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EC number: 202-715-5 | CAS number: 98-94-2
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Density
- Particle size distribution (Granulometry)
- Vapour pressure
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- Stability: thermal, sunlight, metals
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- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
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- Endpoint summary
- Stability
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- 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
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- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
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- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
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- 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:
- supporting study
- Study period:
- December 21st, 1981 to January 20th, 1982
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: Similar to guideline, GLP. The positive control in females did not induce a significant increase in micronuclei.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 982
- Report date:
- 1982
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- 1. The proportion of micronucleated PCEs was determined for 500 PCEs / animal. OECD 474 (1983) or OECD 474 (1997) indicate 1000 or 2000 PCEs /animal, respectively. 2. The positive control in females did not induce a significant increase in micronuclei.
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Cyclohexyldimethylamine
- EC Number:
- 202-715-5
- EC Name:
- Cyclohexyldimethylamine
- Cas Number:
- 98-94-2
- Molecular formula:
- C8H17N
- IUPAC Name:
- N,N-dimethylcyclohexanamine
- Reference substance name:
- N,N-dimethylcyclohexanamine
- Cas Number:
- 98-94-2
- IUPAC Name:
- N,N-dimethylcyclohexanamine
- Reference substance name:
- N,N-dimethylcyclohexylamine
- Cas Number:
- 98-94-2
- IUPAC Name:
- N,N-dimethylcyclohexylamine
- Details on test material:
- CAS 98-94-2, N,N-dimethylcyclohexylamine, purity not
specified
- Substance type: organic
- Physical state: liquid
- Lot/batch No.: 20-133-CJ
- Other: Clear, straw coloured liquid
Constituent 1
Constituent 2
Constituent 3
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Inc.
- Age at study initiation: Adult
- Weight at study initiation: First study: 248.7 g (males) and 209.2 (females). Second study: 191.2 g (males) and 186.2 g (females)
- Assigned to test groups randomly: yes
- Housing: Animals were housed up to 4 rats per cage.
- Diet (e.g. ad libitum): Purina Laboratory Chow ad libitum
- Water (e.g. ad libitum): ad libitum
IN-LIFE DATES: From: December 21st, 1981 To: January 20th, 1982
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- Initial doses were based upon LD50 information and were 80% of the LD50 for high dose and one-half of the high dose for the low dose. High mortality at the high dose prompted a second study, using a third dose of one-fourth the high dose. The three doses employed were thus: 80% of the LDS0
or 450 mg/kg/day, 225 mg/kg/day and 112 mg/kg/day.
A subchronic dosing regimen was used. It consisted of two administrations approximately 24 hours apart. Harvest was at 48 and 72 hours after the first administration of the test article, and at 48 hours after the first administration of the control articles. Equal numbers of males and females were used at each dose/kill -time combination. The route of administration was oral gavage. - Duration of treatment / exposure:
- Two administrations at an interval of approximately 24 hours
- Frequency of treatment:
- Two treatments at a 24-hour interval
- Post exposure period:
- Not documented
Doses / concentrationsopen allclose all
- Dose / conc.:
- 225 mg/kg bw/day (nominal)
- Dose / conc.:
- 450 mg/kg bw/day (nominal)
- Dose / conc.:
- 112 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 4 per sex (2 per sex per sampling time).
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- triethylenemelamine at 0.5 mg/kg dissolved in saline
Triethylenemelamine
- Route of administration: Intraperitoneal injection
- Doses / concentrations: at 0.5 mg/kg dissolved in saline
Examinations
- Tissues and cell types examined:
- % of polychromatic erythrocytes (PCE) in 500 erythrocytes. % micronucleated PCEs in 500 PCEs.
Number of cells scored: 500 PCEs were scored per animal. - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: The test compound was initially tested at 433 mg/ml in corn oil for the low dose. Due to the high morality of the high dose animals (450 mg/kg) wherein 15 out of 16 animals died, the study was repeated with a lower dose and concurrent 48-hour negative control.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): three doses were administered: high dose 450 mg/kg bw, 225 mg/kg bw and 112 mg/kg bw. Sampling time were carried out at 48 and 72 hours after the first treatment and at 48 hours after the first administration of the control articles.
DETAILS OF SLIDE PREPARATION: Following centrifugation to pellet the tissue, the supernatant was drawn off, cells resuspended in a drop of serum, and suspension spread on slides and air-dried. The slides were then fixed in methanol, stained in May-Gruenwald solution followed by Giemsa,
and rinsed in deionized water (Schmid, 1975).
