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EC number: 247-156-8 | CAS number: 25640-78-2
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
Description of key information
BCF values for (1-methylethyl)-1,1'-biphenyl were determined in a pre-guideline study using a method similar to OECD TG 305 E. For the two concentrations applied very diverging factors were determined. BCF value of the supporting substance 4-ethylbiphenyl and values calculated for comparison with seven different methods were with one exception below 2000.
Key value for chemical safety assessment
- BCF (aquatic species):
- 2 896 dimensionless
Additional information
BCF values for (1-methylethyl)-1,1'-biphenyl were determined in a pre-guideline study similar to OECD TG 305 E based on uptake and depuration rate constants (Ozburn et al 1980). Documentation is limited. Individual fish concentration data for the different time points of the study are not reported as well as BCF values directly calculated from this data. BCF values were obtained employing the calculation program BIOFAC. It uses the fish concentration data of the uptake and the depuration phase to calculate respective rate constants. BCF is received as the ratio of uptake and depuration rate. BCF values calculated were
low concentration test group (3.5 µg/L) 2,896
high concentration test group (24.1 µg/L) 10,790
Both BCF values are remarkably different. The difference is much more pronounced than is normal for other substances similar to isopropylbiphenyl. In addition, compared to BCF of substances with similar molecular structure, the BCF of the high exposure group appears extremely high.
In order to assess the solidity of the measured BCF values, two approaches were taken.
For the supporting substance 4-ethylbiphenyl, a measured value is reported in the literature (Dimitrov, 2005). This value is quoted to be 667. 4-Ethylbiphenyl is used with this value in the training sets of several QSAR models for predicting BCF values. This value is considered as characterising the range of the isopropylbiphenyl BCF. Justification for use of 4-ethylbiphenyl as supporting substance is given in the Section to aquatic toxicity.
In a second step, BCF were estimated for (1-methylethyl)-1,1'-biphenyl using various calculation/QSAR methods. Methods/methodologies and results are displayed in the following table
|
US EPA EPI Suite |
US EPA T.E.S.T. |
|||||
Method |
regression based on log Kow |
Arnot-Gobas |
Hierarchical clustering |
Single model |
Group contribution |
FDA |
Nearest neighbour |
Predicted value |
1527 |
3471 |
1175 |
815 |
1290 |
1950 |
440 |
It is obvious, that none of the BCF estimates is close to the value of 10,790 obtained for the high exposure group of Ozburn. Except one value (3,471 - Arnot-Gobas), all other values fall in the range below 2000.
Compared to the BCF of 4-ethylbiphenyl as well as in comparison with the estimated BCF values of isopropylbiphenyl, the measured BCF of 2,896 for (1-methylethyl)-1,1'-biphenyl resulting from the low exposure group of Ozburn appears already high but is considered yet to be realistic. This value is taken as BCF of (1-methylethyl)-1,1'-biphenyl for further use in the chemical safety assessment.
The BCF value for the high exposure group of Ozburn is out of bounds by comparison to the data compiled to evaluate the BCF value of isopropylbiphenyl. It is considered as outlier and is disregarded.
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