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EC number: 918-906-8 | CAS number: 65684-27-7
- 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
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Endpoint summary
Administrative data
Key value for chemical safety assessment
Additional information
Analogue justification
A study on the in vitro genetic toxicity of the target substance glyceryl undecylenate (CAS 123759-97-7) is available, while no data on the in vitro genetic toxicity in mammalian cells of glyceryl undecylenate are available. The genetic toxicity assessment was therefore partly based on studies conducted with analogue substances as part of a read across approach, which is in accordance with Regulation (EC) No. 1907/2006, Annex XI, 1.5. For each specific endpoint the source substance(s) structurally closest to the target substance is/are chosen for read-across, with due regard to the requirements of adequacy and reliability of the available data. Structural similarities and similarities in properties and/or activities of the source and target substance are the basis of read-across. A detailed justification for the read across approach is provided in the technical dossier (see IUCLID Section 13).
Genetic toxicity (mutagenicity) in bacteria in vitro
CAS 123759-97-7
The potential mutagenicity of glyceryl undecylenate was assessed in the S. typhimurium strains TA 1535, TA 1537, TA 98 and TA 100, and in E. coli WP2uvrA pKM in an Ames test performed according to OECD guideline 471 and under GLP conditions (Cathalot, 2015). Concentrations ranging from 0.06 to 0.56 mg/plate were selected for treatment in the main assay, with and without metabolic activation. Plate incorporation was applied in experiment 1, while the preincubation method with 20 min preincubation time was applied in experiment 2. Cytotoxicity was observed from 0.56 mg/plate in the preliminary and main assay, without metabolic activation. No increase in the mean number of revertants per plate was observed when compared to controls. The positive and negative controls included for each test strain were shown to be valid. The results for the assays performed without metabolic activation are considered to be valid. The test substance was not tested up to 5 mg/plate or to the cytotoxic concentration or to the precipitation limit with metabolic activation, as the highest concentration tested was 0.56 mg/plate. Therefore these results are considered to be invalid. The test substance was considered to be non-mutagenic under the conditions of the study, without metabolic activation.
CAS 91031-52-0
A bacterial gene mutation assay with Glycerides, C8-18 and C18-unsatd. mono- and di-, acetates was performed according to OECD guideline 471 and GLP (Sarada, 2010). Two independent experiments were performed both in the presence or absence of metabolic activation in S. typhimurium TA 1535, TA 1537, TA 98 and TA 100 and in E. coli WP2 uvrA. In the preliminary toxicity screening, growth inhibitory effects were observed at ≥ 20 µg/plate in S. typhimurium TA 98 and TA 1537 (without metabolic activation), at ≥ 78 µg/plate in S. typhimurium TA 100 and TA 1535 (without metabolic activation), and at ≥ 313 µg/plate in all S. typhimurium strains with metabolic activation. Based on these results, concentrations ranging from 0.61 to 78 µg/plate were used for the tester strains TA 100, TA 1535, TA98 and TA 1537 in the absence of metabolic activation, whereas concentrations ranging from 10 to 313 µg/plate were applied for treatment of the tester strains TA 100, TA 1535, TA 98 and TA 1537 in the presence of metabolic activation. Since no cytotoxicity was seen in E. coli WP2 uvrA, the maximum test concentration of 5000 µg/plate and concentrations of 2500, 1250, 625 and313 µg/plate were selected for treatment in the main assay. Precipitation of the test substance was observed on the plates with E. coli WP2 uvrA at test concentrations ≥ 1250 µg/plate without metabolic activation and at ≥ 2500 µg/plate with metabolic activation in both experiments. No increase in mean revertant number was observed in any bacterial strain after exposure to the test substance in the presence or absence of metabolic activation. The positive and negative controls revealed the expected results. Under the conditions of this assay, the test substance did not induce gene mutations in the selected strains of S. typhimurium and in E. coli WP2 uvrA in the absence and presence of metabolic activation, respectively.
