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EC number: 200-624-5 | CAS number: 66-25-1
- 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
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- Repeated dose toxicity
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- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
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- Additional toxicological data

Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2018-09-24 - 2018-10-24
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Version / remarks:
- 27 July 1995
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Version / remarks:
- 24 January 2014
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Key result
- Water solubility:
- 5.77 g/L
- Conc. based on:
- test mat.
- Loading of aqueous phase:
- 25 g/L
- Incubation duration:
- 7 d
- Temp.:
- 20.3 °C
- pH:
- 3.6
- Details on results:
- The measurements of the flasks 1A - 1C (days 7 - 9) and flasks 2 - 4 were included in the calculation of the mean as an upward tendency was observed on days 2 - 7. As no further increase was noted, it is assumed that a plateau is reached after 7 days.
- Conclusions:
- The water solubility was determined to be 5.77 g/L.
- Executive summary:
The solubility of the test item in water was determined by measurement of the test item concentration in the test solutions using GC/FID according to OECD guideline 105, EU method A.6 and under GLP conditions.
The preliminary test which is described in the guideline was performed in the method validation study 17111506G926. The solubility of the test item in water was estimated as 5 g/L (measured in a solution with a nominal load of the test item of 10 g/L). For test items with water solubility above 10 mg/L, the flask method is used. The test item solutions were stirred to speed up the solubility in water as a suspension was observed after shaking of the test item with water during the method validation study.
In the main test, 25 g/L Hexanal were used to prepare a saturated solution (in the guide¬lines, fivefold saturation is proposed). Six replicates were prepared (flasks 1A - C and 2 -4); three flasks 1A - C were used during the equilibration time. Four vessels (flasks 1C and 2 - 6) were set onto the stirrer at 29.7 - 30.2 °C (whole temperature range for 10 days; the flasks 1A - 1C were stirred for 3 days at 29.7 - 30.1 °C). After 24 ± 2 hours, flask 1B and after 48 ± 2 hours, flask 1A were set on the stirrer and all flasks were stirrer for further 24 ± 2 hours at 29.7 - 30.1 °C. Then, flasks 1A - 1C (corresponding to days 2 -4) were tempered at 20.1 - 20.5 °C for 25 hours, sampled, extracted and analysed via GC/FID. Because of an upward tendency, the test was prolonged and the flasks 1A - 1C were further stirred at 20.1 - 20.5 °C and sampled on days 4 - 9. Due to a difference of less than 15 % in the concentrations on days 8 and 9 and no upward tendency for the last three values, the test was finished. The flasks 2 - 4 were stirred at 29.7 - 30.2 °C for 10 days, than tempered at 20.1 - 20.3 °C for 24 hours and analysed.
The measurements of the flasks 1A - 1C (days 7 - 9) and flasks 2 - 4 were included in the calculation of the mean as an upward tendency was observed on days 2 - 7.
At the plateau (reached about the day 7), the concentration of Hexanal in water had reached: 5.77 ± 0.28 g/L at 20.3 ± 0.2 °C = 5.77 ± 0.28 kg/m3 (SI units) (mean value ± standard deviation of six individual vessels).
Reference
All separated test solutions showed no Tyndall effect (i.e. a laser beam was not scattered when transmitted through the liquid). Interim pH measurements were made using pH paper; the final measurement was made using a calibrated pH-meter.
Description of key information
The solubility of the test item in water was determined by measurement of the test item concentration in the test solutions using GC/FID according to OECD guideline 105, EU method A.6 and under GLP conditions.
The preliminary test which is described in the guideline was performed in the method validation study 17111506G926. The solubility of the test item in water was estimated as 5 g/L (measured in a solution with a nominal load of the test item of 10 g/L). For test items with water solubility above 10 mg/L, the flask method is used. The test item solutions were stirred to speed up the solubility in water as a suspension was observed after shaking of the test item with water during the method validation study.
In the main test, 25 g/L Hexanal were used to prepare a saturated solution (in the guide¬lines, fivefold saturation is proposed). Six replicates were prepared (flasks 1A - C and 2 -4); three flasks 1A - C were used during the equilibration time. Four vessels (flasks 1C and 2 - 6) were set onto the stirrer at 29.7 - 30.2 °C (whole temperature range for 10 days; the flasks 1A - 1C were stirred for 3 days at 29.7 - 30.1 °C). After 24 ± 2 hours, flask 1B and after 48 ± 2 hours, flask 1A were set on the stirrer and all flasks were stirrer for further 24 ± 2 hours at 29.7 - 30.1 °C. Then, flasks 1A - 1C (corresponding to days 2 -4) were tempered at 20.1 - 20.5 °C for 25 hours, sampled, extracted and analysed via GC/FID. Because of an upward tendency, the test was prolonged and the flasks 1A - 1C were further stirred at 20.1 - 20.5 °C and sampled on days 4 - 9. Due to a difference of less than 15 % in the concentrations on days 8 and 9 and no upward tendency for the last three values, the test was finished. The flasks 2 - 4 were stirred at 29.7 - 30.2 °C for 10 days, than tempered at 20.1 - 20.3 °C for 24 hours and analysed.
The measurements of the flasks 1A - 1C (days 7 - 9) and flasks 2 - 4 were included in the calculation of the mean as an upward tendency was observed on days 2 - 7.
At the plateau (reached about the day 7), the concentration of Hexanal in water had reached: 5.77 ± 0.28 g/L at 20.3 ± 0.2 °C = 5.77 ± 0.28 kg/m3 (SI units) (mean value ± standard deviation of six individual vessels).
Key value for chemical safety assessment
- Water solubility:
- 5.77 g/L
- at the temperature of:
- 20.3 °C
Additional information
The result of the key study is supported by an other experimental study (no GLP, no guidline), handbook data and calculation:
Water solubility of hexanal was determined via gas chromatography. No guideline was followed and no GLP-conditions are considered. Water solubility of hexanal is 5.64 g/L at a temperature of 30 °C.
Water solubility of hexanal was described in several handbooks/puplications. Described properties are nearly the same: hexanal is slightly soluble in water. This is supported by one specific handbook value describing the water solubility of hexanal as 5 g/L at 25 °C and an accepted calculation method (based on an estimated Kow) which leads to a water solubility of 4.68 g/L at 25 °C.
Key Study: Davis, 1968:
Water solubility of hexanal was determined via gas chromatography. No guideline was followed and no GLP-conditions are considered. Water solubility of hexanal is 5.64 g/L at a temperature of 30 °C.
CRC Handbook:
Hexanal is slightly soluble in water.
Sax Dang. Prop.:
Hexanal is very slightly soluble in water.
Handbook of aqu. sol.:
5 g/L at 25 °C
EPI Suite calculation:
4.86 g/L at 25 °C
For the CSA the experimental derived value from the key study was chosen.
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