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EC number: 206-108-6 | CAS number: 301-10-0
- 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
Partition coefficient
Administrative data
Link to relevant study record(s)
- Endpoint:
- partition coefficient
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data from published review article of critically-evaluated log Kow values.
- Justification for type of information:
- Read Across to an analogue based on structural similarity. An analogue justification is attached to section 13 of the dataset.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Principles of method if other than guideline:
- details of method not given
- GLP compliance:
- no
- Type of method:
- shake-flask method to: flask method
- Partition coefficient type:
- octanol-water
- Type:
- log Pow
- Partition coefficient:
- 2.64
- Temp.:
- 25
- Remarks on result:
- other: pH not reported, however, it is noted that meaurement was performed at pH where substance is not ionized.
- Details on results:
- The confidence interval around the reported log Kow value is ± 0.25 (log units)
- Conclusions:
- The log Kow of 2-ethylhexanoic acid is 2.64.
- Executive summary:
The log Kow of 2-ethylhexanoic acid is 2.64. Because this value is the preferred/accepted value among those critically reviewed by Sangster (1989) and Hansch et al. (1995), the determination is assumed to be made at 25 °C and pH where the substance is not ionized. The log D for this substance at pH 7 is estimated to be 0.55 (ACD Labs Log D Suite, v5.16). Therefore, at pH encountered in the environment, the substance will have very low potential for adsorption to organic matter of soils/sediments, or to bioaccumulate in aquatic organisms.
- Endpoint:
- partition coefficient
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data from published review article of critically-evaluated log Kow values.
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
[Please provide information for all of the points below. Indicate if further information is included as attachment to the same record, or elsewhere in the dataset (insert links in 'Cross-reference' table)]
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
Tin bis(2-ethylhexanoate) is an organometallic salt and has a pKa value of 5.09 (please see IUCLID dataset). Under the pH conditions typically occurring in the environment (i.e., pH 6-8), the substance is known to rapidly dissociate into two components, namely 2-ethylhexanoate ion and Sn(II) ion, upon introduction to water. Sn(II) ion is not expected to be stable in water at typical environmental conditions and is likely to be oxidized in the presence of molecular oxygen to form the insoluble inorganic solid Sn(IV)O2 (Pettin et al., 1981; Seby, 2001), which is not expected to be bioavailable to aquatic life (Rudel, 2003).
Tin bis(2-ethylhexanoate) will not exist in any relevant concentrations for a relevant duration in the environment and for a series of endpoints testing of tin bis(2-ethylhexanoate) is technically not feasible due to the rapid dissociation. Where no specific data are available, the assessment of environmental and human health endpoints should be based on its dissociation products. The dissociation products of toxicological relevance are 2-ethylhexanoate and Sn(II) components.
As a result, 2-ethyhexanoic acid and tin(II) chloride shall be used as read-across analogue for tin bis(2-ethylhexanoate) where no specific data are available.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
2-ethylhexanoic acid (CAS 149-57-5)
Tin(II) chloride (CAS 7772-99-8)
Purity of tin(II) bis(2-ethylhexanoate) is >= 92.5%.
Purity of 2-ethylhexanoic acid is 99.9%.
Purity of tin(II) chloride is 98.5%.
3. ANALOGUE APPROACH JUSTIFICATION
Tin bis(2-ethylhexanoate) is an organometallic salt with a dissociation constant of 5.09 at 20 °C. The dissociation study is included in IUCLID dataset. When introduced to water, more than 99% of tin bis(2-ethylhexanoate) will dissociate into 2-ethylhexanoate and Sn(II) components at pH > 6.8.
At environmentally relevant conditions, Sn(II) ion is not expected to be stable in water and is likely to be oxidized in the presence of molecular oxygen to form the insoluble inorganic solid Sn(IV)O2 (Pettin et al., 1981; Seby, 2001,), which is not expected to be bioavailable to aquatic life (Rudel, 2003).
Since tin bis(2-ethylhexanoate) is primarily in a dissociated form in the environment, the observed toxicity is likely dependent upon the toxicities for the respective acid and metal. Thus, where no specific data are available, the assessment of environmental and human health endpoints should be based on its dissociation components, namely Sn(II) in the form of Tin(II) chloride and 2-ethylhexanoic acid.
4. DATA MATRIX
Please refer to justification, attached to this section. - Reason / purpose for cross-reference:
- read-across source
- Principles of method if other than guideline:
- details of method not given
- GLP compliance:
- no
- Type of method:
- shake-flask method to: flask method
- Partition coefficient type:
- octanol-water
- Type:
- log Pow
- Partition coefficient:
- 2.64
- Temp.:
- 25 °C
- Remarks on result:
- other: pH not reported, however, it is noted that meaurement was performed at pH where substance is not ionized.
- Details on results:
- The confidence interval around the reported log Kow value is ± 0.25 (log units)
- Conclusions:
- The log Kow of 2-ethylhexanoic acid is 2.64.
