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EC number: 248-420-5 | CAS number: 27344-06-5
- 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
No bioaccumulation is expected
Key value for chemical safety assessment
- BCF (aquatic species):
- 0.5 dimensionless
Additional information
According to the REACH Regulation, Annex IX, Column 2, the substance does not need to be tested due to the low potential for bioaccumulation (log Kow < 3) and a low potential to cross biological membranes (high molecular weight, high polarity); furthermore direct and indirect exposure of the aquatic compartment is unsuitable.
Four bioaccumulation studies are available on the analogous substance of the category of Stilbene Fluorescent Whitening Agents, OB 3b-A, demonstrating no bioaccumulation in fish. Bluegills (Lepomis machrochirus) was exposed to the test item in dynamic flowthrough tankwater systems, in order to determine at what degree this product accumulate in portions of the fish, which may be consumed by humans. The concentration tested was 0.1 mg/l, the exposure period was 35 days and the elimination phase was 7 days. During the tests, fish and water were periodically sampled and analysed. A further accumulation study using 14C-labeled substance was performed at concentrations of 0.01 and 0.001 mg/l; exposure phase was of 30 days, while elimination phase of 14 days. Only sporadic trace concentrations (less than 0.05 mg/kg) of the test item were present in the fish at exposure levels of 1 mg/l. In most instances, no detectable substance was found.
The data indicates that there is no tendency for the substance to be taken up and stored in the fish. In the case of the 14C-substance, at both the concentrations tested, the levels of radioactivity found in the fish were approximately equal to those found in the tankwater throughout study. Furthermore the absence of accumulated radioactivity demonstrated that neither parent compound, nor possible metabolites of the substance are accumulated in fish (Ganz, 1975).
The test substance was also tested to determine its potential for significant accumulation in the flesh of the Bluegill (Lepomis macrochirus) and channel catfish (Ictalurus punctatus). The test was conducted at the following concentrations: 50 µg/l, 5 µg/l, and 0.5 µg/l total test substances (the study was conducted with five agents administrated in the same solutions). The results of the bluegill analysesexposedto a nominal concentration of 50 µg/l total agents (12.5 µg/l of each one) indicate that no accumulation of the substance of the interest was observed at measurable levels (i.e., greater than 10 µg/kg). At the concentration of 5 and 0.5 µg/l(1.25 and 0.125 µg/l, respectively) no measurable accumulation was detected (Sturm, 1974).
In the Bionomics Inc. and Ciba Geigy Ltd. (1972-1973) study sixty Bluegill were continuously exposed to the chemical in water for a period of at least 28 days. After this period, the fish will be transferred for a period of 7 to uncontaminated water and after this period they were sampled. Generally the test item concentration were not determinable in tissues or were too low to be quantified. In one case, a value of 0.03 mg/kg close to the sensitivity limit (0.01 mg/kg) was measured, confirming that the bioaccumulation potential of the test substance is considered negligible.
The OB 3b-A analogous substance is the methyl/hydroxyethylamino derivative, disulphonated sodium salt, member of the Stilbene Fluorescent Whitening Agents category. It is the least water soluble among all the category members and thus it is expected to be the member in which the absorption is the most favourite process; this characteristic make it the most potentially bioaccumulative and therefore the conservative preferred representative.
For completeness sake, the Bioconcentration Factor (BCF) value was calculated using BCFBAF v3.01 tool, an application contained in the EpiSuite 4.1[1]. The estimation takes into account the substance is a ionic compound. The BCF estimated value from regression-based method is 0.5 (BCF = 3.175 l/kg wet-wt), in agreement with the common value of non bioaccumulative substances.
[1] EpiSuite is the suite of physical/chemical property and environmental fate estimation programs developed by the EPA’s Office of Pollution Prevention Toxics and Syracuse Research Corporation (SRC).
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.