 |
6 |
52.0 |
29.1 |
30.0 |
29.6 |
3.5 |
20.1 |
8 |
62.6 |
42.2 |
37.7 |
39.9 |
1.7 |
30.2 |
10 |
72.0 |
51.5 |
45.7 |
48.6 |
2.3 |
35.0 |
13 |
77.1 |
59.4 |
47.6 |
53.5 |
5.7 |
41.3 |
17 |
82.9 |
70.3 |
65.8 |
68.0 |
4.7 |
47.2 |
21 |
80.5 |
69.7 |
69.3 |
69.5 |
7.3 |
48.4 |
28 |
81.6 |
73.6 |
69.3 |
71.4 |
4.1 |
51.9 |
29 |
78.3 |
74.2 |
69.8 |
72.0 |
3.7 |
48.9 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- see above, "Detail on results" for details
- Interpretation of results:
- readily biodegradable, but failing 10-day window
- Conclusions:
- Altogether, 71.4% of zinc-12-hydroxystearate was biodegraded after 28 days as determined in the OECD 301B test with 14.5 % after 4 days and 53.5% after 13 days. Zinc-12-hydroxystearate is readily biodegradable as the 60% level was passed within 28 days but failed the 10 day window criteria.
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