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EC number: 205-550-7 | CAS number: 142-62-1
- 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
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 30 Apr - 04 Jun 1991
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- other: ISO 10708
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Principles of method if other than guideline:
- 28 days BOD/COD test: Inoculated mineral salt medium was filled in glass flasks of known volume. After a one-week preincubation at 20 °C, the medium was saturated with oxygen and the test substance was added. The closed flasks were incubated on a shaker at 20 ± 1 °C and biodegradation was monitored through regular oxygen measurements. An inoculum blank (inoculated medium without test substance) and a positive control (sodium acetate as reference substance) accompanied the experiments.
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: Activated sludge was obtained from the sewage treatment plant Ohligs, Germany
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- COD
- Initial conc.:
- 49 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS:
Glass flasks were filled with 200 mL mineral salt medium and inoculated with activated sludge (30 mg dry matter/L). After a one-week preincubation at 20 °C, the medium was saturated with oxygen and the test substance was added (approx. 20 mg COD/flask). The closed flasks were incubated on a shaker at 20 ± 1 °C and biodegradation was monitored through regular oxygen measurements.
SAMPLING
- Sampling frequency: Measurement of oxygen after 7, 14, 21, 28 days
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes - Reference substance:
- acetic acid, sodium salt
- Parameter:
- % degradation (O2 consumption)
- Value:
- 84
- Sampling time:
- 28 d
- Parameter:
- COD
- Value:
- 2.128 g O2/g test mat.
- Interpretation of results:
- readily biodegradable
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 12 Sep - 10 Oct 1991
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: Sewage was obtained from the municipal sewage treatment plant Hochdahl, Germany.
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 2 mg/L
- Based on:
- act. ingr.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS:
Glass flasks were filled with mineral salt medium and inoculated with one drop of sewage/L. The closed flasks were incubated on a shaker at 20 ± 1 °C and biodegradation was monitored through regular oxygen measurements using the method of iodometric oxygen determination.
SAMPLING
- Sampling frequency: Measurement of oxygen after 7, 14, 22, 28 days
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes - Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (O2 consumption)
- Value:
- 86
- Sampling time:
- 28 d
- Details on results:
- The result of 86% degradation of the test substance after 28 d is based on the initial concentration of 2 mg/L.
The initial concentration of 5 mg/L was also tested but led to a depletion of oxygen in the closed bottles due to the good biodegradability of the test substance. - Parameter:
- COD
- Value:
- 2.128 g O2/g test mat.
- Results with reference substance:
- The reference substance sodium benzoate attained 85% degradation after 28 days.
Referenceopen allclose all
Table: Biodegradation of the test substance in the BODIS test
Test substance |
Test Concentr. (mg COD/L) |
% Degradation (BOD/COD) after x days |
|||
7 |
14 |
21 |
28 |
||
Hexanoic acid |
100 |
57 |
70 |
79 |
84 |
Sodium acetate |
100 |
62 |
73 |
79 |
79 |
Table: Biodegradation of the test substance in the closed bottle test
Test substance |
Test Concentr. (mg COD/L) |
% Degradation (BOD/COD) after x days |
|||
7 |
14 |
22 |
28 |
||
Hexanoic acid |
2 |
78 |
85 |
91 |
86 |
5 |
68 |
82 |
79 |
81 (a) |
|
Sodium benzoate |
2 |
77 |
77 |
85 |
85 |
(a) The lower degradation values for the 5 mg/L test concentration can be explained by oxygen depletion due to the good biodegradability, i.e. the given values are minimum values.
Description of key information
Readily biodegradable (84 % after 28 d based on O2-consumption, performed similar to OECD 301 D)
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
For hexanoic acid (CAS 142 -62 -1) two GLP-studies on the ready biodegradability are available.
In the first study (Richterich, 1991), which is used as key study, a BODIS-test, similar to OECD 301 D was performed. The substance (100 mg/L) was directly weighend in a glass flask by using a glass plate as carrier. Resulting from the test, the biodegradability of hexanoic acid was determined to be 84% based on O2 -consumption after 28 days.
In the second test performed by Richterich (1992), hexanoic acid was pre-solved in an emulsifier (NP 9,5 EO + 5 PO). The study was conducted according to OECD 301D. After 28 days a degradation of 86% of the test substance was reported based on O2 -consumption.
Concluding from the results of both tests, hexanoic acid (CAS 142 -62 -1) is regarded as readily biodegradable.
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