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EC number: 441-000-4 | CAS number: 121219-07-6 1-ETHOXY-2,3-DIFLUORBENZOL; 1-ETHOXY-2,3-DIFLUOROBENZENE; 2,3-DIFLUOROPHENETOL; DIPHOL
- 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:
- 2000-01-27 till 2000-03-07
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Version / remarks:
- July 17, 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-E (Determination of the "Ready" Biodegradability - Closed Bottle Test)
- Version / remarks:
- December 1992
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum: sewage plant Groß-Zimmern, Germany
Conditioning: The activated sludge used for this study was washed by centrifugation and the supernatant liquid phase was decanted. The solid material was resuspended in tap water and again centri-fuged. This procedure was repeated twice. An aliquot of the final sludge suspension was weighed, dried and the ratio of wet sludge to its dry weight was determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 4 g dry material per litre were mixed with test water and then aerated until use. Before use the sludge was filtered through cotton wool. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 2.94 mg/L
- Based on:
- ThOD
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: reconstituted water according to OECD 301
- Additional substrate: no
- Test temperature: 22 °C
- pH: 7.6 (measured at the start of the test)
- pH adjusted: no
- Aeration of dilution water: yes
- Continuous darkness: yes
- Oxygen Concentration of Test Water: 8.6-8.9 mg O2/L (measured at the start of the test)
TEST SYSTEM
- Culturing apparatus: Karlsruher flasks of 250 mL volume with glass stoppers
- Number of culture flasks/concentration: 2
- Measuring equipment: O2-electrode (WTW Oxi 340, Wissenschaftlich Technische Werkstatten GmbH, Weilheim, Germany)
- Test performed in closed vessels due to significant volatility of test substance: yes
CONTROL AND BLANK SYSTEM
- Inoculum blank: inoculum and test medium
- Procedure control: reference item, inoculum and test medium
- Toxicity control: test item, reference item, inoculum and test medium - Reference substance:
- aniline
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- -2
- Sampling time:
- 28 d
- Details on results:
- Under the test conditions the percentage biodegradation of the test item reached in the mean -2 % after 28 days of incubation.
In the toxicity control containing both, the test item and the reference item Aniline, in the mean 39 % biodegradation was noted within 14 days and 44 % biodegradation after 28 days of incubation. - Results with reference substance:
- The reference item Aniline was sufficiently degraded to in the mean 82 % after 14 days, and to 107 % after 28 days of incubation.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The test item is not biodegradable in a test according to OECD 301 D.
- Executive summary:
The test item was tested for its ready biodegradability in the closed bottle test at 2.94 mg/L. The study procedure was based on EU Method C.4-E and OECD guideline No. 301 D. The test item was investigated for its ready biodegradability in a Closed Bottle Test over a period of 28 days. The biodegradation was followed by the oxygen uptake of the microorganisms during exposure. As a reference item Aniline was tested simultaneously under the same conditions as the test item, and functioned as a procedure control. The relative biodegradation values calculated from the O2 measurements performed during the test period of 28 days revealed no significant (0%) degradation. Since all acceptability criteria prescribed by the protocol were met, this study was considered to be valid. In conclusion, the test item was not biodegradable under the conditions in the closed bottle test presently performed.
Reference
Table 1: Percentage biodegradation at different time intervals during the exposure of 28 days
Treatment |
Conc. (mg/L) |
Flask No. |
% biodegradation after n days of exposure |
||||||
2 |
5 |
7 |
12 |
14 |
21 |
28 |
|||
Test item |
2.94 |
1a |
-2 |
-3 |
-3 |
-4 |
-3 |
-4 |
-2 |
1b |
-2 |
-3 |
-3 |
-4 |
-5 |
-2 |
-2 |
||
mean |
-2 |
-3 |
-3 |
-4 |
-4 |
-3 |
-2 |
||
Procedure Control (Aniline) |
2.02 |
2a |
2 |
54 |
61 |
76 |
81 |
101 |
105 |
2b |
4 |
54 |
63 |
80 |
83 |
103 |
109 |
||
mean |
3 |
54 |
62 |
78 |
82 |
102 |
107 |
||
Toxicity control |
TS: 2.94 Aniline; 2.02 |
4a |
n.d. |
n.d |
29 |
n.d. |
39 |
38 |
43 |
4b |
n.d. |
n.d. |
29 |
n.d. |
39 |
38 |
45 |
||
mean |
n.d. |
n.d. |
29 |
n.d. |
39 |
38 |
44 |
n.d. not determined
TS: test item
Description of key information
The test item is not biodegradable in a test according to OECD 301 D (reference 5.2.1 -1).
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
- Type of water:
- freshwater
Additional information
The test item was tested for its ready biodegradability in the closed bottle test at 2.94 mg/L. The study procedure was based on EU Method C.4-E and OECD guideline No. 301 D. The test item was investigated for its ready biodegradability in a Closed Bottle Test over a period of 28 days. The biodegradation was followed by the oxygen uptake of the microorganisms during exposure. As a reference item Aniline was tested simultaneously under the same conditions as the test item, and functioned as a procedure control. The relative biodegradation values calculated from the O2 measurements performed during the test period of 28 days revealed no significant (0%) degradation. Since all acceptability criteria prescribed by the protocol were met, this study was considered to be valid. In conclusion, the test item was not biodegradable under the conditions in the closed bottle test presently performed (reference 5.2.1 -1).
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