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EC number: 618-804-0 | CAS number: 919-94-8
- 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
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: QSAR, published in peer reviewed literature, adequate for assessment.
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
Data source
Reference
- Reference Type:
- publication
- Title:
- A simple dermal absorption model: Derivation and application
- Author:
- ten Berge, W.
- Year:
- 2 009
- Bibliographic source:
- Chemosphere 75, 1440-1445
Materials and methods
- Principles of method if other than guideline:
- Dermal absorption was predicted using a QSAR.
- GLP compliance:
- no
Test material
- Reference substance name:
- 2-ethoxy-2-methylbutane
- EC Number:
- 618-804-0
- Cas Number:
- 919-94-8
- Molecular formula:
- C7H16O
- IUPAC Name:
- 2-ethoxy-2-methylbutane
Constituent 1
Results and discussion
Any other information on results incl. tables
The model predicted a permeability coefficient of 0.0835 cm/hour. For the calculation of the percentage absorption, an aqueous Kp of 0.0835 cm/hour was used.
Derivation of the initial absorption
As is deduced in EHC 235 (2006), the following equation is true:
Kp= Km* D/h [1]
(Kpis the permeability coefficient; Kmis the pseudo-homogeneous partition, or distribution coefficient between the stratuionm corneum and the vehicle; D is the effective diffusion coefficient; h is the membrane thickness)
To derive the Kpfor the neat substance, the aqueous Kphas to be divided by the stratum corneum/water partition coefficient (Km). The Km(stratum corneum/water) for TAEE was calculated to be 16.3 by using the QSAR described by ten Berge (2009).
Since the aqueous Kpwas 0.0835 cm/hour, the Kpfor neat liquid is: 0.0835 / 16.3 = 0.00513 cm/hour.
To derive the initial absorption of neat TAEE, the Kpfor neat liquid has to be multiplied by the density. The density of TAEE is 764 mg/cm3.
Therefore the initial absorption of neat TAEE is 0.0835 cm/hour x 764 mg/cm3= 3.91 mg/cm2/hour
The above mentioned explanation can alternatively be expressed as follows:
Initial absorption (mg/cm2/hr) = rholiquid* (D/h) [2]
(rholiquidis the density of the liquid (mg/m3); D is the diffusion coefficient of the liquid in the stratum corneum (cm2/hr); h is the tickness of the stratum corneum)
D/h = Kp/Km [3]
(Kpis the permeability coefficient; Kmi s the stratum corneum/water partition coefficient)
Substitution of equation 3 in 2 gives:
Initial absorption (mg/cm2/hr) = rholiquid* Kp/Km [4]
The density of TAEE is764 mg/cm3; the Kpand Kmwere determined to be 0.0835 cm/hour and 16.3, respectively.
As such, the initial absorption (mg/cm2/hr) = 764 * 0.0835/16.3 = 3.91 mg/cm2/hour
In conclusion, the initial absorption of neat TAEE is 3.91 mg/cm2/hour.
Correction for evaporation
Since TAEE is very volatile, a strong competition between evaporation and skin absorption will occur in case the skin is exposed to neat TAEE.
Based on the REACH Guidance appendix R14.1, it was calculated that the evaporation rate of TAEE is 219 mg/cm2/hour.
Therefore, of each dose of TAEE exposed to the skin 1.8% (3.91/219) is available for skin absorption because of the majority of the TAEE evaporates before absorption can occur.
As such, the percentage of dermal absorption of TAEE is assumed considered to be 1.8%. For the calculation of the dermal DNEL, a percentage of dermal absorption of 2% is used (as a worst case figure).
In conclusion, the percentage of dermal absorption of TAEE is 2%.
References
EHC 235 Environmental Health Criteria 235: Dermal Absorption, World Health Organization 2006.
ten Berge W, 2009. A simple dermal absorption model: derivation and application. Chemosphere 75(11), 1440-5.Applicant's summary and conclusion
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