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EC number: 451-530-8 | CAS number: 736150-63-3
- 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
Sediment toxicity
Administrative data
Link to relevant study record(s)
Description of key information
Bacterial lipases in the sewage treatment plant and in the environment are expected to hydrolyze TS-ED 532 to a very large extend into acetic acid, glycerol and 12-acetoxy- and/or 12-hydroxystearic acid. These degradation products are all readily biodegradable. Neither acetic acid nor glycerol (both have a logKow <0) will partition to sediment in any significant degree. 12-acetoxy- and/or 12-hydroxystearic acid have a calculated logKow (EpiSuite) of 6.41 respectively 7.41 (EpiSuite). These degradation products have very similar fate properties to the mother chemical.
In the sewage treatment plant (STP), TS-ED 532 and the degradation products (12-acetoxy- and/or 12-hydroxystearic acid) will behave in a very similar manner to oil also entering the STP. Measurements have shown a removal of the oil of >99% (“Miljøfremmede stoffer i spildevand og slam”. Miljøprojekt nr. 325, 1996. Danish EPA). The same removal is assumed for TS-ED 532 and the degradation products (12-acetoxy- and/or 12-hydroxystearic acid).
The concentration in the inlet to the STPs during the formulation/end-use and service life stages is not expected to exceed the water solubility of TS-ED 532 (and its degradation products). As the removal in the STP is assessed to >99%, the RCR for sediment is calculated at 0.4, which is below 1 for the formulation, end-use and service-life cycle phases.
Overall, it is concluded that there is no need to investigate further the effects of TS-ED 532 and/or relevant degradation products on sediment organisms.
Key value for chemical safety assessment
Additional information
Bacterial lipases in the sewage treatment plant and in the environment are expected to hydrolyze TS-ED 532 to a very large extend into acetic acid, glycerol and 12-acetoxy- and/or 12-hydroxystearic acid. These degradation products are all readily biodegradable. Neither acetic acid nor glycerol (both have a logKow <0) will partition to sediment to any significant degree. 12-acetoxy- and/or 12-hydroxystearic acid have a calculated logKow(EpiSuite) of 6.41 respectively 7.41 (EpiSuite). These degradation products have
fate properties
very similar to TS-ED 532.
In the sewage treatment plant (STP), TS-ED 532 and the degradation products (12-acetoxy- and/or 12-hydroxystearic acid) will behave in a very similar manner to oil also entering the STP. Measurements have shown a removal of the oil of >99% (“Miljøfremmede stoffer i spildevand og slam”. Miljøprojekt nr. 325, 1996. Danish EPA). The same removal is assumed for TS-ED 532 and the degradation products (12-acetoxy- and/or 12-hydroxystearic acid).
The release factor from manufacture of the substance to waste water is assessed to be 0.00008. Only emission during repair and maintenance may place. The emission to air is assessed to be very low due to the low vapour pressure of the substance. With a tonnage of 6000 tonnes/yr and number of emission days set to 300 days/yr, assigning 10% of the whole tonnage to the region, assuming a maximum release to waste water during all life cycle stages of 10%, a RCR in sediment is calculated at 1.6, which is very close to 1. An extra safety factor of 10 was applied for the derivation of the RCR, as the TS-ED 532 and the degradation products (12-acetoxy- and/or 12-hydroxystearic acid) are very hydrophobic so uptake via ingestion of sediment can be important. The approach of using an extra factor of 10 is considered only as a screen for assessing the level of risk to sediment dwelling organisms, and as the RCR is very close to 1, it is assessed that there is no risk to the sediment dwelling organism from the manufacture.
The concentration in the inlet to the STPs during the formulation/end-use and service life stages is not expected to exceed the water solubility of TS-ED 532 (and its degradation products). As the removal in the STP is assessed to >99%, the RCR for sediment is calculated at 0.4, which is below 1 for the formulation, end-use and service-life cycle phases.
Overall, it is concluded that there is no need to investigate further the effects of TS-ED 532 and/or relevant degradation products on sediment organisms.
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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