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EC number: 500-234-8 | CAS number: 68891-38-3 1 - 2.5 moles ethoxylated
- 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
Additional physico-chemical information
Administrative data
- Endpoint:
- other: Membrane-water partition co-efficient
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 06 Feb 2023
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Cross-reference
- Reason / purpose for cross-reference:
- other: Specific composition tested
Reference
- Name:
- SLES (PSL 2EO)
- Type of composition:
- legal entity composition of the substance
- State / form:
- liquid
- Related composition:
- Alcohols, C12-14, ethoxylated, sulfates, sodium salts - Consortium boundary
- Alcohols, C12-14, ethoxylated, sulfates, sodium salts - Unilever
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
- Reference substance:
- SLES (PSL 2EO)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 023
- Report date:
- 2023
Materials and methods
- Principles of method if other than guideline:
- Stock solutions (~1 mM) of Alcohols, C12-14, ethoxylated, sulfates, sodium salts (hereafter referred to as SLES) were prepared in deionised water, and then further diluted in 2-oleoyl-1-palmitoyl-sn-glycero-3-phosphocholine (POPC) medium for donor tissue samples or phosphate-buffered saline (PBS) for reference controls.
Prepared donor, controls and PBS blank solutions (400µL) were added to the red well of the rapid equilibrium dialysis (RED) plate, with PBS buffer (600µL) added to the white well. The plate was sealed and incubated at 37ºC. on an orbital shaker at ~80 rpm to allow equilibration through the membrane between the two wells. After removal from the incubator, and equilibration to room temperature, aliquots were taken to an autosampler vial. Acetonitrile was added, before a brief vortex prior to analysis.
Analysis was conducted on both red and white wells for control samples and blanks prepared in PBS and only the white wells for donor samples. Various concentrations of donor dose concentrations and incubation times have been used.
Analysis was carried out by Liquid Chromatography with Electrospray triple quadrupole detection. Identification was by using Multiple reaction monitoring (MRM), a highly sensitive method of targeted mass spectrometry (MS). Quantitation is carried out by mixed analyte external calibration curve. Data reported is of multiple analyses. - GLP compliance:
- no
- Remarks:
- Study does not make any claim of GLP compliance however it was conducted according to the principles of GLP within a GLP accredited laboratory.
Test material
- Reference substance name:
- Alcohols, C12-14, ethoxylated, sulfates, sodium salts
- EC Number:
- 500-234-8
- EC Name:
- Alcohols, C12-14, ethoxylated, sulfates, sodium salts
- Cas Number:
- 68891-38-3
- Molecular formula:
- not applicable, UVCB
- IUPAC Name:
- Alcohols, C12-14(even numbered), ethoxylated < 2.5 EO, sulfates, sodium salts
- Test material form:
- liquid: viscous
- Remarks:
- Very viscous liquid
- Details on test material:
- Molecular weight: 367 g/mol
Expiry Date: 01/10/2023
Constituent 1
Results and discussion
- Results:
- Analysis is carried out on both blanks, controls and donor samples, where blanks have no test material, controls have no liposome, and donor samples that contain both. The Limit of quantitation (LOQ) is determined from the blank sample and defined as the concentration of the calibration standard that has an area 3 x carryover/blank level.
The data reported is where the incubation time has demonstrated equilibrium of concentration by analysis of red and white well data for the control samples. The control white well is considered the nominal concentration for the calculation. This assumes any losses due to non-liposome effects, i.e. plastic binding are equivalent to those seen in the donor samples.
All valid data are included below, demonstrating the need to ensure both equilibrium between the red and white portion of the control cells and also understand the background levels of each individual component. Different incubation times and concentrations of dose appear to impact the calculated LogKmw. It is not clear if this is an actual effect or method variability.
Any other information on results incl. tables
Calculated LogKmw
SLES @200 n=2 |
SLES C14 @400 n=3 | |
| ||
C12 AS | 4.44 |
|
C14 AS | 5.13 | |
|
|
|
C12EO1 | 4.70 |
|
C12EO2 | 4.60 |
|
C12EO3 | 4.41 |
|
C12EO4 | 4.06 |
|
|
|
|
C14EO1 | <LOQ | 5.22 |
C14EO2 | <LOQ | 5.16 |
C14EO3 | <LOQ | 4.95 |
C14EO4 | <LOQ | 5.15 |
Calculations
LogKmw = log10 {c_membrane / (n_water x dilution from well x 0.000000001)}
c_membrane = {n_membrane / (Conc Liposome mM) x (vol Liposome mL) x (mwt Liposome) x 0.0000001}
n_membrane = n_dose - n_water
n_dose = measured data from white control well x dilution from well
n_water = measured data from white donor well x dilution from well
Applicant's summary and conclusion
- Conclusions:
- To support (Q)SAR predictions for aquatic toxicity, membrane-water partition co-efficients ranging from 4.06 to 5.22 were determined for the components of a representative specification of SLES.
- Executive summary:
An analytical study was conducted to generate membrane-water partition co-efficient values for the components of a representative specification of SLES. The resulting values, ranging from 4.06 to 5.22, were taken forward as part of (Q)SAR predictions for the aquatic toxicity of this substance.
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