Registration Dossier
Registration Dossier
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

Endpoint summary
Administrative data
Description of key information
Additional information
From the available information it was clear that hydrolysis and direct phototransformation in air and/or water will not contribute much to the degradation of biphenyl in the environment. The only relevant abiotic process is indirect phototransformation in air through reaction with photochemically-generated hydroxyl radicals, which is estimated to occur at a half-life of 16 h at hydroxyl radical concentration of 1.5 million OH molecules/cm3. Overall, biodegradation is the most important degradation process affecting fate and lifetime in aquatic and terrestrial compartments. Biphenyl has been demonstrated to be readily biodegradable. Additionally, simulation studies in water and water/sediment systems yielded half-lives of 2-3 days in water and 2-10 days in water/sediment (at 20 and 22°C, respectively).
Relevant processes which influence the distribution of biphenyl in the environment are volatilization, advection, adsorption, and bioaccumulation. No experimental data have been identified on the partitioning between air and water. EUSES calculates a Henry's Law constant for biphenyl of 25 Pa/m3/mol (at 25°C), indicating that the molecule may undergo volatilization from aqueous solutions. A major process determining the distribution of biphenyl in the environment is adsorption. Based on measured adsorption of the subsance in several different soils, an average log Koc of the substance was determined to be 3.19, whereas strong binding to soil is generally indicated by log Koc > 4. It is noteworthy that biodegradation studies in sewage sludge and natural soils indicate that biphenyl remains available for microorganisms and can still be degraded in the partly adsorbed form. Finally biphenyl is easily taken up by organisms but does not tend to be highly bioaccumulative. Studies investigating both total bioaccumulation (total 14C-based) as well as the distribution of accumulated 14C-activity between parent and metabolites indicated that when based on concentrations of parent biphenyl the BCF factors are much lower. A conservative BCF value of 1900 L/kg (wet weight, based on total accumulated biphenyl and metabolites) in fish will be used in the chemical safety and PBT assessments.
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