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Diss Factsheets
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EC number: 202-163-5 | CAS number: 92-52-4
- 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 Key Studies of Kishi et al. (1990) and Southworth and Keller (1986) report measured Koc values in widely varied soils, which range from 876 - 3,300 (log Koc 2.94 - 3.52). Other supporting studies of Saeger et al. indicate log Koc values ranging from 2.16 - 2.38 in various aquatic sediment samples. A QSAR prediction of log Koc = 3.15, using a recently developed QSAR for neutral organics, is also reported by Schüürmann et al. (2006). The average value of eight well-documented log Koc values reported in the Key Studies (ave. log Koc = 3.19) will be used as basis for the Chemical Safety Assessment.
Key value for chemical safety assessment
- Koc at 20 °C:
- 1 546
Additional information
The Key Studies provide the best available and relevant measured values of log Koc for this substances. Several databases and studies refer to an experimentally determined log Koc value of 3.27 for biphenyl, which turns out to be an average of estimated log Koc values determined for various samples of colloidal organic matter. This 1984 study by Landrum et al. (Environmental Science and Technology 18:187 -192) has no similarity to current standardized test guidelines. The experimental database of U.S. EPA KocWIN refers to Schüürmann et al. (2006), Schüürmann et al. refer to a publication of Sabljic et al. (1995), which cites the average log Koc value of Landrum et al. (1984).
Further, several reliable QSAR estimates are available. Using KocWIN v2.00, which is an approved tool for estimating adsorption coefficients for organic substances, the log Koc was predicted to be 3.71 based on first order molecular connectivity index, and 3.47 based on log Kow. A newly developed QSAR for neutral organics however yields a most likely more reliable value of 3.15 (Schüürmann et al., 2006).
Three other sources yielded relevant, but non-reliable information. The environmental fate studies of Saeger et al. (1988a,b,c) – described under the endpoints on biodegradation – yielded log Koc values of 2.25, 2.16 and 2.27-2.38, respectively. These values could not be considered reliable because of the interference of other loss processes (e.g., volatilization, degradation, adsorption to testing equipment, etc.). However, the fact that they are lower than the experimentally determined value as well as the available estimates is completely in line with the expectations based on the rationale for these studies and therefore these values can be used in support of the other available information.
[LogKoc: 3.19]
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