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EC number: 906-151-7 | CAS number: -
- 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
Toxicity to terrestrial plants
Administrative data
Link to relevant study record(s)
Description of key information
m-cresol: EC50 (14 d) = 233 mg/kg d.w. standard soil on Lactuca sativa (OECD TG 208)
o-cresol: EC50 (14 d) > 242 mg/kg d.w. standard soil on Lactica sativa (OECD TG 208)
Key value for chemical safety assessment
Additional information
o-cresol and m-cresol
The toxicity of o-cresol and m-cresol to lettuce (Lactuca sativa) was examined by Hulzebos (1993) according to OECD guideline 208. The organic matter of the two soil types used in the experiment was given to range between 1.4% and 1.8%. The weight of the above-ground biomass was measured after 7 and 14 days. After an exposure period of 14 days an EC50 of >100 mg/kg dw soil was obtained for o-cresol and an EC50 of 96 mg/kg dw soil was obtained for m-cresol. According to TGD (EU 2003) these values were normalised to a standard soil containing 3.4% of organic matter, resulting in a corrected EC50 of >242 mg/kg for o-cresol and a corrected EC50 of 233 mg/kg for m-cresol. The authors state that during the test period, the concentrations of most phenols in soil dropped to less than 20% of the initial concentrations.
p-cresol
The effect of p-cresol on the germination of lettuce fruit (Lactuca sativa) was tested under laboratory conditions (Reynolds, 1978). After an exposure period of 72 h an EC50 of 122 mg/L was determined.
The scope of the terrestrial effects assessment under the adopted REACH regulation is restricted to soil organisms in a narrow sense and does not actually include adverse effects on soil functions that are only indirectly linked to the biota in soils. This test was designed assessing the influence of p-cresol on germination and growth on moist filter paper or agar treated with the substance. As no soil was used standardisation of soil effect data to given soil parameters is not possible. Further, converting the results to an appropriate dimension is not applicable. Therefore the result should not be used for the hazard assessment. Nevertheless, the obtained effect values indicate that p-cresol is of low toxicity to terrestrial plants.
long-term toxicity to terrestrial plants
Long-term toxicity tests on plants are not available. Based on the exposure assessment there is no unacceptable risk of cresols to the soil ((PEC/PNEC < 1) and thus, long-term studies on terrestrial plants do not need to be conducted.
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