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EC number: 293-026-9 | CAS number: 91050-80-5
- 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
Key value for chemical safety assessment
Additional information
Experimental bioaccumulation data are not available for Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] (CAS 91050-80-5). The high log Kow (> 10) as an intrinsic chemical property indicates a potential for bioaccumulation. However, the information gathered on environmental behavior and metabolism, in combination with QSAR-estimated values, provide enough evidence (evidence (in accordance to the Regulation (EC) No 1907/2006, Annex XI General rules for adaptation of the standard testing regime set out in Annexes VII to X, 1.2), to cover the data requirements of Regulation (EC) No 1907/2006, Annex IX to state that the substance is likely to show negligible bioaccumulation potential.
Environmental behavior
Due to ready biodegradability and high potential of adsorption, Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] can be effectively removed in conventional Sewage Treatment plants (STPs) either by biodegradation or by sorption to biomass. The low water solubility (< 0.05 mg/L) and high estimated log Kow values (log Kow > 10) indicate that Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] is highly lipophilic. If released into the aquatic environment, the substance undergo extensive biodegradation and sorption on organic matter, as well as sedimentation. Thus, the bioavailability of this substance in the water column is reduced rapidly. The relevant route of uptake of Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] in organisms is considered predominately by ingestion of particle bounded substance.
Moleculare size
According to Regulation (EC) No. 1907/2006, Annex IX, 9.3.2., Column 2, a study on bioaccumulation is not required since the substance has a low potential to cross biological membranes. As the main components of Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] have a molecular weight higher than 700 g/mol (807 – 1604 g/mol), a reduced BCF is expected according to Guidance on information requirements and chemical safety assessment; Chapter R.11: PBT Assessment; ECHA, 2012. According to Rekker and Mannhold (1992) a molecular weight of > 700 in combination with a calculated log Kow of > 8 can be used as enough evidence to conclude that a substance is unlikely to bioaccumulate (Guidance on information requirements and chemical safety assessment; Chapter R.11: PBT Assessment; ECHA, 2012).
Metabolism of aliphatic esters
Should Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] be taken up by fish during the process of digestion and absorption in the intestinal tissue, aliphatic esters like Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] are expected to be initially metabolized via enzymatic hydrolysis to the corresponding free fatty acids and the free fatty alcohols.. The hydrolysis is catalyzed by classes of enzymes known as carboxylesterases or esterases (Heymann, 1980). The most important of which are the B-esterases in the hepatocytes of mammals (Heymann, 1980; Anders, 1989). Carboxylesterase activity has been noted in a wide variety of tissues in invertebrates as well as in fish (Leinweber, 1987; Soldano et al, 1992; Barron et al., 1999, Wheelock et al., 2008). The catalytic activity of this enzyme family leads to a rapid biotransformation/metabolism of xenobiotics which reduces the bioaccumulation or bioconcentration potential (Lech & Bend, 1980). It is known for esters that they are readily susceptible to metabolism in fish (Barron et al., 1999) and literature data have clearly shown that esters do not readily bioaccumulate in fish (Rodger & Stalling, 1972; Murphy & Lutenske, 1990; Barron et al., 1990). In fish species, this might be caused by the wide distribution of carboxylesterase, high tissue content, rapid substrate turnover and limited substrate specificity (Lech & Melancon, 1980; Heymann, 1980).
Metabolism of enzymatic hydrolysis products
Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] (CAS #91050-80-5) are hydrolysed to the corresponding alcohol (diglycerol) and fatty acid by esterases (Fukami and Yokoi, 2012). Depending on the route of exposure, esterase-catalysed hydrolysis takes place at different sites in the organism: after oral ingestion, esters of diglycerol and fatty acids will undergo chemical changes already in the gastro-intestinal fluids as a result of enzymatic hydrolysis. In contrast, substances which are absorbed through the pulmonary alveolar membrane or through the skin enter the systemic circulation directly before entering the liver where hydrolysis will basically take place.
In an in vitro enzymatic digestion method using fresh pancreatic juice plus bile described by King et al. (1970) the fatty acid labelled polyglycerol esters were studied. Thin layer chromatography (TLC) and radioassay procedures were used to determine the distribution of 14C among the products of digestion.
After enzymatic digestion of oleate-labelled polyglycerol ester, 89-92% of the recovered 14C was present as free oleic acid, whereas the remaining 8 and 11% was unhydrolysed or partially hydrolysed starting material. Hydrolysis of the eicosanoate-labelled polyglycerol ester was much slower than the oleate ester and only 21% of the 14C was recovered as free eicosanoic acid (Michael and Coots, 1971)
After hydrolysis the first cleavage products, fatty acids C16-18, are stepwise degraded by beta-oxidation based on enzymatic removal of C2 units in the matrix of the mitochondria in most vertebrate tissues. The C2 units are cleaved as acyl-CoA, the entry molecule for thecitric acid cycle. The omega and alpha-oxidation, alternative pathways for oxidation, can be found in the liver and the brain, respectively (CIR, 1987).
For the second cleavage product polyol diglycerol, is assumed to be rapidly excreted and metabolism via cleavage of the ether bond to glycerol will not occur as for the related triglycerol (Michael and Coots, 1971).
Data from QSAR calculation
Additional information on bioaccumulation could be gathered through BCF/BAF calculations of representative fatty acid components (C16 (tri, tetra and penta) and C18 (tri, tetra and penta)) using BCFBAF v3.01. The estimated BCF/BAF values of 0.89 and 0.89 L/kg indicate low bioaccumulation potential in organisms, when including biotransformation (Arnot-Gobas estimate, including biotransformation, upper trophic). Even though the representative fatty acid components of the substance are outside the applicability domain of the model they can be used as supporting indication that the potential of bioaccumulation is low. The model training set is only consisting of substances with log Kow values of 0.31 - 8.70. But it supports the tendency that substances with high log Kow values (> 7) have a lower potential for bioconcentration as summarized in the ECHA Guidance R.11 and they are not expected to meet the B/vB criterion (ECHA, 2012).
Conclusion
The biochemical process metabolizing aliphatic esters is ubiquitous in the animal kingdom. Based on the enzymatic hydrolysis of aliphatic esters and the subsequent metabolism of the corresponding carboxylic acid and alcohol, it can be concluded that the high log Kow, which indicates a potential for bioaccumulation, overestimates the true bioaccumulation potential of Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] since it does not reflect the metabolism of substances in living organisms. BCF/BAF values estimated with the BCFBAF v3.01 program also indicate that Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] will not be bioaccumulative (all well below 2000 L/kg). Taking all these information into account, it can be concluded that the bioaccumulation potential of Fatty acids, C16-18, tetraesters with 3,3'-oxybis[1,2-propanediol] is low.
A detailed reference list is provided in the technical dossier (see IUCLID, section 13) and within CSR.
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