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EC number: 201-100-9 | CAS number: 78-27-3
- 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:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study conducted in accordance with GLP.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OTS 798.5395 (In Vivo Mammalian Cytogenics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 1-ethynylcyclohexanol
- EC Number:
- 201-100-9
- EC Name:
- 1-ethynylcyclohexanol
- Cas Number:
- 78-27-3
- Molecular formula:
- C8H12O
- IUPAC Name:
- 1-ethynylcyclohexanol
- Test material form:
- other: solid, melt
- Details on test material:
- Please refer to the section "confidential details on test material" below.
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Research Models and Services Germany GmbH, Sandhofer Weg 7, 97633 Sulzfeld, Germany
- Age at study initiation: 8 - 11 weeks
- Weight at study initiation: male mean value 36.0 g (SD +/- 1.7 g), female mean value 28.6 g (SD +/- 1.4 g)
- Assigned to test groups randomly: yes
- Fasting period before study:
- Housing: single
Cage Type: Makrolon Type II/III, with wire mesh top (EHRET GmbH, 79302 Emmendingen, Germany)
Bedding: granulated soft wood bedding (Rettenmaier & Söhne GmbH + Co. KG, 73494 Rosenberg, Germany)
- Diet: pelleted standard diet, ad libitum (Harlan Laboratories B.V.; Postbus 6174; 5960 AD Horst; The Netherlands)
- Water: tap water, ad libitum (Gemeindewerke, 64380 Rossdorf, Germany)
- Acclimation period: minimum of five days
ENVIRONMENTAL CONDITIONS
- Temperature: 22 +/- 2 °C
- Humidity: 45 - 65 %
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): artificial light 6.00 a.m. - 6.00 p.m.
IN-LIFE DATES: From: To:
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle used: corn oil
- Justification for choice of vehicle: relative non-toxicity for the animals
- Concentration of test material in vehicle:
Main experiment:
# Males: 187.5, 375 and 750 mg/kg b.w. as low, mid and high dose
# Females: 100, 200 and 400 mg/kg b.w. as low, mid and high dose
- Amount of vehicle (if gavage or dermal): 10 mL/kg b.w.
- Lot/batch no.: MKBF8603V (Catalogue no.: C8267; Sigma-Aldrich Vertriebs GmbH, 82041 Deisenhofen, Germany) - Frequency of treatment:
- Vehicle control, positive control and dose groups were treated once.
- Post exposure period:
- Samples of bone marrow were taken 24 hours after the treatment and for the highest dose level an additional sample was taken at 48 h after treatment.
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
Males: 187.5, 375 and 750 mg/kg b.w. as low, mid and high dose
Basis:
actual ingested
based on the pre-experiment
- Remarks:
- Doses / Concentrations:
# Females: 100, 200 and 400 mg/kg b.w. as low, mid and high dose
Basis:
actual ingested
based on the pre-experiment
- No. of animals per sex per dose:
- six
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide
- Justification for choice of positive control: standard according to OECD TG 474
- Route of administration: orally
- Doses / concentrations: 40 mg/kg b.w.; dissolved in sterile water; volume administered: 10 mL/kg b.w
Examinations
- Tissues and cell types examined:
- Bone marrow cells
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
The highest dose level represents in each gender the maximum tolerated dose as determined in the pre-experiment.
TREATMENT AND SAMPLING TIMES (in addition to information in specific fields):
Three adequately spaced dose levels spaced by a factor of 2 were administered, and samples were collected at the central sampling interval 24 h after treatment. For the highest dose level an additional sample was taken at 48 h after treatment.
DETAILS OF SLIDE PREPARATION:
The femora of sacrificed animals (using CO2 followed by bleeding) were removed, the epiphyses were cut off and the marrow was flushed out with foetal calf serum using a syringe. The cell suspension was centrifuged at 1500 rpm (390x g) for 10 minutes and the supernatant was discarded. A small drop of the re-suspended cell pellet was spread on a slide. The smear was air-dried and then stained with May-Grünwald (Merck, 64293 Darmstadt, Germany) / Giemsa (Merck, 64293 Darmstadt, Germany). Cover slips were mounted with EUKITT (Kindler, 79110 Freiburg, Germany). At least one slide was made from each bone marrow sample.
METHOD OF ANALYSIS:
Slides were evaluated using microscopes with 100x oil immersion objectives. Per animal (all animals per sex and test group) 2000 polychromatic erythrocytes (PCE) were analysed for micronuclei. To investigate a cytotoxic effect the ratio between polychromatic and normochromatic erythrocytes was determined in the same sample and expressed in polychromatic erythrocytes per 2000 erythrocytes. The analysis was performed with coded slides. - Evaluation criteria:
- A test item is classified as mutagenic if it induces either a dose-related increase or a clear increase in the number of micronucleated polychromatic erythrocytes in a single dose group. Statistical methods (nonparametric Mann-Whitney test) are used as an aid in evaluating the results, if necessary. However, the primary point of consideration is the biological relevance of the results.
A test item that fails to produce a biological relevant increase in the number of micronucleated polychromatic erythrocytes is considered non-mutagenic in this system. - Statistics:
- See evaluation criteria above.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- other: vehicle control serves as negative control
- Positive controls validity:
- valid
- Additional information on results:
- On the basis of the pre-experiments 750 mg/kg b.w. for the males and 400 mg/kg b.w. for the females were estimated to be suitable as highest dose levels. Gender specific differences in toxicity were observed. In accordance with the guidelines both genders were used in the main experiment.
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei: no - test item, positive control induced the appropriate response
- Ratio of PCE/NCE:
- Appropriateness of dose levels and route: yes, triggered by observed gender specific differences in toxicity
- Statistical evaluation: yes, non-parametric Mann-Whitney test
- All animals treated with the vehicle control (corn oil) did not express any clinical signs of toxicity.
Any other information on results incl. tables
Table 1: Rates of micronuclei (Males)
Test group |
Dose |
Sampling time (h) |
PCEs with micronuclei |
Range |
PCE per 2000 erythrocytes |
Vehicle control |
0 |
24 |
0.075 |
1 -3 |
1292 |
Test item |
187.5 |
24 |
0.100 |
0 -4 |
1294 |
Test item |
375 |
24 |
0.058 |
0 -2 |
1307 |
Test item |
750 |
24 |
0.092 |
0 -4 |
1276 |
Positive control |
40 |
24 |
2.075 |
29 -54 |
1255 |
Test item |
750 |
48 |
0.142 |
0 -8 |
1345 |
Table 2: Rates of micronuclei (Females)
Test group |
Dose |
Sampling time (h) |
PCEs with micronuclei |
Range |
PCE per 2000 erythrocytes |
Vehicle control |
0 |
24 |
0.108 |
1 - 4 |
1295 |
Test item |
100 |
24 |
0.083 |
0 - 3 |
1371 |
Test item |
200 |
24 |
0.175 |
1 - 7 |
1381 |
Test item |
400 |
24 |
0.092 |
0 - 4 |
1265 |
Positive control |
40 |
24 |
1.733 |
18 -52 |
1260 |
Test item |
400 |
48 |
0.092 |
1 - 3 |
1400 |
Applicant's summary and conclusion
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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