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EC number: 269-130-5 | CAS number: 68187-85-9
- 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:
- 08 Mar - 18 Apr 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Version / remarks:
- 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Version / remarks:
- 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Hessisches Ministerium für Umwelt, Klimaschutz, Landwirtschaft und Verbraucherschutz, Germany
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: Sewage treatment plant Bensheim, Germany
- Preparation of inoculum for exposure: Activated sludge used for this study was deposited for 15 min and washed by centrifugation. Aliquotes of washed sludge suspension, corresponding to 3.5 g dry material/L were mixed with test water and aerated overnight.
- Pretreatment: Sludge was washed by centrifugation, liquid phase was then decanted and solid material was re-suspended in tap water and centrifuged, procedure was repeated 3 times. An aliquot of the final sludge suspension was weighed, dried and ratio of wet sludge to dry weight was determined. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 103.1 mg/L
- Based on:
- test mat.
- Initial conc.:
- 298.6 mg/L
- Based on:
- ThOD
- Remarks:
- ThODNH4
- Initial conc.:
- 301.1 mg/L
- Based on:
- ThOD
- Remarks:
- ThODNO3
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: according to guideline
- Test temperature: 22 °C ± 1 °C
- pH: 7.4 - 7.9
- Suspended solids concentration in flask: 28.7 mg sludge/L
- Continuous darkness: yes
- Other: continuous stirring
TEST SYSTEM
- Culturing apparatus: Manometric Test System with test flasks containing a volume of approx. 500 mL.
- Number of culture flasks/concentration: 2
- Measuring equipment: BSB/BOD-Sensor-System, Aqualytic Dortmund, Germany
- Test performed in closed vessels: yes
- Details of trap for CO2: potassium hydroxide solution (45%)
SAMPLING
- Sampling method: The pressure decrease in the reaction vessels was measured daily.
CONTROL AND BLANK SYSTEM
- Inoculum control: 2 flasks
- Abiotic sterile control: 1 flask (poisoned with CuSO4)
- Toxicity control: 1 flask
- Other: procedure control: 1 flask
- Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (O2 consumption)
- Value:
- 63
- Sampling time:
- 28 d
- Remarks on result:
- other: mean of ThODNH4 and ThODNO3
- Details on results:
- Toxicity control: 61% biodegradation after 14 d and 62% after 28 d (the test item can be assumed to be not inhibitory to the aerobic activated sludge microorganisms as degradation was >25% within 14 d.)
- Results with reference substance:
- 94% biodegradation of reference substance after 14 d and 103% after 28 days.
- Validity criteria fulfilled:
- yes
- Remarks:
- See Table 2 in section "Any other information on results incl. tables"
- Interpretation of results:
- readily biodegradable
Reference
Table 1: Percentage Biodegradation of Test Item and of the Toxicity Control based on ThODNO3 and of Sodium Benzoate based on ThODNH4
Time |
Percentage Biodegradation 1) |
|||
(Days) |
Test Item |
Sodium Benzoate 2) |
Toxicity |
|
|
Flask 1 [%] |
Flask 2 [%] |
Flask 5 [%] |
Flask 7 [%] |
1 |
3 |
3 |
32 |
11 |
2 |
10 |
10 |
47 |
16 |
3 |
12 |
13 |
65 |
29 |
4 |
17 |
17 |
71 |
33 |
5 |
20 |
20 |
76 |
36 |
6 |
22 |
22 |
76 |
38 |
7 |
23 |
25 |
79 |
41 |
8 |
31 |
35 |
91 |
51 |
9 |
35 |
38 |
91 |
53 |
10 |
38 |
40 |
91 |
55 |
11 |
38 |
42 |
94 |
56 |
12 |
40 |
43 |
94 |
58 |
13 |
43 |
45 |
94 |
60 |
14 |
45 |
47 |
94 |
61 |
15 |
46 |
47 |
97 |
61 |
16 |
48 |
48 |
97 |
62 |
17 |
50 |
50 |
97 |
62 |
18 |
53 |
52 |
97 |
62 |
19 |
55 |
53 |
97 |
62 |
20 |
55 |
55 |
97 |
62 |
21 |
56 |
55 |
100 |
62 |
22 |
56 |
57 |
100 |
62 |
23 |
58 |
57 |
100 |
62 |
24 |
60 |
58 |
103 |
62 |
25 |
60 |
58 |
103 |
62 |
26 |
61 |
60 |
103 |
62 |
27 |
63 |
62 |
103 |
62 |
28 |
63 |
62 |
103 |
62 |
1) ThODNO3 of Test Item: 2.921 mg O2/mg test item
2) ThODNH4 of sodium benzoate: 1.666 mg O2/mg reference item
Table 2: Validity criteria
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
Difference of extremes of replicate values of the removal of the test chemical at the plateau, at the end of the test or at the end of the 10-d window, as appropriate, is less than 20%. |
2% |
Yes |
Percentage degradation of the reference compound has reached the pass levels by day 14. |
>60% |
Yes |
The toxicity control should degrade to at least 35% (based on DOC) or at least 25% (based on ThOD or ThCO2) within 14 d. |
62% |
Yes |
The oxygen uptake of the inoculum blank is normally 20-30 mg O2/L and should not be greater than 60 mg/L in 28 days. |
25 mg O2/L |
Yes |
Description of key information
Readily biodegradable (63% degradation after 28 d, OECD 301 F)
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
One study is available, in which the biodegradability of Fatty acids, tall-oil, esters with ethylene glycol (CAS 68187-85-9) was tested. The study was conducted according to the OECD guideline 301 F and GLP. Non-adapted activated sludge was used as inoculum and was exposed to 103.1 mg/L test material (298.6 mg/L based on ThODNH4 and 301.1 based on ThODNO3) for 28 d. Oxygen consumption was measured daily by decreasing of the pressure in the bottles in order to monitor the biodegradation of the substance. A reference and a toxicity control were run in parallel. 63% biodegradation (mean of ThODNH4 and ThODNO3) was recorded after 28 d. Since the test item is a UVCB substance and consists of structurally similar constituents with different chain-lengths, sequential (instead of concurrent) biodegradation of the individual structures can take place, but all can be considered as readily biodegradable. Thus, referring to Annex I to the OECD Guideline for Testing of Chemicals ‘Revised introduction to the OECD guidelines for testing of chemicals, section 3’ (OECD, March 2006), the 10-day window should not be considered for UVCB substances and due to a degradation of >60 % within 28 days the substance is considered readily biodegradable.
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