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Diss Factsheets
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EC number: 701-257-8 | 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
Description of key information
Within a 47 d degradation study according to the OECD Guideline 301F, 61 % of
the test substance (sulfonic acids, C14 -17 alkane, Ph esters) were degraded based on the oxygen consumption (Bayer Industry Services, 2004).
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable
Additional information
The lowest degradation was observed in the study Mitsubishi (2003) with 23 % degradation after 28 days. Despite that study showed the lowest degradation it was not chosen as key study.
According to the OECD Guideline No 301, the activity of the used sludge should be proved by the means of a reference substance showing a degradation of at least 40 % and 65 % after 7 d and 14 d, respectively. As aniline, chosen as reference substance, was degraded about 54 % (7 d) and 63 % (14 d), the validity criteria set out by the guideline are not completely fulfilled by Mitsubishi (2003). The degradation power of the sludge slowed down after seven days (as can be seen at the degradation of the reference substance). The degradation of sulfonic acid, C14-17-alkane, Ph esters starts after a lag phase of approximately 7 days. Thus, the low degradation might be the result of the low activity of the sludge rather than of the non-degradability of the test item.
Therefore, the study of Bayer Industry Services (2004) was chosen as key study, as it was a GLP Guideline study fulfilling the validity criteria. Furthermore, the test was prolonged to 47 days as the plateau was not reached after 28 days.
Additionally, one study with hexadecane sulfonic acid phenyl ester was conducted (Bayer AG, 2003). That substance was chosen as representative for the UVBC substance sulfonic acids, C14-17-alkane, Ph esters as the aliphatic part of the UVCB substance mainly consists of linear C14 to C17 chains. The degradation of the test item was delayed as well just starting after day 8 of the degradation study. The degradation curve showed that the plateau was not reached yet after 28 days with still ongoing degradation.
As sulfonic acids, C14-17-alkane, Ph esters did not reach the pass level after 28 days, it cannot be classified as readily biodegradable. But there is evidence, supported by the degradation of the hexadecane sulfonic acid phenyl ester, that degradation takes place just starting after a lag phase of approximately one week. Therefore, the substance can be scored as almost biodegradable.
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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