Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
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: 942-135-6 | 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 somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- not stated
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was conducted according to a test protocol that is comparable to the appropriate OECD test guideline, with acceptable restrictions. Only 1000 erythrocytes were scored per animal, full experimental details were not reported, toxicity details were lacking. It was not compliant with GLP. Read across to the registered substance is considered scientifically justified.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- The toxicity of behenyl alcohol: I. Genotoxicity and subchronic toxicity in rats and dogs
- Author:
- Iglesias G, J J Hlywka, J E Berg, M H Khalil, L E Pope and D Tamarkin
- Year:
- 2 002
- Bibliographic source:
- Regulatory Tox. and Pharm. 36, 69-79 2002a
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- (only 1000 PCEs per animal scored for micronuclei)
- Principles of method if other than guideline:
- Well-conducted study according to protocol very similar to OECD guideline 474
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Docosan-1-ol
- EC Number:
- 211-546-6
- EC Name:
- Docosan-1-ol
- Cas Number:
- 661-19-8
- Molecular formula:
- C22H46O
- IUPAC Name:
- docosan-1-ol
- Details on test material:
- - Name of test material (as cited in study report): behenyl alcohol
- Substance type: colourless, waxy solid
- Physical state: solid
- Analytical purity: no data, but for repeated dose toxicity (oral), 98%
- Impurities (identity and concentrations): no data
- Composition of test material, percentage of components: no data
- Isomers composition: no data
- Purity test date: no data
- Lot/batch No.: no data, but for repeated dose toxicity (oral), obtained from Condea, Germany
- Expiration date of the lot/batch: no data
- Stability under test conditions: no data
- Storage condition of test material: no data
- Other:
- Melting point: 70 deg C
- Soluble in: ethanol and chloroform
- Insoluble in: water
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: BRL Tierfarm Fullinsdorf, Switzerland
- Age at study initiation: >=10 weeks
- Weight at study initiation: no data
- Assigned to test groups randomly: no data
- Fasting period before study: 18 hours, but continued to receive water ad libitum
- Housing: Markrolon Type 1 cages with wire mesh tops and granulated soft wood bedding
- Diet (e.g. ad libitum): standard pellet diet, ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21
- Humidity (%): not regulated
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12 / 12
IN-LIFE DATES: no data
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: polyethylene glycol
- Justification for choice of solvent/vehicle: no data
- Concentration of test material in vehicle: no data [calculated: 5, 15 and 50 mg/ml]
- Amount of vehicle (if gavage or dermal): 10 ml/kg bw
- Lot/batch no. (if required): no data
- Purity: no data - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: few details; test material suspended in vehicle
- Duration of treatment / exposure:
- single administration
- Frequency of treatment:
- single administration
- Post exposure period:
- none
Doses / concentrations
- Remarks:
- Doses / Concentrations:
50, 150, 500 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- 6
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
- Justification for choice of positive control(s): no data
- Route of administration: presumably oral gavage
- Doses / concentrations: 40 mg/kg bw
Examinations
- Tissues and cell types examined:
- bone marrow cells
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: based on previous study - 500 mg/kg bw estimated to be the "maximum attainable dose"
TREATMENT AND SAMPLING TIMES (in addition to information in specific fields): 24, 48 and 72 hours after dosing
DETAILS OF SLIDE PREPARATION: femurs removed, marrow flushed out with foetal calf serum, cell suspension centrifuged and supernatant discarded, small drop of cell pellet spread on slide, air dried, stained with May-Grunwald, mounted; 1 slide/sample
METHOD OF ANALYSIS: 1000 polychromatic erythrocytes (PCEs) scored for micronuclei; polychromatic:normochromatic (PCE:NCE) ratio scored
OTHER: only 5/sex per dose level evaluated - Evaluation criteria:
- To be considered positive, either a statistically significant dose-related increase in the number of micronucleated PCEs or a reproducible, statistically significant positive response for at least one dose level
- Statistics:
- Mann-Whitney test
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Remarks:
- presumably toxic at >500 mg/kg bw
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: no data
- Solubility: no data
- Clinical signs of toxicity in test animals: no data
- Evidence of cytotoxicity in tissue analyzed: no data
- Rationale for exposure: no data
- Harvest times: no data
- High dose with and without activation: no data
- Other: presumably toxic above 500 mg/kg bw since this maximum dose was chosen for the main study on the basis of the results of the range-finding study
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): 0.03-0.09% for vehicle controls, 0.04-0.10% for test material treated, 0.71% for positive control
- Ratio of PCE/NCE (for Micronucleus assay): 1.05-1.27 for vehicle controls, 0.98-1.55 for test material treated, 0.93 for positive control
- Appropriateness of dose levels and route: appropriate (top dose was apparently the maximum tolerated dose, oral route relevant to humans)
- Statistical evaluation: no statistically significant increases in the frequency of micronuclei in mice treated with the test material; statistical significance not presented for positive control
Any other information on results incl. tables
Table 1 Results of micronucleus assay 24 hour sampling time
Treatment |
Suspending agent |
Low dose |
Mid dose |
High dose |
Concentration mg/kg bw |
0 |
40 |
50 |
150 |
Harvest time |
24 |
24 |
24 |
24 |
Micronucleated PCE (%) |
0.03 |
0.71 |
0.07 |
0.08 |
Ratio PCE/NCE |
1.27 |
0.93 |
0.98 |
1.07 |
Table 2 Results of micronucleus assay 48 hour sampling time
Treatment |
Suspending agent |
Test substance |
Test substance |
Test substance |
Concentration mg/kg bw |
0 |
50 |
150 |
500 |
Harvest time |
48 |
48 |
48 |
48 |
Micronucleated PCE (%) |
0.09 |
0.1 |
0.04 |
0.05 |
Ratio PCE/NCE |
1.05 |
1.06 |
1.01 |
1.23 |
Table 3 Results of micronucleus assay 72 hour sampling time
Treatment |
Suspending agent |
Low dose |
Mid dose |
High dose |
Concentration mg/kg bw |
0 |
50 |
150 |
500 |
Harvest time |
72 |
72 |
72 |
72 |
Micronucleated PCE (%) |
0.09 |
0.09 |
0.05 |
0.07 |
Ratio PCE/NCE |
1.41 |
1.33 |
1.55 |
1.46 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
In a reliable study, behenyl alcohol (C22) did not increase the incidence of micronuclei in mouse bone marrow cells after a single oral gavage dose of up to 500 mg/kg bw.
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.