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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 947-752-4 | CAS number: -
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Justification for type of information:
- JUSTIFICATION FOR DATA WAIVING
According to REACH Annex VII column 2, 9.1.2. Growth inhibition study aquatic plants (algae preferred), the study does not need to be conducted if there are mitigating factors indicating that aquatic toxicity is unlikely to occur for instance if the substance is highly insoluble in water or the substance is unlikely to cross biological membranes.
In general, there is no legal limit value available defining a substance as poorly water soluble or insoluble under REACH. However, in ECHA’s Guidance document Chapter R.7b: Endpoint specific guidance Version 3.0 – February 2016, it is stated: „poorly water soluble substances (e.g. water solubility below 1 mg/L or below the detection limit of the analytical method of the test substance)“. Further, poorly soluble substances are defined by OECD (2000 OECD SERIES ON TESTING AND ASSESSMENT, Number 23, GUIDANCE DOCUMENT ON AQUATIC TOXICITY TESTING OF DIFFICULT SUBSTANCES AND MIXTURES, ENV/JM/MONO(2000)6) as substances with a limit of solubility <100 mg/l although technical problems are more likely to occur at <1mg/l as defined in TGD (1996). Very low water solubility (i.e. in the low μg/l range) could be used as a reason to significantly modify a standard test or to test non-pelagic organisms preferentially.
ECHA’s Guidance document Chapter R.7c: Endpoint specific guidance Version 3.0 – June 2017 further says: „As indicated in the OECD TG 305, for strongly hydrophobic substances (log Kow > 5 and a water solubility below ~ 0.01-0.1 mg/L), testing via aqueous exposure may become increasingly difficult. However, an aqueous exposure test is preferred for substances that have a high log Kow but still appreciable water solubility with respect to the sensitivity of available analytical techniques, and for which the maintenance of the aqueous concentration as well as the analysis of these concentrations do not pose any constraints.
The water solubility is < 11.2 µg/L for the test item resp. < 1 mg/l for the analyte, i.e. iron, so the criteria mentioned above are met. Further, the criterion for “below the detection limit of the analytical method of the test substance” is also met. The establishment and validation of the analytical method was properly performed.
The detection limit of the analytical method is (ICP-OES) is 0.001 mg/l Fe, working range of the ICP-OES is actually 0.005 – 1 mg/l.
Ecotoxicity tests are performed in media containing various supplements and biological material, which is expected to lower the sensitivity of the analytical method. Hence, quantification of the test item up to its water solubility in ecotoxicity test media could like not be performed at all. So, the required analytics for ecotoxicity testing, both short and long-term, are technically not feasible, and testing does not need to be conducted.
Summarizing, a study of the acute toxicity of the registered substance to algae does not need to be conducted, as it is considered both not technically feasible and no additional information on classification and labelling could be retrieved, and the study can be omitted.
Cross-reference
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2018-01-15 - 2018-01-19
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- no
- GLP compliance:
- yes
- Type of method:
- column elution method
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: sponsor
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Refrigerated (5 ± 3°C) - Key result
- Water solubility:
- <= 11.2 µg/L
- Conc. based on:
- test mat.
- Temp.:
- 20 °C
- Remarks on result:
- other: pH value not available
- Water solubility:
- <= 1 µg/L
- Conc. based on:
- element
- Remarks:
- Fe
- Temp.:
- 20 °C
- Remarks on result:
- other: Analytical method was established with Fe as analyte
- Conclusions:
- Water solubility of the test item was performed according to OECD 105 under GLP using the column elution method, which was chosen as the substance was considered to have a water solubility below 10E-2 g/L. Quantification of the solved material was performed using ICP-OES by determination of the iron contained in the test item. An iron concentration of 1 μg/L corresponds to about 11.2 μg/L for the idealized structure of the test item. So, the method is considered suitable and the results are considered sufficiently reliable. The water solubility of the test item is below or equal to the detection limit of the analytical method (1 μg/L Fe) and hence appears insoluble in water. With reference to column 2 of Annex VII to REACH “If the substance appears ‘insoluble’ in water, a limit test up to the detection limit of the analytical method shall be performed”, the water solubility of the test item is reported as ≤11.2 μg/L. So the substance must be considered insoluble in water.
- Executive summary:
The test item was analysed for water solubility according to OECD Guideline 105 under GLP, using the column elution method.
The concentration of the test item in the collected fractions was calculated from the iron content determined by ICP-OES.
The water solubility of the test item is below or equal to the detection limit of the analytical method (1 μg/L Fe) and hence appears insoluble in water.
An iron concentration of 1 μg/L corresponds to about 11.2 μg/L for the idealized structure of the test item.
With reference to column 2 of Annex VII to REACH “If the substance appears ‘insoluble’ in water, a limit test up to the detection limit of the analytical method shall be performed”, the water solubility of the test item is reported as ≤11.2 μg/L.
(See also “Guidance on Information Requirements and Chemical Safety Assessment Chapter R.7a: Endpoint specific guidance”, Version 6.0, July 2017, page 66ff).
The water solubility of the test item was determined to ≤11.2 μg/L.
The water solubility was determined at 20 °C. The pH value of the collected aqueous fractions could not be determined since HNO3 was immediately added for stabilization.
Data source
Materials and methods
Results and discussion
Applicant's summary and conclusion
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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