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EC number: 204-589-7 | CAS number: 122-99-6
- 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
The NOEC based on emergence rate, dry weight, fresh weight and shoot height was 250, 63, <63 and <63 mg/kg soil DM, respectively. - The percentage of organic carbon in the natural soil has not been corrected for. As the percent organic carbon was 0.88% and the agreed standard organic matter percent for tests is 3.4% a correction factor of 3.86 should be multiplied by all endpoints. The resulting lowest EC50 (standard) was 131 mg a.s./kg dry mass soil; fresh weight for Brassica napus. for Avena sativa, 250, <63, <63 and <63 mg/kg soil DM, respectively, for Brassica napus, and 63, <63, <63 and <63 mg/kg soil DM, respectively, for Vicia sativa (most sensitive species). The EC50 based on emergence rate, dry weight, fresh weight and shoot height was 466, 235, 166 and 203 mg/kg soil DM, respectively, for Avena sativa, 361, 37, 34 and 40 mg/kg soil DM, respectively, for Brassica napus (most sensitive species), and 64, 107, 83 and >251 mg/kg soil DM, respectively, for Vicia sativa.
Key value for chemical safety assessment
- Short-term EC50 or LC50 for terrestrial plants:
- 131 mg/kg soil dw
Additional information
In the key study, the effects of 2-phenoxyethanol on Brassica napus, Avena sativa and Vicia sativa were investigated according to OECD 208 under GLP (BASF SE, 2008). Soil samples were exposed to phenoxyethanol (purity 99.9%) at nominal concentrations of 0, 62.5, 125, 250, 500 and 1000 mg/kg DM. Five days after exposure, the seeds were sowed and the emerging seedlings were recorded as well as 14 days after emergence of all seedlings, the dry weight, fresh weight and shoot length were determined. The NOEC based on emergence rate, dry weight, fresh weight and shoot height was 250, 63, <63 and <63 mg/kg soil DM, respectively, for Avena sativa, 250, <63, <63 and <63 mg/kg soil DM, respectively, for Brassica napus, and 63, <63, <63 and <63 mg/kg soil DM, respectively, for Vicia sativa (most sensitive species). The EC50 based on emergence rate, dry weight, fresh weight and shoot height was 466, 235, 166 and 203 mg/kg soil DM, respectively, for Avena sativa, 361, 37, 34 and 40 mg/kg soil DM, respectively, for Brassica napus (most sensitive species), and 64, 107, 83 and >251 mg/kg soil DM, respectively, for Vicia sativa. In a supporting study, the inhibiting effect of 2-phenoxyethanol on seedling emergence and growth was investigated for three terrestrial plants according to OECD Guideline 208 (Sasol Germany GmbH, 1994). Seeds were planted in concentrations of 0, 1, 10 and 100 mg/kg soil dw test substance (purity 85.7%, contaminated with phenoxydiethanol). The NOEC was based on seedling emergence while the EC50 value was based on growth inhibition. For Brassica alba, a NOEC(17d) of 100 mg/kg soil dw and an EC50(17d) of 40 mg/kg soil dw were found. For Lepidum sativum, a NOEC(17d) of >100 mg/kg soil dw and an EC50(17d) of 38 mg/kg soil dw were found, and for Triticum aestivum, a NOEC(17d) of >100 mg/kg soil dw and an EC50(17d) of 73 mg/kg soil dw were determined.
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