Registration Dossier
Registration Dossier
Diss Factsheets
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EC number: 202-423-8 | CAS number: 95-48-7
- 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: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 106 (Adsorption - Desorption Using a Batch Equilibrium Method)
- GLP compliance:
- no
- Type of method:
- batch equilibrium method
- Media:
- soil
- Radiolabelling:
- no
- Test temperature:
- 20 +/-1 °C
- Analytical monitoring:
- yes
- Details on test conditions:
- Soil: Brookston clay loam soil (type Argiaquoll, fine, loamy, mixed, mesic), collected from top 15 cm air-dried, 5.10% organic matter, pH 5.7 soil/solution ratio 1:10 TS concentrations 5, 10, 20, 30, 50 mg/l, deoxygenated by purging with N2 and H2 (9:1 v/v)
- Type:
- Koc
- Value:
- 22
- Transformation products:
- not measured
- Details on results (Batch equilibrium method):
- predicted Koc = 18
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The Koc of o-cresol was determined with batch equilibrium methods. In the experiment, similar to OECD Guideline 106 a Koc of 22 was obtained for clay.
- Executive summary:
The distribution between the organic phase of soil solids and water was determined in batch equilibrium experiments similar to the OECD guideline 106. For a clay loam soil determined a Koc value of 22.
- Endpoint:
- adsorption / desorption: screening
- 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
- Principles of method if other than guideline:
- Investigations on sorption properties of brown coal sediments originating from a pond near Leipzig (Germany)
- GLP compliance:
- not specified
- Type of method:
- batch equilibrium method
- Media:
- sediment
- Radiolabelling:
- yes
- Test temperature:
- room temperature
- Analytical monitoring:
- yes
- Details on sampling:
- GC/MS analysis
- Details on matrix:
- properties of coal sediment: 6.5 - 16.9 wt% organic matter and 52 wt% organic carbon
- Type:
- log Koc
- Value:
- 1.75
- Temp.:
- 25 °C
- % Org. carbon:
- 52
- Remarks on result:
- other: coal sediment
- Type:
- log Koc
- Value:
- 1.7
- Temp.:
- 25 °C
- % Org. carbon:
- 52
- Remarks on result:
- other: river sediment
- Transformation products:
- not measured
- Conclusions:
- In experiments using sediments Koc values of 50 and 56 for o-cresol were determined. The values suggest a low potential for adsorption in soil and sediment.
- Executive summary:
Kopinke (1995) studied the sorption properties of sediments using the batch equilibrium method. A Koc of 50 and 56 was found for coal and river sediment, respectively. The values suggest a low potential for adsorption in soil and sediment.
Referenceopen allclose all
Reported value of 1.75 referes to coal sediment. A log Koc of 1.7 was determined for river sediment.
Description of key information
The experimentally determined Koc values for o-cresol are: 22 for a clay loam, 50 for coal and 56 for river sediment.
As a worst-case assumption, the lowest experimentally determined Koc value of 22 is taken into account for further assessment.
Key value for chemical safety assessment
- Koc at 20 °C:
- 22
Additional information
The distribution between the organic phase of soil solids and water was determined in batch equilibrium experiments similar to the OECD guideline 106. For a clay loam soil a Koc of 22 was determined.
In an experiment the sorption properties of o-cresol in sediments using the batch equilibrium method was determined. A Koc of 50 and 56 was found for coal and river sediment, respectively.
The Koc values suggest a low potential for adsorption for o-cresol in soil and sediment.
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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.

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