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Diss Factsheets
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EC number: 203-612-8 | CAS number: 108-74-7
- 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
Dissociation constant
Administrative data
Link to relevant study record(s)
- Endpoint:
- dissociation constant
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Remarks:
- The functional groups (reaction centres) of this chemical substance were within the domain of applicability for the SPARC model. Similar molecules were used in the training set and the validation set. SPARC is one of the recommended models for the estimation of pKa identified in ECHA Guidance on Information Requirements.
- Guideline:
- other:
- Version / remarks:
- ECHA Guidance on Information Requirements and Chemical Safety Assessment, Chapter R.6: QSARs and Grouping of Chemicals. May 2008.
- Principles of method if other than guideline:
- (Q)SAR - SPARC
- Specific details on test material used for the study:
- SMILES: C1N(C)CN(C)CN1C
- Dissociating properties:
- yes
- No.:
- #1
- pKa:
- ca. 9.5
- Temp.:
- 25 °C
- Remarks on result:
- other: QSAR Predicted Value
- Conclusions:
- SPARC estimated the macro pKa to be 9.5.
- Executive summary:
Accurate values for the pKa of hexahydro-1,3,5 -trimethyl-1,3,5 -triazine were difficult to determine using classic experimental methodology due to hydrolysis at low pH. Structural modelling provided an overall pKa pf 9.5.
- Endpoint:
- dissociation constant
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- Not reported
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- significant methodological deficiencies
- Remarks:
- The effect of hydrolysis of hexahydro-1,3,5-trimethyl-1,3,5-triazine is suspected to have interfered with the titration results.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 112 (Dissociation Constants in Water)
- GLP compliance:
- no
- Dissociating properties:
- yes
- No.:
- #1
- pKa:
- ca. 7.1
- Temp.:
- 20 °C
- Remarks on result:
- other: Titration (Methodology 1)
- No.:
- #1
- pKa:
- 8.69
- Temp.:
- 20 °C
- Remarks on result:
- other: Molar Solution (Methodology 2)
- Conclusions:
- Compared to the SPARC models the unhydrolysed value is lower than predicted but much nearer than the titrimetric value. This supports the theory of hydrolysis of this molecule in the “real world” situation. The true value must lie between 7 and 9 and would allow a conclusion to support an assertion that the pKa is not within physiological relevance (i.e. >6).
Referenceopen allclose all
Methodology (1)
Titration method: pKa = 7.1
Methodology (2)
pKa estimate from molar solutions:
Sample 1 pKa = 8.54
Sample 2 pKa = 8.39
The SPARCs model prediction for the first ionisation of MMA Tz gives a value of pKa = 9.5
The dilution method above gives a value of 8.69 which is approximately half an order of magnitude below the SPARCS model and magnitude ~ 1.5 above the titrimetric determination.
This result adds weight to the hypothesis of facile hydrolysis of the parent triazine in dilute aqueous solution (assuming the SPARC model is accurate).
Plotting both pKa values as a function of concentration and extrapolating to zero concentration (infinite dilution) gives a value of pKa = 8.69
Description of key information
pKa = 7 - 9, OECD 112, Mountford (2010)
pKa = 8.5, SPARC, Hargreaves (2010)
Key value for chemical safety assessment
- pKa at 20°C:
- 8.5
Additional information
Accurate values for the pKa for hexahydro-1,3,5-trimethyl-1,3,5-triazine were difficult to determine using classic experimental methodology due to hydrolysis at low pH. Using the titration method, pKa was estimated to be 7.1. Structural modelling provided an overall pKa of 9.5 and pKa estimated from the pH of molar solutions was estimated to be 8.69. Based on a weight-of-evidence approach, the pKa of hexahydro-1,3,5-trimethyl-1,3,5-triazine is between 7-9.5, with typical values being approximately 8.5.
There are considerable differences between the modelled and laboratory results for pKa. This is possibly due to interferences in the method, caused by the hydrolysis of hexahydro-1,3,5 -trimethyl-1,3,5 -triazine at low pH and the formation of methylmethylenimine (N-methylmethanimine). Using identical modelling procedures to those used for hexahydro-1,3,5 -trimethyl-1,3,5 -triazine, the pKa of methylmethylenemine was estimated to be 6.91, which is close to that obtained using the titration method.
To investigate the pKa further with minimal interference from methylmethyleneimine, pKa of hexahydro-1,3,5 -trimethyl-1,3,5 -triazine was estimated from the pH of solution with a known molar concentration. This exercise was conducted twice for hexahydro-1,3,5 -trimethyl-1,3,5 -triazine at molar solutions of 0.10 and 0.202, pH was measured as 10.77 and 10.85 respectively. From these solutions, pKa was estimated to be 8.54 and 8.39. Plotting both pKa values as a function of concentration and extrapolation to zero concentration (infinite dilution) gives a value pKa = 8.69.
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