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EC number: 221-111-2 | CAS number: 3006-86-8
- 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
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:
- 2019-07-23 to 2019-08-30
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- yes
- Remarks:
- Slow-stirring conditions were applied. Test duration was 14 days.
- GLP compliance:
- no
- Type of method:
- flask method
- Key result
- Water solubility:
- 2.1 mg/L
- Conc. based on:
- test mat. (dissolved fraction)
- Loading of aqueous phase:
- 10 mg/L
- Incubation duration:
- 14 d
- Temp.:
- 20 °C
- pH:
- ca. 7
- Details on results:
- The determined result for the water solubility of the test substance was an average value of two samples taken after 14 days. The average result was calculated to be 2.1 mg/L for the test substance.
- Conclusions:
- The water solubility of the test substance was determined to be 2.1 mg/L at 20 °C.
- Executive summary:
The water solubility fo the test substance was determined in a study performed according to OECD 105 using the shake flask method. A slight modification ot the guideline was applied based on the physico-chemical properties of the test substance - slow-stirring was applied and the incubation period was extended to 14 days. The test was carried out in glass flasks with a Teflon tap near the bottom. The definitive test was performed at 10 mg/L, without centrifugation. It was determined that centrifugation resulted in substance loss due to adsorption to the test vessel walls. In duplicate flasks, approximately 10 mg of the test substance were weighed in and 1 litre of demineralised water was added to each flask. The flasks were placed in the dark at 20 °C and stirred as slowly as possible. At the time points 1, 2, 3, 4, 7, 9, 11 and 14 days after addition of the test substance, the solution was stopped and left to rest for 1 hour before samples were tapped. In duplicate about 10 mL was sampled from the bottom of the flask (dead volume of the tap was rinsed to waste) and transferred to separate centrifuge tubes. Subsequently, 2 mL hexane was added to the centrifuge tube to extract the test substance. The extracts were analysed with GC-MS. The determined result for the water solubility of the test substance was an average value of two samples taken after 14 days. The average result was calculated to be 2.1 mg/L at 20 °C.
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 2012-05-11 to 2012-05-23
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Version / remarks:
- adopted July 27, 1995
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Version / remarks:
- 31 May 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 830.7840 (Water Solubility)
- Version / remarks:
- March 1998
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- column elution method
- Key result
- Water solubility:
- < 1 mg/L
- Temp.:
- 20 °C
- pH:
- 7.5
- Key result
- Water solubility:
- < 1.07 mg/L
- Temp.:
- 25 °C
- Remarks on result:
- other: Estimation of the water solubility using EUSES.
- Details on results:
- Preliminary test:
The water solubility of the test item was estimated to be ca. 6 mg/L in a preliminary test and therefore the column elution method was used in the main test.
Calibration:
The calibration solutions were prepared on each analytical occasion. The calibration samples were analysed by HPLC with three parallel injections from each. The 1,1-bis(tert-butylperoxy)cyclohexane concentrations were calculated with the help of the linear regression data.
Main test:
The water solubility of the test item was determined to be < 1 mg/L (Limit of Quantification, LOQ) at 20 °C ± 0.5 °C - Conclusions:
- The water solubility of 1,1-bis(tert-butylperoxy)cyclohexane was estimated to be < 1 mg/L (quantification limit analytical method, HPLC-UV) at 20 °C ± 0.5 °C. Thus, the test item was considered to be slightly soluble or insoluble.
- Executive summary:
The water solubility of 1,1-bis(tert-butylperoxy)cyclohexane was determined according to EU method A.6, OECD Guideline 105, and EPA OPPTS 830.7840 guideline. The water solubility of the test item determined to be < 1 mg/L (Limit of Quantification) at 20 °C ± 0.5 °C using the column elution method for the performance of the main test. Thus, 1,1-bis(tert-butylperoxy)cyclohexane was considered to be slightly soluble or insoluble.
Referenceopen allclose all
Table 1: Results of test substance in water, no centrifugation
Time (days) |
Concentration Replicate I (µg/L) |
Concentration Replicate II (µg/L) |
Average conc. (µg/L) |
1 |
890.3 |
834 |
862.1 |
2 |
1345.7 |
1306 |
1325.8 |
3 |
1558.1 |
1585 |
1571.4 |
4 |
1739.7 |
1682 |
1711.0 |
7 |
1990.5 |
1936 |
1963.4 |
9 |
2125.1 |
2032 |
2078.6 |
11 |
2201.3 |
2159 |
2179.9 |
14 |
2160.3 |
2102 |
2131.0 |
Description of key information
The water solubility of the test substance was determined to be 2.1 mg/L at 20 °C.
Key value for chemical safety assessment
- Water solubility:
- 2.1 mg/L
- at the temperature of:
- 20 °C
Additional information
The water solubility fo the test substance was determined in a study performed according to OECD 105 using the shake flask method. A slight modification ot the guideline was applied based on the physico-chemical properties of the test substance - slow-stirring was applied and the incubation period was extended to 14 days. The test was carried out in glass flasks with a Teflon tap near the bottom. The definitive test was performed at 10 mg/L, without centrifugation. It was determined that centrifugation resulted in substance loss due to adsorption to the test vessel walls. In duplicate flasks, approximately 10 mg of the test substance were weighed in and 1 litre of demineralised water was added to each flask. The flasks were placed in the dark at 20 °C and stirred as slowly as possible. At the time points 1, 2, 3, 4, 7, 9, 11 and 14 days after addition of the test substance, the solution was stopped and left to rest for 1 hour before samples were tapped. In duplicate about 10 mL was sampled from the bottom of the flask (dead volume of the tap was rinsed to waste) and transferred to separate centrifuge tubes. Subsequently, 2 mL hexane was added to the centrifuge tube to extract the test substance. The extracts were analysed with GC-MS. The determined result for the water solubility of the test substance was an average value of two samples taken after 14 days. The average result was calculated to be 2.1 mg/L at 20 °C.
In a supporting study, the water solubility of 1,1-bis(tert-butylperoxy)cyclohexane was determined according to EU method A.6, OECD Guideline 105, and EPA OPPTS 830.7840 guideline. The water solubility of the test item was determined to be < 1 mg/L (Limit of Quantification, LOQ) at 20 °C ± 0.5 °C using the column elution method for the performance of the main test. Thus, the test item was considered to be slightly soluble or insoluble. The reason for the difference in the results can be the adsorption of the test item to the walls of the test vessels.
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