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Diss Factsheets
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EC number: 275-073-7 | CAS number: 70969-70-9
- 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)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Guideline:
- other:
- Version / remarks:
- EPISUITE QSAR
- Principles of method if other than guideline:
- EPISUITE QSAR Calculated from Log Kow
- GLP compliance:
- no
- Type of method:
- other: QSAR estimate
- Radiolabelling:
- no
- Test temperature:
- not applicable
- Computational methods:
- Log Koc and Koc have been estimated by QSAR using KOCWIN 2.00 embedded in EPI Suite™ (2000) software, that was developed by the EPA's Office of Pollution Prevention Toxics and Syracuse Research Corporation (SRC)
- Type:
- Koc
- Value:
- 7 585 dimensionless
- Key result
- Type:
- log Koc
- Value:
- 3.88 dimensionless
- Validity criteria fulfilled:
- yes
- Conclusions:
- Log Koc (based on Molecular Connectivity Index (MCI)): 3.88
- Executive summary:
Based on the estimated log Koc value, it can be concluded that the substance has a high tendency for adsorption to soil.
The estimated log Koc value meets in an adequate way, the required information on adsorption/desorption for a chemical safety assessment under Regulation (EC) No. 1907/2006, Annex VIII, 9.3.1 (Adsorption/desorption). Given the higher accuracy of the MCI model (see 3.4 in QPRF and corresponding QMRF-document) the estimated Koc of 7585 (log Koc 3.88) is taken forward for hazard and risk assessment.
Reference
Description of key information
The test on adsorption/desorption cannot be performed due to low water solubility of test substance and subsequent analytical difficulties. As surrogate, a QSAR estimation was performed using KOCWIN 2.00 that estimated the Koc to be 7585 (log Koc 3.88).
Key value for chemical safety assessment
- Koc at 20 °C:
- 7 585
Additional information
The test item was found to be inherently biodegradable under the test conditions within 28 days (biodegradation of 59% achieved). However, the pass level for ready biodegradability, i.e. biodegradation of at least 60% of the ThOD in a 10-day window within the 28-day period of the test, was not reached. Hence, the substance is considered inherently biodegradable and bioelimination is expected. In addition, the substance is highly insoluble in water as shown in the test on water solubility (result <1 µg/L) but also in the acute algae study where a loading rate of 100 mg/l resulted in an analytical concentration below the limit of quantification (10 µg/l). Thus, conducting the study is technically not feasible and is waived in line with the criteria in Annex VIII, column 2 REACH.
As surrogate data, the Koc (and log Koc) were estimated by KOCWIN, version 2.00, a validated QSAR model developed by the US EPA's Office of Pollution Prevention Toxics and Syracuse Research Corporation (SRC).
The model uses two different algorithms. The first algorithm is based on the Molecular Connectivity Index (MCI), while the second one uses the log Kow value as the starting point (either calculated by KOWWIN or as manual input based on measured results).
Overall, the MCI methodology is somewhat more accurate than the Log Kow methodology, although both methods yield good results. If the training datasets are combined into one dataset of 516 compounds (69 having no corrections plus 447 with corrections), the MCI methodology has an r2, standard deviation and average deviation of 0.916, 0.330 and 0.263, respectively, versus 0.86, 0.429 and 0.321 for the Log Kow methodology. Consequently, the results delivered by the MCI method have been preferred. The MCI model delivered a result for Koc of 7585 (L/kg) and a log Koc of 3.88, respectively. In lack of experimental data, this value is used for risk assessment.
[LogKoc: 3.88]
[LogKoc: 3.88]
[LogKoc: 3.88]
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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