Genetic toxicity (cytogenicity) in mammalian cells in vitro
CAS 91052-13-0
An in vitro mammalian chromosome aberration test with was performed in Chinese hamster lung cells (CHL/IU) with glycerides, C8-18 and C18-unsatd. mono- and di-, acetates, according to OECD guideline 473 and under GLP conditions (Seki, 2010). In a preliminary cell growth inhibition test with concentrations ranging from 9.8 to 5000 µg/plate, no significant inhibition of cell growth was observed after 4 h exposure in the presence and absence of metabolic activation (S9 mix). However, a moderate reduction of cell growth of 30-40% compared with the controls was observed at concentrations ranging from 156-1250 µg/mL after 24 and 48 h continuous exposure. Based on the results of this study, concentrations of 20, 39, 78 and 156 µg/mL (with and without metabolic activation) were used for the analysis of chromosomal aberrations after short-term exposure (6 h). In addition, concentrations of 78, 156, 313, 625, 1250, 2500 and 5000 µg/mL were chosen for analysis chromosomal aberrations after continuous exposure (24 and 48 h), without metabolic activation. No increase in the number of cells with chromosomal aberrations was observed compared to controls in any of the experiments performed. No cytotoxic effects were observed in any of the experiments performed. An oily precipitation of the test substance was observed at concentrations ≥ 78 µg/mL, but did not interfere with chromosomal analysis of the cells. The positive controls included during short-term and continuous exposure were shown to be valid. Under the conditions of this experiment, the test substance was considered to be not clastogenic in Chinese hamster lung cells (CHL/IU), in the presence and absence of metabolic activation.
CAS 111-03-5
2,3-dihydroxypropyl oleate was assessed in an in vitro mammalian chromosome aberration test in Chinese hamster lung cells (CHL/IU) according to OECD guideline 473 and under GLP conditions (Nakajima, 2005). In a preliminary cytotoxicity test, cells were exposed to concentrations ranging from 6.96 to 3565 µg/mL for a continuous 24-h exposure period with metabolic activation (S9-mix) or a short-term 6 h exposure with and without metabolic activation. The test substance was not cytotoxic after short-term exposure at any concentration in the presence of metabolic activation. Without metabolic activation, relative growth was reduced to about 71% of the control value after a period of 6 h. Continuous exposure for 24 h without metabolic activation caused no cytotoxicity up to concentrations of 1783 µg/mL. At 3565 µg/mL, relative growth was decreased to ca. 13 % of the control value. The concentration leading to 50% cytotoxicity was calculated to be 2738 µg/mL. Based on these results, concentrations of 891, 1783 and 3565 µg/mL (with and without metabolic activation) were selected for chromosome analysis after short-term exposure, and concentrations of 55.7, 111, 223 and 446 µg/mL (without metabolic activation) were chosen for chromosome analysis after continuous exposure. No increase in the number of cells with chromosomal aberrations was observed compared to controls in any of the experiments performed. No cytotoxic effects were observed after short-term exposure, but the test substance was cytotoxic at 446 µg/mL after 24 hours continuous treatment. Visible precipitation of the test substance was observed at concentrations ≥ 223 µg/mL; however, this did not interfere with chromosomal analysis. The positive controls included during short-term and continuous exposure were shown to be valid. Under the conditions of this experiment, the test substance was considered to be not clastogenic in Chinese hamster lung cells (CHL/IU) in the presence and absence of metabolic activation.
Genetic toxicity (mutagenicity) in mammalian cells in vitro
CAS 736150-63-3
An in vitro mammalian cell gene mutation assay was performed with glycerides, castor-oil-mono, hydrogenated, acetates according to OECD guideline 476 and under GLP conditions (Edwards, 2002). In the first experiment, mutations at the TK locus of mouse lymphoma L5178Y cells were investigated at concentrations of 625, 1250, 2500, 3600 and 5000 µg/mL. The L5178Y cells were exposed to the test material for a period of 3 h in the presence and for 4 h in the absence of metabolic activation (S9-mix), respectively. At 3600 µg/mL, the relative total growth was 1-11% compared with the negative controls. In the second experiment, cells were exposed to a concentration range of 313 to 3600 µg/ for a period of 24 h, without metabolic activation, and to a concentration range of 156-3600 µg/mL for a period of 4 h, with metabolic activation. Since the relative growth without metabolic activation was very low (0-2%) at all test concentrations, the 24-h treatment of cells in the absence of metabolic activation was repeated with concentrations ranging from 2.5-320 µg/mL, which resulted in appropriate levels of cytotoxicity (10-20% relative growth) at 160 µg/mL. In the presence of metabolic activation, the relative total growth was 37 and 0% at 2500 and 3600 µg/mL in the second experiment, respectively. After a 3-day expression period of the cultures, the resistance to 5-trifluorothymidine (TFT) was determined in all experiments. The test substance did not induce a significant increase in the mutant frequency at any preparation time and dose concentration. The positive controls significantly increased mutant frequency. In conclusion, the test substance did not induce mutations in mouse-lymphoma L5178Y cells, neither in the presence nor in the absence of a metabolic activation system, under these experimental conditions.
