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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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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
Phototransformation in air
Administrative data
Link to relevant study record(s)
- Endpoint:
- phototransformation in air
- Type of information:
- calculation (if not (Q)SAR)
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Accepted calculation/estimation method, as recommended in ECHA Chapter 7 guidance (May 2008).
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Principles of method if other than guideline:
- The second-order rate constant for reaction with photochemically-generated hydroxyl radical (indirect photolysis) was estimated using U.S. EPA AOPWIN software v1.92a (June 2008). The associated atmospheric half-life was calculated from an assumed average hydroxyl radical concentration of 500,000 molecules/cm3 and 24 hr. day (ECHA recommended values).
- GLP compliance:
- no
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not applicable - Estimation method (if used):
- U.S. EPA AOPWIN software v1.92a (June 2008).
Assumed hydroxyl radical concentration of 500,000 molecules/cm3 and 24 hr photoday - Light source:
- other: sunlight irradiance producing default tropospheric hydroxyl radical concentration of 500,000 molecules/cm3
- Details on light source:
- not applicable
- Details on test conditions:
- Half-lives calculated from estimated second-order rate constant, default hydroxyl radical concentration of 500,000 molecules/cm3, and 24-hr. photoday.
- Preliminary study:
- not applicable
- Test performance:
- not applicable
- DT50:
- 1.6 d
- Test condition:
- Estimated half-life for reaction with hydroxyl radical (500,000 OH molecules/cm3) over 24 hr photoday
- Transformation products:
- not measured
- Results with reference substance:
- Butyric acid (CASRN 107-92-6)
SMILES: O=C(O)CCC
Experimental Rate Constant: 2.4 x 10-12 cm3/molecule*sec
Half-life based on experimental rate constant: 160 hrs (6.7 days)
Predicted Rate Constant: 2.7 x 10-12 cm3/molecule*sec
Half-life based on predicted rate constant: 142 hrs (5.9 days)
The prediction is accurate within a factor of 2 for estimating second-order rate constant of OH radical and organic acids such as butyric acid and 2-ethyl hexanoic acid - Validity criteria fulfilled:
- not applicable
- Conclusions:
- The estimated atmospheric half-life for Stannous Octoate is 1.6 days, indicating that the substance will not behave as a persistent atmospheric pollutant if emitted to the air. This half-life is < 2 days, and therefore the substance is not regarded as having potential for long-range transport in the atmosphere.
Reference
The predicted second-order rate constant for reaction of OH radical with Stannous Octoate is 9.9 x 10 -12 cm3/molecule*sec. This rate constant equates to an estimated half-life of 38.9 hrs, or 1.6 days; assuming an OH radical concentration of 500,000 molecules/cm3.
Description of key information
The predicted second-order rate constant for reaction of OH radical with tin bis(2-ethylhexanoate) is 9.9 x 10-12 cm³/molecule*sec. This rate constant equates to an estimated half-life of 38.9 hrs, or 1.6 days; assuming an OH radical concentration of 500,000 molecules/cm3.
Key value for chemical safety assessment
- Half-life in air:
- 38.9 h
- Degradation rate constant with OH radicals:
- 0 cm³ molecule-1 s-1
Additional information
The estimated atmospheric half-life for tin bis (2-ethylhexanoate) is 1.6 days, indicating that the substance will not behave as a persistent atmospheric pollutant if emitted to the air. This half-life is < 2 days, and therefore the substance is not regarded as having potential for long-range transport in the atmosphere.
The training set used to develop the AOPWIN algorithm does not include other Sn(II) organometallic compounds. However, since the mode of reactivity for the tin bis (2-ethylhexanoate) molecule with hydroxyl radical is dominated by reactions with the 2-ethyl hexanoate part (i.e., hydrogen abstraction), the presence of the Sn atom is not expected to result in decreased accuracy of the prediction. The accuracy of this prediction of the second-order rate constant for organic acids was demonstrated by comparing experimental and predicted rate constants for butyric acid. The predicted value deviates from the experimental value by only 12 %.
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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