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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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption, other
- Remarks:
- adsorption
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Remarks:
- Some of the constituents of the substance are not fully compliant with the applicability domain of the model. The maximum occurrence of aliphatic ether groups –C-O-C- in the training set of the model is equal to 2. Thus, constituents with an ethoxylation degree EO > 2 are outside the applicability domain of the model. However, this calculation is used in a weight of evidence approach, in accordance to the REACh Regulation (EC) No 1907/2006, Annex XI section 1.2. It is adequately documented and justified. For more details please refer to the model description and the complete prediction report in the section `Attached justification´.
- Justification for type of information:
- 1. SOFTWARE
EPI Suite v4.11 (June 2017) Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11 (June 2017). US EPA, United States Environmental Protection Agency, Washington, DC, USA.
2. MODEL (incl. version number)
KOCWIN v2.01, Log Kow based model.
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
See “Test material information”.
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
See attached information on the model provided by the developer. Further information on the OECD criteria as outlined by the applicant is provided below under "Any other information of materials and methods incl. tables".
5. APPLICABILITY DOMAIN
See attached information and information as provided in "Any other information on results incl. tables".
6. ADEQUACY OF THE RESULT
See assessment of adequacy as outlined in the "Overall remarks, attachments" section. - Qualifier:
- according to guideline
- Guideline:
- other: REACH Guidance on QSARs and grouping of chemicals (R.6)
- Principles of method if other than guideline:
- - Software tool(s) used including version: EPI Suite v4.11 (June 2017)
- Model(s) used: KOCWIN v2.01
Full reference and details of the used formulas can be found in:
1. Doucette, W.J. 2000. Soil and sediment sorption coefficients. In: Handbook of Property Estimation Methods, Environmental and Health Sciences. R.S. Boethling & D. Mackay (Eds.): Lewis Publishers (ISBN 1-56670-456-1).
2. US EPA. 2012. Estimation Programs Interface Suite™ for Microsoft® Windows, v 4.11. United States Environmental Protection Agency, Washington, DC, USA.
- Model description: see field 'Justification for non-standard information', 'Attached justification' and 'any other information on Material and methods'.
- Justification of QSAR prediction: see field 'Justification for type of information', 'Attached justification' and/or 'overall remarks'. - GLP compliance:
- no
- Type of method:
- other: calculation with QSAR
- Media:
- soil
- Details on test conditions:
- BASIS FOR CALCULATION OF Koc:
- Estimation software: EPI Suite™ v4.11 (June 2017), KOCWIN v2.01, Log Kow based method
- Result based on calculated log Kow of: see attached information. - Type:
- Koc
- Value:
- >= 4.7 - <= 3 272 L/kg
- Temp.:
- 25 °C
- Remarks on result:
- other: Based on log Kow
- Type:
- log Koc
- Value:
- >= 0.67 - <= 3.51 dimensionless
- Temp.:
- 25 °C
- Remarks on result:
- other: Based on log Kow
- Endpoint:
- adsorption / desorption, other
- Remarks:
- adsorption
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Remarks:
- Some of the constituents of the substance are not fully compliant with the applicability domain of the model. The maximum occurrence of aliphatic ether groups –C-O-C- in the training set of the model is equal to 2. Thus, constituents with an ethoxylation degree EO > 2 are outside the applicability domain of the model. However, this calculation is used in a weight of evidence approach, in accordance to the REACh Regulation (EC) No 1907/2006, Annex XI section 1.2. It is adequately documented and justified. For more details please refer to the model description and the complete prediction report in the section `Attached justification´.
- Justification for type of information:
- 1. SOFTWARE
EPI Suite v4.11 (June 2017) Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11 (June 2017). US EPA, United States Environmental Protection Agency, Washington, DC, USA.
2. MODEL (incl. version number)
KOCWIN v2.01, MCI based model.
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
See “Test material information”.
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
See attached information on the model provided by the developer. Further information on the OECD criteria as outlined by the applicant is provided below under "Any other information of materials and methods incl. tables".
5. APPLICABILITY DOMAIN
See attached information and information as provided in "Any other information on results incl. tables".
6. ADEQUACY OF THE RESULT
See assessment of adequacy as outlined in the "Overall remarks, attachments" section. - Qualifier:
- according to guideline
- Guideline:
- other: REACH Guidance on QSARs and grouping of chemicals (R.6)
- Principles of method if other than guideline:
- - Software tool(s) used including version: EPI Suite v4.11 (June 2017)
- Model(s) used: KOCWIN v2.01, MCI based method
Full reference and details of the used formulas can be found in:
Meylan, W., P.H. Howard and R.S. Boethling, "Molecular Topology/Fragment Contribution Method for Predicting Soil Sorption Coefficients", Environ. Sci. Technol. 26: 1560-7 (1992)
- Model description: see field 'Justification for non-standard information', 'Attached justification' and 'any other information on Material and methods'
- Justification of QSAR prediction: see field 'Justification for type of information', 'Attached justification' and/or 'overall remarks' - GLP compliance:
- no
- Type of method:
- other: calculation with QSAR
- Media:
- soil
- Details on test conditions:
- BASIS FOR CALCULATION OF Koc:
- Estimation software: EPI Suite™ v4.11 (June 2017), KOCWIN v2.01, MCI based method
- Type:
- Koc
- Value:
- >= 342.2 - <= 35 190 L/kg
- Temp.:
- 25 °C
- Remarks on result:
- other: Based on MCI
- Type:
- log Koc
- Value:
- >= 2.53 - <= 4.55 dimensionless
- Temp.:
- 25 °C
- Remarks on result:
- other: Based on MCI
Referenceopen allclose all
For detailed information on the results please refer to the attached report.
For detailed information on the results please refer to the attached report.
Description of key information
Alkyl ether sulfate constituents: log Koc = 2.53 - 4.55 (MCI method); log Koc = 0.67 - 3.51 (log Kow-based method) (QSAR, EPI Suite KOCWIN v2.01)
Key value for chemical safety assessment
Additional information
Information on the adsorption potential of Alcohols, C12-14, ethoxylated, sulfates, sodium salts was generated using two QSAR models (MCI and log Kow – regression based methods) implemented within the EPI Suite KOCWIN v2.01.
Since the substance is a salt of UVCB nature and QSAR models cannot predict salts and UVCBs, representative structures were selected for QSAR estimations, in order to include those expected to have the minimum and maximum log Koc. The SMILES notations encoding representative structures were neutralized and the inorganic counter-ion was removed.
Predicted log Koc values of the alkyl ether sulfate constituents range from 2.53 to 4.55 (MCI method) and from 0.67 to 3.51 (log Kow-based method). Alkyl ether sulfate constituents with ethoxylation degree higher than 2 are not compliant with the applicability domain of both models because the maximum occurrence of aliphatic ether groups in the training set of both models is equal to 2. However, the reliability of the predictions for the upper boundaries is supported by clear trends between the alkyl chain length and ethoxylation degree with predicted Koc values.
Overall, the results for all constituents can be considered as reliable and used in a weight of evidence approach and the log Koc of the substance Alcohols, C12-14, ethoxylated, sulfates, sodium salts can be estimated to range between 2.53 and 4.55 (MCI method) and between 0.67 and 3.51 (log Kow-based method).
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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