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EC number: 500-116-6 | CAS number: 52609-19-5 1 - 2.5 moles ethoxylated
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
Ames (OECD 471): not mutagenic in bacteria
Chromosomal Aberration (OECD 473): not clastogenic in mammalian cells
HPRT (OECD 476): not mutagenic in mammalian cells
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Genetic toxicity in vivo
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
To cover the endpoint genotoxicity of substance C16AE (CAS 52609-19-5), studies from C16-18AE (CAS 68439-49-6) were taken for read-across. Read-across is justified because the length of the alkyl chain and the grade of ethoxylation does not exert any meaningful influence on genotoxicity. Moreover, the structure of alcohol ethoxylates (AE) is not of concern for potential genotoxicity and in all available in-vitro and in-vivo genotoxicity assays, there was no indication of genetic toxicity of a broad range of structurally different AE (HERA, 2009).
Mutagenicity in bacteria was assessed in a study performed according to OECD Guideline 471. Salmonella typhimurium strains TA 1535, TA 1537, TA 98 and TA 100 were treated with C16-18AE (CAS 68439-49-6) using the plate incorporation method as well as the preincubation method, both with and without the addition of a rat liver S9-mix. The dose ranges were for the plate incorporation test were 50, 160, 500, 1600 and 5000 µg/plate; for the first preincubation test 50, 150, 300, 900 and 1500 µg/plate and for the second one 10, 25, 50, 100 and 150 µg/plate. All tests were done in triplicates. The vehicle (acetone) and negative (untreated) control plates produced counts of revertant colonies within an acceptable range. All positive controls used in the test induced marked increases in the frequency of revertant colonies, both with and without the metabolising system. A reproducible mutagenic activity of the test material to any of the tester strains was not observed with and without metabolic activation. Thus, under the conditions of this test the test substance can be regarded as not mutagenic in bacteria.
The clastogenic potential was assessed in a chromosomal aberration test with C16-18AE (CAS 68439-49-6) in mammalian cells according to OECD Guideline 473. Chinese hamster ovary cells (CHO) were exposed to 313, 625, 1250, 2500 and 5000 µg/mL in the presence and 1.25, 2.5, 5, 10, 20, 39 and 78 µg/mL in the absence of metabolic activation. Positive and vehicle (1% ethanol) control cultures were included in each assay. No increases in the number of chromosome aberrations in the presence or absence of metabolic activation were seen at any concentration tested. Appropriate reference mutagens used as positive controls showed a significant increase in chromosome aberrations, thus indicating the sensitivity of the assay, and the efficacy of the S9-mix. Hence, the test substance can not be regarded as clastogenic.
The mutagenic potential in mammalian cells was assessed with C16-18AE (CAS 68439-49-6) by a HPRT-assay according to OECD Guideline 476. Following pre-tests with the concentration ranging from 1-100 µg/mL, the latter being the solubility limit of the test substance, Chinese hamster ovary cells were exposed for 4 h to concentrations of 1.8, 6, 18, 60 and 100 µg/mL in the absence and presence of metabolic activation by rat liver S9-mix. No dose-related increases in mutant colony numbers were obtained in two independent experiments with the test substance in either the presence or absence of S9-mix. Appropriate reference mutagens used as positive controls produced highly significant increases in mutation frequency, thus indicating the sensitivity of the assay. Therefore, the test substance is regarded as not mutagenic in mammalian cells.
In conclusion, C16AE (CAS 52609-19-5) is regarded as non-genotoxic.
Justification for selection of
genetic toxicity endpoint
No study selected as all results were negative.
Justification for classification or non-classification
According to the classification
criteria of Regulation (EC) No. 1272/2008 (CLP) the substance does not
need to be classified for genotoxicity.
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