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Diss Factsheets
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EC number: 954-921-6 | CAS number: -
- 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
Dissociation constant
Administrative data
Link to relevant study record(s)
- Endpoint:
- dissociation constant
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 29 Nov 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 112 (Dissociation Constants in Water)
- Version / remarks:
- May 1981
- GLP compliance:
- yes (incl. QA statement)
- Dissociating properties:
- no
- Remarks on result:
- other: the test substance has no dissociation within the range pH 2 to pH 12
- Conclusions:
- The test substance has no dissociation within the range pH 2 to pH 12.
- Executive summary:
The study was performed to evaluate the dissociation constant of the test substance in water according to OECD TG 112 and in compliance with GLP. Expert assessment and an evaluation with the specialized predictive software lead to the conclusion that no dissociation was to be expected within the range pH 2 to pH 12.
Reference
RESULT:
Both solutions prepared precipitated out of solution on the addition of the water, indicating that an aqueous sample solution concentration of 0.01 M could not be achieved even when using 50 % v/v co-solvent. In the absence of suitable solubility, titration of sample solutions at the required concentrations was not feasible.
On expert assessment of the functional groups present within the test substance structure, no dissociating functional groups were identified within the dissociation constant range of interest (2 to 12), which would permit dissociation of the test substance within the environmentally relevant pH range of 4 to 10. This conclusion was fully supported by computer estimation of the dissociation constants. Evaluation with the specialized predictive software Advanced Chemistry Development, Algorithm Version v12.1.0.50374, resulted in dissociation constant values below 0 for the acceptance of protons by the two amide groups and a dissociation constant value above 12 for the donation of the proton from the secondary amide group (actual value 12.43 ± 0.20). The solubility of the test substance in water was insufficient to allow dissolution of the test substance in water at a concentration of 0.01 M, considered optimal for the investigation of dissociation constants and also critical to allow evaluation of any functional groups down to a possible dissociation constant value of 2. As a result of this, it was intended to adapt the OECD Method 112 procedure both by increasing the sample solution concentration above that of half the water solubility of the test substance and also the proportion of co-solvent content in the sample solutions to compensate for this, correcting to the dissociation constant in pure water using the Yasuda-Shedlovsky extrapolation method. However, successful dissolution at the required concentration could not be achieved, even on using 50 % v/v co-solvent. The alternative experimental procedure suitable for low water soluble substances, the spectrophotometric method, was not suitable for this test substance. This was due to the spatial separation between the possible dissociating functional groups and the absorbing aromatic functional groups, especially for the tertiary amide functional group. Therefore absorbance properties of the test substance were not expected to be dependent on the degree of ionization and more critically, the absence of any changes in absorbance could not be taken as conclusive of the absence of dissociation.
Expert assessment of the test substance structure did not identify any potential dissociating functional groups within the dissociation constant range of interest (2 to 12), which would permit dissociation of the test substance within the environmentally relevant pH range of 4 to 10. This conclusion was fully supported by computer estimation of the dissociation constants. Evaluation with the specialized predictive software Advanced Chemistry Development, Algorithm Version v12.1.0.50374, resulted in dissociation constant values below 0 for the acceptance of protons by the two amide groups and a dissociation constant value above 12 for the donation of the proton from the secondary amide group (actual value 12.43 ± 0.20). Although experimental evaluation of this conclusion was also attempted, low solubility in aqueous media prevented successful completion of any titrations, even when using significant co-solvent concentrations. The alternative experimental procedure suitable for low water soluble substances, the spectrophotometric method, was not suitable for this test substance due to the spatial separation between the possible dissociating functional groups and the absorbing aromatic functional groups; especially for the tertiary amide functional group. Therefore absorbance properties of the test substance were not expected to be dependent on the degree of ionization and more critically, the absence of any changes in absorbance could not be taken as conclusive of the absence of dissociation.
Description of key information
No dissociation within the range of pH 2 - 12, OECD 112, test substance was prepared in methanol and dimethyl sulfoxide, spectrophotometer, O'Connor 2017.
Key value for chemical safety assessment
Additional information
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