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EC number: 203-583-1 | CAS number: 108-44-1
- 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
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study meets generally accepted scientific principles.
- 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 +/- 2 °C
- Analytical monitoring:
- yes
- Details on matrix:
- - 4 different soils were used having an organic matter between 1.09 and 4.25 % and pH values ranging between 7.5 and 6.1
- air-dried and sieved (2 mm) - Details on test conditions:
- - one gram of soil was shaken for 2 h with 10 mL chemical solution in 0.01 M CaCl2
- centrifugation for 10 min
- 5 ppm, 10 ppm, 15 ppm and 20 ppm of test substance served as initial concentrations - Type:
- Koc
- Value:
- 44.31
- Temp.:
- 20 °C
- Type:
- log Koc
- Value:
- 1.65
- Temp.:
- 20 °C
- Details on results (Batch equilibrium method):
- In the reference, only the logKom value accounting for 1.41 is reported., which easily can be transfered to the resepective logKoc value by the following equation (according to Hong et al., 1996):
Koc= Kom*1.724 - Validity criteria fulfilled:
- not specified
- Remarks:
- Since the test is poorly reported the validity criteria cannot be assessed sufficiently. Nevertheless the test is considered as valid based on the data given.
- Conclusions:
- The experimentally determined logKoc of the substance is 1.65 at 20°C.
- Executive summary:
- The distribution of m-toluidine onto four different soils was investigated following a method similar to the OECD 106 (Briggs, 1981). Adsorption was measured in soils at four initial concentrations and the adsorption isotherms for the substance were linear. When Kd was converted to Kom the value on each of the four soils was within 20% of the mean value. The adsorption/desorption behaviour of m-toluidine is characterized by a logKoc of 1.65 at 20°C. In the reference, only the logKom value accounting for 1.41 is reported, which easily can be transfered to the resepective logKoc value by the following equation: Koc= Kom*1.724.
Reference
The adsorption isotherms for the substance was linear. When Kd was converted to Kom the value on each of the four soils was within 20% of the mean value of 1.41 (log Kom).
Description of key information
The experimentally determined logKoc of the substance is 1.65 at 20°C.
Key value for chemical safety assessment
- Koc at 20 °C:
- 44.31
Additional information
The distribution of m-toluidine onto four different soils was investigated following a method similar to the OECD 106. Adsorption was measured in soils at four initial concentrations and the adsorption isotherms for the substance were linear. When Kd was converted to Kom the value on each of the four soils was within 20% of the mean value. The adsorption/desorption behaviour of m-toluidine is characterized by a logKoc of 1.65 at 20°C. In the reference, only the logKom value accounting for 1.41 is reported, which easily can be transfered to the resepective logKoc value by the following equation: Koc= Kom*1.724.
[LogKoc: 1.65]
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