- Executive summary:
The log Kow of 2-ethylhexanoic acid is 2.64. Because this value is the preferred/accepted value among those critically reviewed by Sangster (1989) and Hansch et al. (1995), the determination is assumed to be made at 25 °C and pH where the substance is not ionized. The log D for this substance at pH 7 is estimated to be 0.55 (ACD Labs Log D Suite, v5.16). Therefore, at pH encountered in the environment, the substance will have very low potential for adsorption to organic matter of soils/sediments, or to bioaccumulate in aquatic organisms.
- Endpoint:
- partition coefficient
- Data waiving:
- study technically not feasible
- Justification for data waiving:
- the study does not need to be conducted because the substance is inorganic
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
[Please provide information for all of the points below. Indicate if further information is included as attachment to the same record, or elsewhere in the dataset (insert links in 'Cross-reference' table)]
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
Tin bis(2-ethylhexanoate) is an organometallic salt and has a pKa value of 5.09 (please see IUCLID dataset). Under the pH conditions typically occurring in the environment (i.e., pH 6-8), the substance is known to rapidly dissociate into two components, namely 2-ethylhexanoate ion and Sn(II) ion, upon introduction to water. Sn(II) ion is not expected to be stable in water at typical environmental conditions and is likely to be oxidized in the presence of molecular oxygen to form the insoluble inorganic solid Sn(IV)O2 (Pettin et al., 1981; Seby, 2001), which is not expected to be bioavailable to aquatic life (Rudel, 2003).
Tin bis(2-ethylhexanoate) will not exist in any relevant concentrations for a relevant duration in the environment and for a series of endpoints testing of tin bis(2-ethylhexanoate) is technically not feasible due to the rapid dissociation. Where no specific data are available, the assessment of environmental and human health endpoints should be based on its dissociation products. The dissociation products of toxicological relevance are 2-ethylhexanoate and Sn(II) components.
As a result, 2-ethyhexanoic acid and tin(II) chloride shall be used as read-across analogue for tin bis(2-ethylhexanoate) where no specific data are available.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
2-ethylhexanoic acid (CAS 149-57-5)
Tin(II) chloride (CAS 7772-99-8)
Purity of tin(II) bis(2-ethylhexanoate) is >= 92.5%.
Purity of 2-ethylhexanoic acid is 99.9%.
Purity of tin(II) chloride is 98.5%.
3. ANALOGUE APPROACH JUSTIFICATION
Tin bis(2-ethylhexanoate) is an organometallic salt with a dissociation constant of 5.09 at 20 °C. The dissociation study is included in IUCLID dataset. When introduced to water, more than 99% of tin bis(2-ethylhexanoate) will dissociate into 2-ethylhexanoate and Sn(II) components at pH > 6.8.
At environmentally relevant conditions, Sn(II) ion is not expected to be stable in water and is likely to be oxidized in the presence of molecular oxygen to form the insoluble inorganic solid Sn(IV)O2 (Pettin et al., 1981; Seby, 2001,), which is not expected to be bioavailable to aquatic life (Rudel, 2003).
Since tin bis(2-ethylhexanoate) is primarily in a dissociated form in the environment, the observed toxicity is likely dependent upon the toxicities for the respective acid and metal. Thus, where no specific data are available, the assessment of environmental and human health endpoints should be based on its dissociation components, namely Sn(II) in the form of Tin(II) chloride and 2-ethylhexanoic acid.
4. DATA MATRIX
Please refer to justification, attached to this section.
Referenceopen allclose all
Description of key information
The substance decomposes when coming into contact with water. Therefore the decomposition products Sn(II)O and 2 -ethylhexanoic acid have to be adressed:
1. 2 -ethylhexanoic acid:
The log Kow of 2-ethylhexanoic acid is 2.64. Because this value is the preferred/accepted value among those critically reviewed by Sangster (1989) and Hansch et al. (1995), the determination is assumed to be made at 25 °C and pH where the substance is not ionized. The log D for this substance at pH 7 is estimated to be 0.55 (ACD Labs Log D Suite, v5.16). Therefore, at pH encountered in the environment, the substance will have very low potential for adsorption to organic matter of soils/sediments, or to bioaccumulate in aquatic organisms.
2. Partition Coefficient for Sn(II) part of salt:
Waived, as this property is not required nor
relevant for an insoluble inorganic species.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 2.64
- at the temperature of:
- 25 °C
Additional information
When introduced to water, the Tin bis(2-ethylhexanoate) substance will dissociate (99% dissociated at pH > 6.8), where the Sn(II) will be initially speciated as the Sn(OH)2 substance, which will be oxidized in oxygenated solutions to become the insoluble solid SnO2. The 2-ethyl hexanoic acid part of the salt has its maximum water solubility at pH > 6.8, where it exists completely as the ethyl hexanoate anion. By definition, log Kow must be determined at pH where an ionizable substance is fully neutralized, in this case, pH < 2.8. The reported log Kow of 2-ethylhexanoic acid is 2.64. Because this value is the preferred/accepted value among those critically reviewed by Sangster (1989) and Hansch et al. (1995), the determination is assumed to be made at 25 °C and pH where the substance is not ionized. The distribution coefficient log D for this substance at pH 7 is estimated to be 0.55 (ACD Labs Log D Suite, v5.16). Therefore, at pH encountered in the environment, the substance will have very low potential for adsorption to organic matter of soils/sediments, or to bioaccumulate in aquatic organisms.
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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