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Diss Factsheets
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EC number: 221-975-0 | CAS number: 3302-10-1
- 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
- Remarks:
- adsorption
- Type of information:
- calculation (if not (Q)SAR)
- Adequacy of study:
- key study
- Study period:
- 2019
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Scientifically accepted estimation method
- Reason / purpose for cross-reference:
- other: log Pn input parameter for the calculation
- Reason / purpose for cross-reference:
- other: pKa input parameter for the calculation
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Calculation method determining the Koc for charged molecules according to Franco & Trapp (2008), Franco, Fu and Trapp (2009) and additional information via personal communication from A. Franco (2010).
- GLP compliance:
- no
- Type of method:
- other: calculation of log Koc for ionized molecule
- Media:
- soil
- Radiolabelling:
- no
- Test temperature:
- not applicable, calculation
- Details on study design: HPLC method:
- not applicable, calculation
- Analytical monitoring:
- not required
- Details on sampling:
- not applicable, calculation
- Details on matrix:
- not applicable, calculation
- Details on test conditions:
- not applicable, calculation
- Computational methods:
- The following input parameters were used for the calculation:
1. Test substance is an acid.
2. Octanol-water partition coefficient for the neutral molecule, Pn= Kow (neutral). This value was determined in a reliable study (OECD 117) at acidic pH (pH 3.0), such that nearly 100% of molecules were in the neutral, non-dissociated state.
log Kow (neutral) = logPn = 3.2
3. Dissociation constant
pKa was determined in a reliable study (OECD 112, titration method) to be 4.8.
pKa = 4.8
For further details, see IUCLID section "Any other information on materials and methods incl. tables". - Sample No.:
- #1
- Type:
- Koc
- Value:
- 79.5 L/kg
- pH:
- 8
- Temp.:
- 20 °C
- Matrix:
- Soil
- Sample No.:
- #2
- Type:
- Koc
- Value:
- 92.9 L/kg
- pH:
- 7
- Temp.:
- 20 °C
- Matrix:
- Soil
- Key result
- Sample No.:
- #5
- Type:
- Koc
- Value:
- 122.9 L/kg
- pH:
- 6.5
- Temp.:
- 20 °C
- Matrix:
- Soil
- Sample No.:
- #3
- Type:
- Koc
- Value:
- 200.6 L/kg
- pH:
- 6
- Temp.:
- 20 °C
- Matrix:
- Soil
- Sample No.:
- #4
- Type:
- Koc
- Value:
- 620.4 L/kg
- pH:
- 4.5
- Temp.:
- 20 °C
- Matrix:
- Soil
- Details on results (HPLC method):
- not applicable, calculation
- Statistics:
- not applicable, calculation
- Validity criteria fulfilled:
- not applicable
- Remarks:
- estimation method
- Conclusions:
- The Koc for 3,5,5-trimethylhexanoic acid was estimated by calculation as a function of soil pH using the method of Franco, Fu and Trapp (2009), with the following results (OXEA, 2019):
pH 8.0: 79.5 L/kg
pH 7.0: 92.9 L/kg
pH 6.5: 122.9 L/kg
pH 6.0: 200.6 L/kg
pH 4.5: 620.4 L/kg - Executive summary:
The Koc for 3,5,5-trimethylhexanoic acid was estimated by calculation as a function of soil pH using the method of Franco, Fu and Trapp (2009).
The model considers as the main parameters governing adsorption the log Kow of the neutral compound (logPn = 3.2, determined experimentally) as well as the dissociation degree, characterized by pKa (4.8, determined experimentally) and the prevailing soil pH. As such, adsorption of a compound to soil is broken down into the sum of adsorption of the neutral species multiplied by the non-dissociated fraction and the adsorption of the ionized species multiplied by the dissociated (ionized) fraction at a given soil pH. The model allows calculation of Koc as a function of soil pH, with the following results obtained for 3,5,5-trimethylhexanoic acid (OXEA, 2019):
pH 8.0: 79.5 L/kg
pH 7.0: 92.9 L/kg
pH 6.5: 122.9 L/kg
pH 6.0: 200.6 L/kg
pH 4.5: 620.4 L/kg
For environmental exposure and risk assessment, the value of (rounded) 123 L/kg obtained for Koc at soil pH 6.5 is regarded to be most relevant, because European soils are predominantly of neutral to slightly acidic pH.
Reference
Description of key information
The Koc for 3,5,5-trimethylhexanoic acid was estimated by calculation as a function of soil pH using the method of Franco, Fu and Trapp (2009), with the following results (OXEA, 2019):
pH 8.0: 79.5 L/kg
pH 7.0: 92.9 L/kg
pH 6.5: 122.9 L/kg - key value for agricultural soils in Europe
pH 6.0: 200.6 L/kg
pH 4.5: 620.4 L/kg
Key value for chemical safety assessment
- Koc at 20 °C:
- 123
Additional information
The Koc for 3,5,5-trimethylhexanoic acid was estimated by calculation as a function of soil pH using the method of Franco, Fu and Trapp (2009).
The model considers as the main parameters governing adsorption the log Kow of the neutral compound (logPn = 3.2, determined experimentally) as well as the dissociation degree, characterized by pKa (4.8, determined experimentally) and the prevailing soil pH. As such, adsorption of a compound to soil is broken down into the sum of adsorption of the neutral species multiplied by the non-dissociated fraction and the adsorption of the ionized species multiplied by the dissociated (ionized) fraction at a given soil pH. The model allows calculation of Koc as a function of soil pH, with the following results obtained for 3,5,5-trimethylhexanoic acid (OXEA, 2019):
pH 8.0: 79.5 L/kg
pH 7.0: 92.9 L/kg
pH 6.5: 122.9 L/kg
pH 6.0: 200.6 L/kg
pH 4.5: 620.4 L/kg
For environmental exposure and risk assessment, the value of (rounded) 123 L/kg obtained for Koc at soil pH 6.5 is regarded to be most relevant, because European soils are predominantly of neutral to slightly acidic pH.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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