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Diss Factsheets
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EC number: 204-791-5 | CAS number: 126-53-4
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The result is based on a well documented QSAR model and the properties of the substance fall well within the applicability domain of the model.
- Justification for type of information:
- QSAR prediction
- Qualifier:
- according to guideline
- Guideline:
- other: The QSAR is based on similarities with Kow and is described in W.J. Doucette, Soil and sorption coefficients. In handbook of property estimation methods, Boethling and Mackay, ISBN 1-56670-456-1, 1990
- Principles of method if other than guideline:
- For polar and non polar compounds, different QSARS were derived, but both based on the log Kow values. AS TMP-pelargonate is polar the QSAR for polar compounds must be used. This is a well defined and straightforward equation, based on the log Kow values:
log Koc = 0.55313 log Kow + 0.9521 + sum of corrections
Corrections are based on the chemical structure of the compound. - Type of method:
- other: QSAR
- Radiolabelling:
- no
- Test temperature:
- The QSAR is applicable for ambient temperatures
- Details on study design: HPLC method:
- not applicable
- Analytical monitoring:
- not required
- Details on sampling:
- not applicable
- Details on matrix:
- not applicable
- Details on test conditions:
- not applicable
- Type:
- log Koc
- Value:
- 6.701 L/kg
- Details on results (HPLC method):
- not applicable
- Adsorption and desorption constants:
- not applicable
- Recovery of test material:
- not applicable
- Concentration of test substance at end of adsorption equilibration period:
- not applicable
- Concentration of test substance at end of desorption equilibration period:
- not applicable
- Transformation products:
- no
- Details on results (Batch equilibrium method):
- not applicable
- Statistics:
- not applicable
- Validity criteria fulfilled:
- yes
- Conclusions:
- The log Koc of Tripelargonin as calculated with a QSAR (based on the log Kow) equals 6.7013
- Executive summary:
log Koc was calculated with a QSAR based on the log Kowvalue of Tripelargonin (10.68). The log Koc value is calculated as 6.7013
.
The value is considered reliable as the QSAR has a well defined algorithm and taking into account that Tripelargonin falls well within the applicability domain of the model and the good SD of model predictions against experimental results.
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study result is based on a QSAR, with a well documented model and the properties of the substance well within the applicability domain of the model.
- Justification for type of information:
- QSAR prediction
- Qualifier:
- according to guideline
- Guideline:
- other: The Molecular connectivity index approach was used, as was described by Meylan et al; Environmental Science and Technology, 26, 1560 - 1567, 1992
- Principles of method if other than guideline:
- The molecular connectivity (MCI) approach is used to derive the appropriate Koc value. For non-polar compounds the QSAR has a simple linear form: log Koc = 0.5213 MCI + 0.60. For more polar compounds corrections are made for the polar groups.
- Type of method:
- other: QSAR
- Media:
- other: QSAR
- Test temperature:
- The QSAR is applicable to ambient temperatures
- Details on study design: HPLC method:
- not applicable
- Analytical monitoring:
- not required
- Details on sampling:
- not applicable
- Details on matrix:
- not applicable
- Details on test conditions:
- not applicable
- Type:
- log Koc
- Value:
- 7.143 L/kg
- Details on results (HPLC method):
- not applicable
- Adsorption and desorption constants:
- not applicable
- Recovery of test material:
- not applicable
- Concentration of test substance at end of adsorption equilibration period:
- not applicable
- Concentration of test substance at end of desorption equilibration period:
- not applicable
- Details on results (Batch equilibrium method):
- not applicable
- Statistics:
- not applicable
- Validity criteria fulfilled:
- yes
- Conclusions:
- With the MCI QSAR a log KOC of 7.1430 was calculated.
- Executive summary:
EPI Suite v4.10 was used to calculate the log Koc value of Tripelargonin. The QSAR is based on the well documented MCI model and the resulting log Koc equals 7.1430.
For this property of the compound, the model has a well defined algorithm. The physical and chemical properties of TBP fall well within the the molecular weight of the training and validation dataset. The training dataset consists of 447 compounds of which some have similar structures. The plot of experimental log Koc against modelled Koc has an R2 of 0.90, a SD of 0.34 and an average deviation of 0.273. Therefore the calculated value of log Koc can be considered to be reliable.
Referenceopen allclose all
EPI Suite vs 4.10 was used to calculate the log Koc value of Tripelargonin. The approach is based on a well documented QSAR, which results in a log Koc of 6.7013
for Tripelargonin.
The model has a clear algorithm for this property of the compound. Currently there is no well defined model domain, however the modelling results will be less reliable if the molecular weight is not in the range of the molecular weights of the training and validation dataset. The molecular weight of Tripelargonin falls well within the the molecular weight of the training and validation dataset.
The training dataset consists of 447 compounds of which some have similar structures to Tripelargonin The plot of experimental log Koc against modelled Koc has an R2 of 0.855, a SD of 0.396 and an average deviation of 0.307.
The MCI model has a clear algorithm for this defined property of the compound. Currently there is no well defined model domain, however the modelling results will be less reliable if the molecular weight is not in the range of the molecular weights of the training and validation dataset. It should be noticed that the molecular weight of Tripelargonin falls within the boundaries of molecular weight of the training set but not within the validation dataset.
The training dataset consists of 447 compounds of which some have similar structures to Tripelargonin. The plot of experimental log Koc against modelled Koc has an R2 of 0.90, a SD of 0.34 and an average deviation of 0.273.
Description of key information
EPI Suite v4.10 was used to calculate the log Koc value of Tripelargonin.
The QSAR is based on the well documented MCI model and the resulting log Koc equals 7.87. In addition, log Koc was calculated with a QSAR based on the log Kow value of TMP-Pelargonate (12.11).
The log Koc value calculated with that method was 7.49. The value used for risk assessment purposes, is the average of both.
Key value for chemical safety assessment
- Koc at 20 °C:
- 9 463 500
Additional information
The medium value of the two available Log Koc was used for the assessment
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