Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 949-820-9 | 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

Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian cell study: DNA damage and/or repair
- Remarks:
- Comet assay
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2012
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Genotoxicity assessment of vaccine adjuvant squalene
- Author:
- Yüzbaşıoğlu D et al
- Year:
- 2 013
- Bibliographic source:
- Food Chem Toxicol. 2013 Jun;56:240-6
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The in vivo DNA damaging potential of squalene was evaluated in rats following sub-cutaneous injection and quantification of tail length and tail intensity.
- GLP compliance:
- not specified
- Type of assay:
- mammalian comet assay
Test material
- Reference substance name:
- 2,6,10,15,19,23-hexamethyltetracosa-2,6,10,14,18,22-hexaene
- EC Number:
- 203-826-1
- EC Name:
- 2,6,10,15,19,23-hexamethyltetracosa-2,6,10,14,18,22-hexaene
- Cas Number:
- 111-02-4
- Molecular formula:
- C30H50
- IUPAC Name:
- 2,6,10,15,19,23-hexamethyltetracosa-2,6,10,14,18,22-hexaene
- Details on test material:
- - Name of test material (as cited in study report): Squalene
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- not specified
- Details on test animals or test system and environmental conditions:
- Wistar rats (10–12weeks old) were procured from RefikSaydam National Public Health Agency, Experimental Animal Unit (Ankara, Turkey).Rats were kept in separate cages in an experimental room under controlled conditions of temperature (22±2 C) and humidity (50– 60%) with feed and water being available ad libitum. Lighting was controlled to provide 12 h artificial light followed by 12 h darkness.
Administration / exposure
- Route of administration:
- subcutaneous
- Vehicle:
- Vehicle(s)/solvent(s) used: None- Duration of treatment / exposure:
- Group 1 was the treatment group studied 1day after the squalene injection.
Group 2 was studied 14 days after squalene injection - Frequency of treatment:
- Single
- Post exposure period:
- 1 and 14 days
Doses / concentrations
- Remarks:
- Doses / Concentrations: 0, 0.07, 0.14, 0.28, 0.56, 1.12 mg/kg bw
Basis: nominal concentration
- No. of animals per sex per dose:
- 5 animals per dose
- Control animals:
- yes, concurrent no treatment
- Positive control(s):
- yes, with mitomycin-C 2 mg/Kg
Examinations
- Evaluation criteria:
- Quantification of DNA breakage was realized using Comet Image Analysis System (‘‘Comet Assay IV’’, Perceptive Instruments Ltd., UK).At least 300 comets for each experimental group were recorded as tail length and tail intensity.
- Statistics:
- For data evaluation, the z-test was used for the percentage of abnormal cells, CA/cell, MI, RI, NDI, MN assays. The t-test was applied for SCEs and comet assay results to determine the statistical difference between treated and untreated samples. Dose–response relationships were determined from the correlation and regression coefficients for the percentage of abnormal cells, CA/cell, SCE, mean MN and DNA.
Results and discussion
Test results
- Key result
- Sex:
- not specified
- Genotoxicity:
- positive
- Toxicity:
- no effects
- Vehicle controls validity:
- not specified
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- DNA damage was seen in lymphocytes of rats one day after injection of squalene in in vivo (Group 1). Squalene significantly increased Comet Tail Length (CTL) at 0.14, 0.28, 0.56 mg/kg doses however it significantly decreased CTL at 0.07 and 1.12 mg/kg doses. Whereas, squalene decreased comet tail intensity (CTI) at all doses (except 0.28 mg/kg), however, this decrease was significant only at 0.07 and 1.12 mg/kg doses compared to control. In contrast to the results obtained for group 1, in group 2, squalene significantly increased both CTL and CTI (except 0.07 mg/kg) at all doses used but 1.12 mg/kg.
Any other information on results incl. tables
For result tables, kindly refer to the attached background material section of the IUCLID.
Applicant's summary and conclusion
- Conclusions:
- Under the test conditions, the substance was considered to be genotoxic in an in vivo comet assay in rat.
- Executive summary:
A study was performed to investigate the genotoxic potential of the test substance, squalene using in vivo mammalian comet assay in rat. Five dose levels of squalene, determined based on the amount of squalene in human vaccines (0.07 mg/kg, 0.14 mg/kg, 0.28 mg/kg, 0.56 mg/kg, 1.12 mg/kg) were given to rats subcutaneously for each treatment groups (5 animals/groups). In addition, an untreated control and a positive control (mitomycin-C,2mg/kg) were also used to test the validity of the assay for all treatment groups. Rat blood samples taken from two different groups were used in in vivo Comet assay. Group 1 was the treatment group studied 1 day after the squalene injection. Group 2 was studied 14 days after squalene injection. For in vivo comet assay, approximately 100 µL whole blood was collected from rat’s tail vein into lithium–heparin tubes. Due to the intensity of cells, blood samples were diluted and suspended with phosphate buffer (pH:7.4) in 1:1 ratio and then centrifuged. Lymphocytes were isolated by Biocoll separating solution. After the isolation step, lymphocytes were resuspended in PBS (phosphate buffered saline). Afterwards, the protocol for in vitro comet assay was applied. Quantification of DNA breakage was realized using Comet Image Analysis System. At least 300 comets for each experimental group were recorded as tail length and tail intensity. DNA damage was seen in lymphocytes of rats one day after injection of squalene in in vivo (Group 1). Squalene significantly increased Comet Tail Length (CTL) at 0.14, 0.28, 0.56 mg/kg doses however it significantly decreased CTL at 0.07 and 1.12 mg/kg doses. Whereas, squalene decreased comet tail intensity (CTI) at all doses (except 0.28 mg/kg), however, this decrease was significant only at 0.07 and 1.12 mg/kg doses compared to control. In contrast to the results obtained for group 1, in group 2, squalene significantly increased both CTL and CTI (except 0.07 mg/kg) at all doses used but 1.12 mg/kg. Under the test conditions, the substance was considered to be genotoxic in an in vivo comet assay in rat (Yüzbaşıoğlu, 2013).
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.