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EC number: 219-371-7 | CAS number: 2425-79-8
- 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)
Description of key information
The adsorption coefficient for both soil and sewage sludge was determined based on the retention times of the active ingredient (ca. 2.03 minutes), the lower limit of the peak (ca. 1.91 minutes), and the upper limit of the peak (ca. 2.64 minutes) using OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC).
The adsorption coefficient of the test substance on soil is estimated as log Koc of 1.1 ±0.7 (pH = 6.7, 25 °C) with a lower limit of 0.6 ±0.8 and an upper limit of 3.0 ±0.5 (pH 6.7, 25 °C).
The adsorption coefficient of the test substance on sewage sludge is estimated as log Koc of 1.3 ±0.9 (pH = 6.7, 25 °C) with a lower limit of 0.8 ±1.0 and an upper limit of 3.3 ±0.7. In general substances with a Koc <500 – 1000 L/kg are not likely sorbed to sediment (SETAC 1993). According to this, a log Koc or log Kow of ≥3 is used as a trigger value for sediment effects assessment. On this basis, the substance is expected to demonstrate high mobility in soil and medium to high mobility in sewage sludge. SETAC. 1993. Guidance Document on Sediment Toxicity Tests and Bioassays for Freshwater and Marine Environments. From the Workshop on Sediment Toxicity Assessment at Renesse, Netherlands on 8-10 November 1993. Hill I, Mathiessen P, Heimbach F (eds). Society of Environmental Toxicology and Chemistry – Europe, Brussels.
Key value for chemical safety assessment
- Koc at 20 °C:
- 20
Additional information
The key study is a Klimisch-1, GLP-compliant study, sponsored by the Epoxy Resin Consortium and carried out in 2010 by the Výzkumný ústav organických syntéz a.s. (Čížek K) according to OECD 121 and EU Method C.19 (HPLC estimation method). The adsorption coefficient of the substance in soil and in sewage sludge was estimated by comparison of the substance’s retention time compared to the retention times of six reference compounds (acetanilide (CAS 103-84-4), benzamide (CAS 55-21-0), 2,5-dichloroaniline (CAS 95-82-9), phenyl benzoate (CAS 93-99-2), phenanthrene (CAS 85-01-8), and fenthion (CAS 55-38-9)).
As the test substance produced a wide uneven peak, the adsorption coefficient for both soil and sewage sludge was determined based on the retention times of the active ingredient (ca. 2.03 minutes), the lower limit of the peak (ca. 1.91 minutes), and the upper limit of the peak (ca. 2.64 minutes). The adsorption coefficient of the test substance on soil is estimated as log Koc of 1.1 ±0.7 (pH = 6.7, 25 °C) with a lower limit of 0.6 ±0.8 and an upper limit of 3.0 ±0.5. The adsorption coefficient of the test substance on sewage sludge is estimated as log Koc of 1.3 ±0.9 (pH = 6.7, 25 °C) with a lower limit of 0.8 ±1.0 and an upper limit of 3.3 ±0.7.
Since both log Koc (soil) and log Koc (sludge) are below the lower limit of the method (lower limit = 1.5 log units), the results are considered less reliable.
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