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EC number: 619-228-2 | CAS number: 96556-05-7
- 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:
- 03 September 2014 to 16 November 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Version / remarks:
- 1995
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Version / remarks:
- 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Key result
- Water solubility:
- > 50 g/L
- Conc. based on:
- test mat.
- Loading of aqueous phase:
- 50 g/L
- Incubation duration:
- 19 h
- Temp.:
- 20 °C
- pH:
- 13
- Details on results:
- Visual Appraisal
- The visual assessment of the samples prepared was inconclusive, possibly due to the complex composition of the test material. The test material is not a pure substance and has several minor components/impurities, some of which are not miscible with water. However, for the main visual test, the formation of two distinct phases at loading rates at or above 30.1 % confirmed that the test material was not miscible with water, as initially indicated by computer modelling.
Analytical Evaluation
- The mean peak areas relating to the standard and sample solutions are shown in Tables 4 and 5.
- The concentration (g/L) of test material in the sample solutions is shown in Table 6.
- In each case, when monitoring the main component of the test material, the analytical results equated to the approximate initial loading concentration, indicating complete dissolution of the species of interest. - Conclusions:
- Under the conditions of this study, the water solubility of the test material has been determined to be greater than 50 g/L (i.e. greater than 5 % w/w).
- Executive summary:
The water solubility of the test material was investigated in accordance with the standardised guidelines OECD 105 and EU Method A.6., under GLP conditions.
The software EPI Suite v4.1 by the U.S. Environmental Protection Agency estimated that the test material was completely miscible in water. Therefore, the standard OECD 105 methodology was deemed to be not applicable to this test material and it was decided to address the data endpoint by visual appraisal. The visual assessment of the samples prepared was inconclusive, possibly due to the complex composition of the test material (presence of minor components/impurities which are not miscible with water). However, the formation of two distinct phases at loading rates at or above 30.1 % confirmed that the test material was not miscible with water.
Due to the presence of undissolved matter observed at the lower concentrations used for visual appraisal, further samples were prepared at loading rates of approximately 5.0 and 50 g/L to investigate the test material water solubility analytically, using a GC-FID method. The recovered concentration of the main test material component approximated the initial loading rate in both cases. Therefore, the undissolved material could be attributed to the water-immiscible impurities present within the test material.
The test material, as a whole, was determined visually to be insoluble at all loading rates evaluated (5.03 to 94.9 % w/w). Critically however, analysis of solutions loaded at nominal concentrations of 0.50 and 5.0 % w/w resulted in complete recovery of the main test material component. Therefore, the overall conclusion was that the water solubility of the octahydro-1,4, 7-trimethylIH- 1,4, 7-triazonine (Me3TACN) was greater than 50 g/L; nevertheless, the presence of lesser soluble impurities must be acknowledged.
Under the conditions of this study, the water solubility of the test material has been determined to be greater than 50 g/L (i.e. greater than 5 % w/w). The test material can therefore be classified as very soluble in water, as indicated by the European Chemicals Agency (ECHA).
Reference
Table 4: Flask Shake Method - Analysis Sample 1
Solution |
Mean Peak Area |
Standard at 558 mg/L |
3.2541 x10^6 |
Standard at 547 mg/L |
3.1083 x10^6 |
Matrix Blank |
None detected |
Sample 1A |
2.8670 x10^6 |
Sample 1B |
3.0488 x10^6 |
Table 5: Flask Shake Method - Analysis Sample 2
Solution |
Mean Peak Area |
Standard at 265 mg/L |
6.3119 x10^6 |
Standard at 291 mg/L |
6.8043 x10^6 |
Matrix Blank |
None detected |
Sample 2A |
5.0421 x10^6 |
Sample 2B |
4.9584 x10^6 |
Table 6: Flask shake Method Results
Sample Number |
Time Shaken at ~30 °C (h) |
Time Equilibrated at 20 °C (h) |
Concentration (g/L) |
Mean Concentration (g/L) |
Solution pH |
1 |
3 |
3 |
(A)4.98 (B)5.29 |
5.13 |
12.29 |
2 |
3 |
19 |
(A)53.4 (B)52.5 |
52.9 |
13.01 |
Description of key information
Under the conditions of this study, the water solubility of the test material has been determined to be greater than 50 g/L (i.e. greater than 5 % w/w).
Key value for chemical safety assessment
- Water solubility:
- 50 g/L
- at the temperature of:
- 20 °C
Additional information
The water solubility of the test material was investigated in accordance with the standardised guidelines OECD 105 and EU Method A.6., under GLP conditions. The study was awarded a reliability score of 1 in accordance with the criteria set forth by Klimisch et al. (1997).
The software EPI Suite v4.1 by the U.S. Environmental Protection Agency estimated that the test material was completely miscible in water. Therefore, the standard OECD 105 methodology was deemed to be not applicable to this test material and it was decided to address the data endpoint by visual appraisal. The visual assessment of the samples prepared was inconclusive, possibly due to the complex composition of the test material (presence of minor components/impurities which are not miscible with water). However, the formation of two distinct phases at loading rates at or above 30.1 % confirmed that the test material was not miscible with water.
Due to the presence of undissolved matter observed at the lower concentrations used for visual appraisal, further samples were prepared at loading rates of approximately 5.0 and 50 g/L to investigate the test material water solubility analytically, using a GC-FID method. The recovered concentration of the main test material component approximated the initial loading rate in both cases. Therefore, the undissolved material could be attributed to the water-immiscible impurities present within the test material.
The test material, as a whole, was determined visually to be insoluble at all loading rates evaluated (5.03 to 94.9 % w/w). Critically however, analysis of solutions loaded at nominal concentrations of 0.50 and 5.0 % w/w resulted in complete recovery of the main test material component. Therefore, the overall conclusion was that the water solubility of the octahydro-1,4, 7-trimethylIH- 1,4, 7-triazonine (Me3TACN) was greater than 50 g/L; nevertheless, the presence of lesser soluble impurities must be acknowledged.
Under the conditions of this study, the water solubility of the test material has been determined to be greater than 50 g/L (i.e. greater than 5 % w/w). The test material can therefore be classified as very soluble in water, as indicated by the European Chemicals Agency (ECHA).
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