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EC number: 201-964-7 | CAS number: 90-05-1
- 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, other
- Remarks:
- adsorption
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Adsorption of substituted phenols by soil
- Author:
- Boyd S.A
- Year:
- 1 982
- Bibliographic source:
- Soil Science, 134 : 337-343
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Soil adsorption isotherm
- GLP compliance:
- not specified
- Type of method:
- batch equilibrium method
- Media:
- soil
Test material
- Reference substance name:
- Guaiacol
- EC Number:
- 201-964-7
- EC Name:
- Guaiacol
- Cas Number:
- 90-05-1
- Molecular formula:
- C7H8O2
- IUPAC Name:
- Phenol
- Details on test material:
- Phenols used in this study were obtained from Aldrich Chemical Co., Eastman Kodak Co., and Mallinckrodt and used without further purification
Constituent 1
- Radiolabelling:
- no
Study design
Batch equilibrium or other method
- Analytical monitoring:
- yes
- Details on matrix:
- A Brookston clay loam soil obtained from the Michigan State University Soils Research Farm, Eas Lansing, Michigan, was used in this study. Samples were collected from the top 15 cm of the soil profile, air-dried, and ground to pass through an 18-mesh (1-mm) screen.
- Details on test conditions:
- Batch equilibrations were set up inside an anaerobic glovebox using a 1:10 soil:solution ratio and 5 initial concentrations of Guaiacol : 5, 10, 20, 30 and 50 ppm.
Triplicate samples were measured for each initial concentration.
Aqueous solutions (100 mL) of Guaiacol were prepared in 0.0025 M CaCl2 that had been deoxygenated by purging for 10 min. with purified N2. For isotherm of Guaiacol, 152.5 g of soil samples were weighed into 50-mL Oak Ridge-type polypropylene centrifuge tubes and transferred into an anaerobic glove box. 25-mL aliquots of Guaiacol solution were added to triplicate soil samples, and remaining 25 mL aliquot was saved for use as an analytical standard. The centrifuge tubes were subsequently capped, removed from the glove box, and shaken for 24 h at 20+/-1°C. At the end of the 24 h equilibration period, the samples were centrifuged at 20 000 g for 20 min. in a refrigerated centrifuge set at 20°C.
Portion of the aqueous phase was then filtered through small glass wool plugs held in 9-in. Pasteur pipets. Samples were collected in glass vials, capped, and analysed immediately, using HPLC.
Duration of adsorption equilibration
- Duration:
- 24 h
- Temp.:
- 20 °C
Results and discussion
Adsorption coefficient
- Type:
- Koc
- Value:
- 40.01
Applicant's summary and conclusion
- Executive summary:
Adsorption isotherms of guaiacol have been determined using a Brookston clay loam soil, a soil:solution ratio of 1:10 and 5 initial concentrations (5, 10, 20, 30 and 50 ppm).
The measured soil organic carbon partition coefficient Koc was 40.01.
Based on this result, guaiacol is not considered to be a highly adsorptive substance.
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