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EC number: 242-359-8 | CAS number: 18479-51-1
- 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:
- 11/05/2000 - 08/06/2000
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study according to international guideline (OECD Guideline 301 D) under GLP conditions, validity criteria met.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 000
- Report date:
- 2000
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-E (Determination of the "Ready" Biodegradability - Closed Bottle Test)
- Deviations:
- no
- Principles of method if other than guideline:
- Not relevant
- GLP compliance:
- yes
- Remarks:
- Statement of compliance
Test material
- Reference substance name:
- 3,7-dimethyloct-1-en-3-ol
- EC Number:
- 242-358-2
- EC Name:
- 3,7-dimethyloct-1-en-3-ol
- Cas Number:
- 18479-49-7
- Molecular formula:
- C10H20O
- IUPAC Name:
- 3,7-dimethyloct-6-en-3-ol
- Details on test material:
- - Name of test material (as cited in study report): Dihydrolinalool
- Physical state: Liquid
- Storage condition of test material: In refrigerator protected from light
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not relevant
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, domestic, non-adapted
- Details on inoculum:
- - Source of inocculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): Secondary effluent freshly obtained from a municipal sewage treatment plant: "Waterschap de Maaskant", 's Hertogenbosch, The Netherlands
- Pretreatment: Secondary effluent was filtered through a coarse filter paper, the first 200 ml was discarded.
- Storage conditions: The filtrate was kept aerated until inoculation
- Inoculation: 0.1 ml filtrate of secondary effluent per litre of final volume - Duration of test (contact time):
- 28 d
Initial test substance concentrationopen allclose all
- Initial conc.:
- 1.031 mg/L
- Based on:
- test mat.
- Initial conc.:
- 2.062 mg/L
- Based on:
- test mat.
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Mineral medium according to the testing guideline
- Test temperature: Recorded daily in a vessel in the same room
- pH: Recorded at the start of the test in all test bottles
- pH adjusted: no
- Continuous darkness: yes
TEST SYSTEM
Parallel groups of 250-300 ml BOD bottles with glass stoppers were prepared to allow duplicate measurements of oxygen consumption at the test intervals. The oxygen concentration was determined immediately at the start of the experiment (day 0), and at day 7, 14, 21 and 28 in duplicate.
CONTROL AND BLANK SYSTEM
- Inoculum blank: Containing only inoculum
- Toxicity control: Containing test substance, reference substance and inoculum
- Positive control: Containing 2 mg/l reference substance
Reference substance
- Reference substance:
- acetic acid, sodium salt
- Remarks:
- Merck art. 6268, batch 049 TA933768
Results and discussion
- Preliminary study:
- Not applicable
- Test performance:
- The temperature varied between 19.5°C and 21.0°C. The pH recorded at the start of the test was 7.6 in all test bottles.
The positive control showed 75% biodegradation within 7 days. The oxygen depletion in the inoculum blank was 0.93 mg O2/l The oxygen depletion
in the toxicity control was always more than 75% of the sum of the oxygen depletion in the positive control and 1.031 mg/l Dihydrolinalool.
Therefore, Dihydrolinalool was assumed to be not inhibitory.
% Degradationopen allclose all
- Parameter:
- % degradation (O2 consumption)
- Value:
- 10
- Sampling time:
- 7 d
- Remarks on result:
- other: High test subst concentration (2 mg/l)
- Parameter:
- % degradation (O2 consumption)
- Value:
- 64
- Sampling time:
- 28 d
- Remarks on result:
- other: High test subst concentration (2 mg/l)
- Parameter:
- % degradation (O2 consumption)
- Value:
- 32
- Sampling time:
- 7 d
- Remarks on result:
- other: Low test subst. concentration (1 mg/l)
- Parameter:
- % degradation (O2 consumption)
- Value:
- 63
- Sampling time:
- 28 d
- Remarks on result:
- other: Low test subst. concentration (1 mg/l)
- Details on results:
- The relative biodegradation values calculated from the O2 measurements performed during the test period of 28 days revealed significant
degradation of Dihydrolinalool at both concentrations. After 7 days of incubation degradation was 32% at 1 mg/l Dihydrolinalool and 10% at 2 mg/l
Dihydrolinalool. After 14 days biodegradation had increased to levels of 59% and 54% respectively. Biodegradation tended to level-off at
approximately 65% in both test concentrations. For detailed results see the Table included in overall remarks.
Furthermore, the limit for ready biodegradability (i.e. 60% of degradation within 28 days, obtained within 10 days of biodegradation exceeding 10%) was met for the high concentration (2.062 mg/l) of Dihydrolinalool, as can be seen in the attached figure.
BOD5 / COD results
- Results with reference substance:
- Not relevant
Any other information on results incl. tables
Test medium |
Concentration (mg/l) |
Oxygen depletion (mg BOD/l) after x days |
||||
0 |
7 |
14 |
21 |
28 |
||
Positive control |
2.052 |
0 |
75 |
72 |
76 |
72 |
Test substance low |
1.031 |
0 |
32 |
59 |
59 |
63 |
Test substance high |
2.062 |
0 |
10 |
54 |
65 |
64 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- Oxygen depletion in inoculum blank <1.5 mg O2/l, residual O2 concentration in test bottles >0.5 mg/l at all times, difference between duplicates <20% and control substance degraded >60% within 7 days
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Dihydrolinalool was readily biodegradable under the conditions of the closed bottle test performed.
- Executive summary:
The biodegradability of Dihydrolinalool was tested in a closed bottle test (OECD TG 301D). The validity criteria for the test were met. The relative biodegradation values calculated from the O2 measurements performed during the test period of 28 days revealed significant degradation of Dihydrolinalool at both concentrations. After 28 days of incubation degradation approximately 65% in both test concentrations. Furthermore, the limit for ready biodegradability (i.e. 60% of degradation within 28 days, obtained within 10 days of biodegradation exceeding 10%) was met for the high concentration (2.062 mg/l) of Dihydrolinalool.
In conclusion, Dihydrolinalool was readily biodegradable under the conditions of the closed bottle test performed.
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