METHOD OF ANALYSIS: Based on total numbers of PCE in the optic fields. The frequency of PCEs versus mature erythrocytes (RBCs) was
determined by scoring the number of RBCs observed in the optic fields while scoring the f i r s t 200 PCEs for micronuclei. - Evaluation criteria:
- A test article is positive if two treatment groups are positive (p < 0.05). If only one treatment group is positive, the result is designated as unconfirmed positive.
- Statistics:
- Student t test and ANOVA using mean square for error (MSE)
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- not specified
- Negative controls validity:
- not specified
- Positive controls validity:
- not specified
- Additional information on results:
- TOXIC RESPONSE/EFFECTS BY DOSE LEVEL:
- Mortality and time to death: 6 at medium dose, 15 at high dose and one positive control animal were found dead during the study. Time to death not recorded.
- Clinical signs: all medium and high dose animals showed convulsions after dosing on the first day. After seizure, animals were lethargic.
EFFECT ON PCE/NCE RATIO:
%PCE at 112 and 225 mg/kg was 82 and 117, respectively (males, 48 h); 61 and 113% (males 72h).
%PCE at 112, 225 and 450 mg/kg was 62, 126 and 88, respectively (females, 48h), and 110 and 55% respectively (females, 72 h, all females of 450 mg/kg died)
GENOTOXIC EFFECTS:
Mean number of micronucleated PCE: at 48 h: at 112, 225 and 450 mg/kg: 0.65, 0.4 and 0.4 respectively (male and female)
at 72h: at 112 and 225 mg/kg: 0.28 and 0.52 respectively (male and female).
MUTANT/ABERRATION/mPCE/ POLYPLOIDY FREQUENCY: MPCE: no treatment related effects
Any other information on results incl. tables
All medium and high dose animals convulsed after dosing on first day; after seizure, animals were lethargic.
Applicant's summary and conclusion
- Conclusions:
- Although there was no increase in micronuclei in the females treated with the positive controls, DMCHA does not induce micronuclei in rat polychromatic erythrocytes and is therefore not clastogenic.
- Executive summary:
A study (Cimino, 1982) was performed to assess the ability of DMCHA to induce micronuclei in polychromatic erythrocyte from rat bone marrow.
DMCHA was administered via intraperitoneal injection to groups of 4 animals/sex/dose level. Negative and positive control cultures were also prepared. Triethylenemelanine was used as the positive control at a dose level of 0.5 mg/kg bw. A preliminary study was carried out and due to the high mortality at 450 mg/kg bw, the study was repeated with a lower dose and concurrent 48 hour negative control. A total of three doses were administered 450 mg/kg bw/day, 225 mg/kg bw/day and 112 mg/kg bw/day. Two administrations were performed at a 24 hour intervals. Harvest of the cells was performed at 48 and 72 hours after the first administration and at 48 hours after the first administration of the control articles.
The animals were sacrificed and the bone marrow was extracted for preparation. The tissue was centrifuged and the supernatant was collected, resuspended in serum and spread on slides. The slides were then fixed in methanol, stained in May-Gruenwald solution followed by Giemsa and rinse in deionised water prior to analysis for scoring.
Five hundred PCEs per animal were scored.The frequency of micronucleated cells was expressed as percent micronucleated cells based on the total PCEs present in the scored optic field. The frequency of PCEs versus mature erythrocytes (RBCs) was determined by scoring the number of RBCs observed in the optic fields while scoring the first 200 PCEs for micronuclei. The percentage micronuclei in marrow from the negative controls were 0.45% and 1.00% for males, and 0.85% and 0.65% for females, in the first and second studies respectively. The positive control compound, triethylenemelamine (TEM),induced an increase in frequency of micronuclei in males but not in females. The mean number of micronucleated PCE at 48 h were 0.65 at 112, 0.4 at 225 and 0.4 at 450 mg/kg (male and female). At 72 hours, the mean numbers of micronucleated PCE were 0.28 at 112 and and 0.52 at 225 mg/kg: (male and female).
Although there was no increase in micronuclei in the females treated with the positive controls, DMCHA does not induce micronuclei in rat polychromatic erythrocyte and is therefore not clastogenic. The negative response in the in vivo assay confirmed the negative in vitro responses in a battery of mutagenicity assays.
Based on these results, the test substance does not require classification according to Regulation EC No. 1272/2008 or Directive 67/548/EEC.
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