Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 219-370-1 | CAS number: 2425-77-6
- 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
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- June 14-22 2000
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well documented study performed according to OECD Guideline and GLP.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 000
- Report date:
- 2000
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 106 (Adsorption - Desorption Using a Batch Equilibrium Method)
- Deviations:
- no
- GLP compliance:
- yes
- Type of method:
- batch equilibrium method
- Media:
- soil
Test material
- Reference substance name:
- Isofol 18T
- IUPAC Name:
- Isofol 18T
- Details on test material:
- - Name of test material (as cited in study report): Isofol 18T
- Substance type: pure active substance
- Physical state: liquid
Constituent 1
- Radiolabelling:
- no
Study design
- Test temperature:
- 23 °C
Batch equilibrium or other method
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling interval: 16 h for adsorption, 16 hr for first wash, 40.5 h for second wash
- Sample storage before analysis: Not identified
- Details on matrix:
- COLLECTION AND STORAGE
- Geographic location: Richmond, British Columbia, Canada
PROPERTIES
Soil 1 - Very Strongly to Strongly Acid Sandy Soil
- Soil texture
- % sand: 89
- % silt: 8
- % clay: 3
- Horizon: Bmz
- Soil taxonomic classification: Orthic Humic Podzol
- Soil order: Podzolic
- pH: 5.1
- Organic carbon (%): 1.9
- CEC (meq/100 g): 12.2
- Carbonate as CaCO3: 1.89
Soil 2 - Moderately or Slightly Acid Loamy Soil
- Soil texture
- % sand: 19
- % silt: 56
- % clay: 25
- Horizon: Bnt
- Soil taxonomic classification: Orthic Humic Gleysol
- Soil series: Ladner
- Soil order: Gleysolic
- pH: 5.7
- Organic carbon (%): 0.4
- CEC (meq/100 g): 20.6
- Carbonate as CaCO3: 1.28
Soil 3 - Slightly Alkaline Loamy Soil
- Soil texture
- % sand: 1
- % silt: 69
- % clay: 30
- Horizon: C
- Soil taxonomic classification: Eluviated Eutric Brunisol
- Soil series: Wapta
- Soil order: Brunisolic
- pH: 9.0
- Organic carbon (%): 7.8
- CEC (meq/100 g): 9.7
- Carbonate as CaCO3: 21.84 - Details on test conditions:
- TEST SYSTEM
- Type, size and further details on reaction vessel: 15 ml polypropylene test tubes
- Amount of soil and water per treatment: 2 g of soil to 10 ml liquid
- Number of reaction vessels/concentration: 2 treatment tubes plus 1 blank per soil type
- Test performed in open system: Yes
- Method of preparation of test solution: 2ml of Alcohols, C16-20 Branched was stirred rapidly in a glass beaker with 200 ml of Ultrapure Water overnight at 23 degrees C to produce saturated solution. The aqueous phase was removed by siphoning with the first 20 ml discarded.
- Are the residues from the adsorption phase used for desorption: Yes
- Method of preparation of soil: Soil samples were pre-equilibrated by adding 2 g of soil and 5 ml of 0.01 M Calcium Chloride solution into 15 ml polypropylene test tubes and mixing for 23 hr.
- Adsorption Method: 5 ml of aqueous Alcohols, C16-20 Branched solution was added to appropriate tubes. The soil solutions were mixed for 16 hrs at 23 degrees C and then centrifuged (2000 rpm, 20 min). The volumes of soil and supernatants were recorded for only 1 tube per soil. The level of supernatants was marked with a felt pen on sides of tubes. The supernatants were decanted into clean 15 ml test tubes for analysis.
- Desorption Method: Calcium Chloride was added to marks on the test tubes containing the soil pellets. The pellets were resuspended and mixed for 16 hrs at 23 degrees C. The contents were centrifuged (2000 rpm, 20 min) and supernatants decanted for analysis (Wash 1). Process was repeated (Wash 2).
- Extraction Method: 2 ml of MTBE was added to test tubes containing decanted supernatant and rapidly mixed (rotomixer, end over end; 23 degrees C; 10 min). The MTBE layer was transferred to glass septum vials for GC-FID analysis.
Results and discussion
Adsorption coefficientopen allclose all
- Type:
- Koc
- Value:
- >= 214 - <= 4 170
- Type:
- log Koc
- Value:
- >= 2.33 - <= 3.62
Results: Batch equilibrium or other method
Mass balance (%) at end of adsorption phaseopen allclose all
- Sample no.:
- #1
- Duration:
- 16 h
- % Adsorption:
- > 88
- Sample no.:
- #2
- Duration:
- 16 h
- % Adsorption:
- > 88
- Sample no.:
- #3
- Duration:
- 16 h
- % Adsorption:
- > 88
Mass balance (%) at end of desorption phaseopen allclose all
- Sample no.:
- #1
- Duration:
- 16 h
- % Desorption:
- < 12
- Sample no.:
- #1
- Duration:
- 40.5 h
- % Desorption:
- < 12
- Sample no.:
- #2
- Duration:
- 16 h
- % Desorption:
- < 12
- Sample no.:
- #2
- Duration:
- 40.5 h
- % Desorption:
- < 12
- Sample no.:
- #3
- Duration:
- 16 h
- % Desorption:
- < 12
- Sample no.:
- #3
- Duration:
- 40.5 h
- % Desorption:
- < 12
- Details on results (Batch equilibrium method):
- See Below
Any other information on results incl. tables
Alcohols, C16-20 Branched was not detected by GC in supernatants from the adsorption or desorption phases of the study. Based on these results Alcohols, C16 -20 Branched was found to adsorb extensively (>88%) to the 3 tests soils. Desorption was considered to be <12%. A value for the Koc was not determined in the study. However, using the data from the study and equations from OECD 106 guidelines, values for Koc and log Koc can be determined. The calculated Koc values ranged from 214 to 4170, while the log Koc values ranged from 2.33 to 3.62.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Alcohols, C16-20 Branched adsorbs extensively (>88%) to soil.
- Executive summary:
This study determined the % adsorption and desorption of Alcohols, C16 -20 Branched to soil. Alcohols, C16 -20 Branched was mixed with three different soil types for 16 hrs. The samples were centrifiuged and the supernatant analyzed. Alcohols, C16 -20 Branched was determined to adsorb extensively (>88%) to soil. Calculated Koc values ranged from 214 to 4170, while the log Koc values ranged from 2.33 to 3.62.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.