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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: 500-107-7 | CAS number: 40039-93-8
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Study period:
- Jan 2013
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Calculated BCF using the BCF base-line model v.02.05.
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Calculated BCF using the BCF base-line model v.02.05 (attached as appendix I) and CATALOGIC model for metabolism simulation (attached as appendix II).
- GLP compliance:
- no
- Radiolabelling:
- no
- Type:
- BCF
- Value:
- 1.51 dimensionless
- Basis:
- other: QSAR estimation
- Remarks on result:
- other: Component A
- Type:
- BCF
- Value:
- 0.87 dimensionless
- Basis:
- other: QSAR estimation
- Remarks on result:
- other: Component B
- Type:
- BCF
- Value:
- 0.72 dimensionless
- Basis:
- other: QSAR estimation
- Remarks on result:
- other: Component C
- Validity criteria fulfilled:
- yes
- Remarks:
- Components A, B, C are in the structural and mechanistic domain of the model and estimations of log BCF are considered reliable.
- Conclusions:
- Component A - is characterized by high lipophilicity. Although its log Kow value (log Kow=5.74) would classify it as bioaccumulative, mitigating factors are taken into consideration which reduced its maximum bioaccumulation potential. The BCF base-line model estimates that size and metabolism as most significant mitigating factors reducing its bioaccumulation down to log BCF = 1.51 leading to ultimate classification as Not bioaccumulative.
Component B - the results are confirmed by observed data for structural analogues identified in the Toolbox (also in training set of the BCF base-line model).
Component B is characterized by extreme lipophilicity (calculated log Kow=14.3). Following the conceptual non-linearity of the BCF base-line model, a low bioaccumulation potential is estimated for component B due to its passive diffusion. As a result its log BCFmax is 0.97. Given the extremely low value of log BCFmax (0.97) the contribution of the significant mitigating factors - size and metabolism is formally very small (the ultimate log BCF is 0.87).
The Guidance on information requirements and chemical safety assessment - PBT assessment of ECHA recommends that a chemical may be considered as not bioaccumulative if: DiamMax average > 1.7 nm, molecular weight > 1100 g/mol, log Kow > 10. Component B meets the listed indicators. It has DiamMax in the range 19.0÷32.9 Å (1.9÷3.3 nm), MW=1256 and log Kow =14.3. Hence, based on direct analysis if its volumetric parameters, one could conclude that it is unlikely Component B to have BCF > 2000 (log BCF = 3.3).
Hence, component B should be classification definitely as Not bioaccumulative.
Component C - the estimated log BCFmax = 4.05 for component C is based on its high lipophilicity (calculated log Kow=5.5). The BCF base-line model estimates metabolism to be the most significant mitigating factor for component C. The significant contribution of metabolism in reducing the log BCFmax value for component C is due to the presence of hydroxyl groups in its structure. The presence of hydroxyl groups allows the direct application of high probability Phase II transformations (O-glucuronidation), skipping hydroxylating phase I reactions. It is estimated that metabolism reduces the bioaccumulation of component C down to log BCF = 0.72 leading to ultimate classification Not bioaccumulative.
Reference
Description of key information
Component A is the smallest component and has low but measurable water solubility value of 33.4ug/l thus, it is been considered as the worst case scenario.
Key value for chemical safety assessment
- BCF (aquatic species):
- 1.51 dimensionless
Additional information
Component A - is characterized by high lipophilicity. Although its log Kow value (log Kow=5.74) would classify it as bioaccumulative, mitigating factors are taken into consideration which reduced its maximum bioaccumulation potential. The BCF base-line model estimates that size and metabolism as most significant mitigating factors reducing its bioaccumulation down to log BCF = 1.51 leading to ultimate classification as Not bioaccumulative.
Component B - the results are confirmed by observed data for structural analogues identified in the Toolbox (also in training set of the BCF base-line model). Component B is characterized by extreme lipophilicity (calculated log Kow=14.3). Following the conceptual non-linearity of the BCF base-line model, a low bioaccumulation potential is estimated for component B due to its passive diffusion. As a result its log BCFmax is 0.97. Given the extremely low value of log BCFmax (0.97) the contribution of the significant mitigating factors - size and metabolism is formally very small (the ultimate log BCF is 0.87). The Guidance on information requirements and chemical safety assessment - PBT assessment of ECHA recommends that a chemical may be considered as not bioaccumulative if: DiamMax average > 1.7 nm, molecular weight > 1100 g/mol, log Kow > 10. Component B meets the listed indicators. It has DiamMax in the range 19.0÷32.9 Å (1.9÷3.3 nm), MW=1256 and log Kow =14.3. Hence, based on direct analysis if its volumetric parameters, one could conclude that it is unlikely Component B to have BCF > 2000 (log BCF = 3.3). Hence, component B should be classification definitely as Not bioaccumulative.
Component C - the estimated log BCFmax = 4.05 for component C is based on its high lipophilicity (calculated log Kow=5.5). The BCF base-line model estimates metabolism to be the most significant mitigating factor for component C. The significant contribution of metabolism in reducing the log BCFmax value for component C is due to the presence of hydroxyl groups in its structure. The presence of hydroxyl groups allows the direct application of high probability Phase II transformations (O-glucuronidation), skipping hydroxylating phase I reactions. It is estimated that metabolism reduces the bioaccumulation of component C down to log BCF = 0.72 leading to ultimate classification Not bioaccumulative.
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