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EC number: 201-793-8 | CAS number: 88-04-0
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2002
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 002
- Report date:
- 2002
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- Deviations:
- no
- GLP compliance:
- yes
- Type of method:
- HPLC estimation method
- Media:
- other: methanol: water (75:25 v/v)
Test material
- Reference substance name:
- 4-chloro-3,5-xylenol
- EC Number:
- 201-793-8
- EC Name:
- 4-chloro-3,5-xylenol
- Cas Number:
- 88-04-0
- Molecular formula:
- C8H9ClO
- IUPAC Name:
- 4-chloro-3,5-dimethylphenol
- Test material form:
- solid: crystalline
- Details on test material:
- Sponsor's identification
Description
Batch number
Date received
Storage conditions
PCMX
cream coloured, crystalline solid
285/13847
27 September 2001
room temperature, in the dark
Constituent 1
- Specific details on test material used for the study:
- Sponsor's identification
Description
Batch number
Date received
Storage conditions
PCMX
cream coloured, crystalline solid
285/13847
27 September 2001
room temperature, in the dark
Sample solutions were prepared in stoppered glass flasks at a nominal concentration of
5.0 x 10·2 g/l in the three buffer solutions.
The solutions were shielded from light whilst maintained at the test temperature. - Radiolabelling:
- no
Study design
- Test temperature:
- 25C
HPLC method
- Details on study design: HPLC method:
- The sample, formamide and reference standard solutions were injected in duplicate using the
following HPLC parameters:
HPLC System
Column
Column temperature
Mobile phase
pH of mobile phase
Flow-rate
UV detector wavelength
Injection volume
Construction of calibration curve
Agilent Technologies 1100, incorporating
autosampler and workstation
Luna 5μ CN (250 x 4.6 mm id)
30°C
methanol: water (55:45 v/v)
6.2
1.0 ml/min
dead time and reference standards: 210 nm
sample: 221 nm
10 μl
Batch equilibrium or other method
- Details on sampling:
- .
Results and discussion
Adsorption coefficientopen allclose all
- Key result
- Sample No.:
- #1
- Type:
- log Koc
- Value:
- 2.08
- Temp.:
- 25 °C
- Key result
- Sample No.:
- #2
- Type:
- log Koc
- Value:
- 2.08
- Temp.:
- 25 °C
Results: HPLC method
- Details on results (HPLC method):
- Table 5.4
Injection
Retention Time Capacity Factor (k) (mins) log10 k log10 Koc
I 4.562 0.328 -0.485 2.08
2 4.561 0.327 -0.485 2.08
Mean log10 Koc: 2.08
Adsorption coefficient: 120
Any other information on results incl. tables
Table 5.4
Injection
Retention Time Capacity Factor (k) (mins) log10 k log10 Koc
I 4.562 0.328 -0.485 2.08
2 4.561 0.327 -0.485 2.08
Mean log10 Koc: 2.08
Adsorption coefficient: 120
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The adsorption coefficient (Koc) of the test material has been determined to be 120, log10 Koc 2.08.
- Executive summary:
The method guideline states that the measurement of adsorption coefficient should be carried out
on substances in their ionised and unionised forms. However, the dissociation constants of certain
functional groups found in the test material made it impossible to satisfy this criteria. Testing
would be required at pH 11 or above to obtain the hydroxyl group in an ionised form. The
dissociation constant of the hydroxyl group was estimated to be 9.8. As a consequence of this, the
functional group will always be present in its unionised form. Therefore, as pH 11 or above is
outside the environmental pH range for this test and also experimentally impractical, testing was
carried out at approximately neutral pH with the functional group unionised only.
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