Short-, medium- and long-chain triglycerides (SCT, MCT, LCT)
The SALATRIM (short- and long-chain acyl triglyceride molecules) family of triacylglycerols was assessed using a gene mutation assay in cultured mammalian cells (Chinese hamster ovary (CHO-K1) cells) similarly to OECD guideline 476 (Hayes et al., 1994). Gene mutations at the HPRT locus were investigated in the presence and absence of metabolic activation (rat liver S9-mix) with concentrations of 31.25, 62.5, 125, 250, 500 and 1000 µg/mL. Two cultures were tested per dose level. The highest concentration was limited by the low solubility of the fats in the assay medium. No significant cytotoxicity was reported. No increase in mutant frequency was observed at any concentration tested whether with or without metabolic activation. The positive controls significantly increased the mutant frequency. Therefore, it was concluded that under the conditions of the study, the test material was not mutagenic at the HPRT locus of Chinese hamster ovary cells in the absence and presence of metabolic activation.
Overall conclusion for genetic toxicity
The target substance glyceryl undecylenate (CAS 123759-97-7) was shown not to induce gene mutations in bacteria without metabolic activation.There are no available studies on the genetic toxicity ofglyceryl undecylenatein mammalian cells. Analogue read-across from 4 source substances was applied fromin vitro studies in bacterial cells, from in vitro studies on cytogenicity and from gene mutations in mammalian cells. The results of the available in vitro studies were consistently negative. Based on the available data and following the analogue approach, glyceryl undecylenate is not expected to be mutagenic in vitro and clastogenic in vitro.
Justification for selection of genetic toxicity endpoint
Hazard assessment is conducted with a study performed using the target substance and by means of read-across from structural analogues. All available in vitro genetic toxicity studies were negative. All available studies are adequate and reliable based on the identified similarities in structure and intrinsic properties between source and target substances and overall quality assessment (refer to the endpoint discussion for further details).
Short description of key information:
Ames test (OECD 471): negative with and without metabolic activation in S. typhimurium TA 1535, TA 1537, TA 100 and TA 98 and in E. coli WP2 uvrA pKM
Chromosome aberration (OECD 473): negative in Chinese hamster lung cells (CHL/IU) with and without metabolic activation
Gene mutation in mammalian cells (OECD 476): negative in mouse lymphoma L5178Y cells and Chinese hamster ovary (CHO-K1) cells with and without metabolic activation
Endpoint Conclusion: No adverse effect observed (negative)
Justification for classification or non-classification
According to Article 13 of Regulation (EC) No. 1907/2006 "General Requirements for Generation of Information on Intrinsic Properties of substances", information on intrinsic properties of substances may be generated by means other than tests e.g. from information from structurally related substances (grouping or read-across), provided that conditions set out in Annex XI are met. Annex XI, "General rules for adaptation of this standard testing regime set out in Annexes VII to X” states that “substances whose physicochemical, toxicological and ecotoxicological properties are likely to be similar or follow a regular pattern as a result of structural similarity may be considered as a group, or ‘category’ of substances. This avoids the need to test every substance for every endpoint". Since the analogue concept is applied to glyceryl undecylenate (CAS 123759-97-7), data will be generated from data available for reference source substance(s) to avoid unnecessary animal testing. Additionally, once the analogue read-across concept is applied, substances will be classified and labelled on this basis.
Therefore, based on the analogue read-across approach, the available data on genetic toxicity do not meet the classification criteria according to Regulation (EC) 1272/2008 and are therefore conclusive but not sufficient for classification.
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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