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EC number: 261-684-6 | CAS number: 59272-84-3
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 983
- Report date:
- 1983
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- adopted in 2016
- Deviations:
- yes
- Remarks:
- no historical controls given, immature and mature micronucleated erythrocytes counted in 400 erythrocytes/animal
- GLP compliance:
- yes
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- (carboxymethyl)dimethyl-3-[(1-oxotetradecyl)amino]propylammonium hydroxide
- EC Number:
- 261-684-6
- EC Name:
- (carboxymethyl)dimethyl-3-[(1-oxotetradecyl)amino]propylammonium hydroxide
- Cas Number:
- 59272-84-3
- Molecular formula:
- C21H42N2O3
- IUPAC Name:
- (carboxymethyl)dimethyl-3-[(1-oxotetradecyl)amino]propylammonium hydroxide
- Test material form:
- solid
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- Swiss
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Central Institute for the Breeding of Laboratory Animals, TNO, Zeist, The Netherlands
- Weight at study initiation: males: about 23 g; females: about 19 g
- Assigned to test groups randomly: yes
- Diet: ad libitum
- Water: ad libitum
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: water
- Concentration of test material in vehicle: 10%
- Amount of vehicle (if gavage or dermal): 10 mL/kg bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: The test substance was dissolved in water as a 10% solution. As the aqueous solution of W-1108 foamed rather strongly, a drop (appr. 50 mg) of an antifoam agent (Polymekor 1488, Goldschmidt, FRG) was added per 100 mL solution.
- Duration of treatment / exposure:
- not applicable
- Frequency of treatment:
- single treatment
- Post exposure period:
- 24, 48, and 72 hours
Doses / concentrations
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- mitomycin C
- Justification for choice of positive control(s): as described in OECD 474
- Route of administration: i.p.
- Doses / concentrations: 1.5 mg mitomycin C/20 mL saline/kg bw
Examinations
- Tissues and cell types examined:
- Tissue: bone marrow
Cell type: bone marrow cells - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: It is widely accepted that for a meaningful micronucleus test a very high dose should be administered to the test animals. Usually a proportion (20 - 80%) of the LD50 value is used. The LD50 value for the test substance is 1875 mg/kg bw.
DETAILS OF SLIDE PREPARATION: The femurs were dissected free, the bone marrow was flushed from the femurs into a centrifuge tube containing calf serum and the mixture was centrifuged. The excess serum was removed. The cells were then resuspended by mixing gently, a drop of the suspension was placed on a slide and spread with a haemocytometer cover glass. Five slides were prepared from each animal. The smears were air dried, fixed in methanol and stained according to May-Grünwald Giemsa.
METHOD OF ANALYSIS: The stained smears were examined by light microscopy to determine the incidence of micronucleated poly- and normochromatic erythrocytes and the ratio of polychromatic and normochromatic erythrocytes. The incidence of micronucleated poly- and normochromatic erythrocytes was determined in a total of 1000 erythrocytes per animal (200 erythrocytes per slide).
The counting procedure followed in the positive control animals was slightly different. Generally the determination of the incidence of micronucleated erythrocytes per 1000 erythrocytes was restricted to four animals (two males and two females) at each sacrifice time: 24 h, 48 h, 72 h. In the remaining animals the incidence of micronucleated cells was recorded per 400 erythrocytes.
For all animals (solvent control, positive control and test animals) the ratio of poly- and normochromatic erythrocytes was determined by counting the number of poly- and normochromatic erythrocytes in a total of 400 erythrocytes per animal. - Evaluation criteria:
- not specified
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- Toxicity: Two males treated with the test substance showed a rough coat on the first day after treatment and one female showed signs of slight diarrhoea.
Body weight was significantly reduced on Day 1 in males and females.
Any other information on results incl. tables
Table 1: results
Group |
Number of animals |
Dose [mg/kg bw] |
% PCEs (= PCE x 100 / (PCE + NCE) at sampling time |
Total micronuclei per 1000 erythrocytes at sampling time (range) |
||||
|
|
|
24h |
48h |
72 h |
24h |
48h |
72 h |
Vehicle control (water) |
5 males |
0 |
51 |
44 |
62 |
2.4 (1-5) |
2.6 (1-5) |
1.8 (0-4) |
5 females |
0 |
56 |
54 |
49 |
1.4 (0-5) |
1 (0-2) |
0.8 (0-2) |
|
Positive control |
5 males |
1.5 |
50 |
27 |
36 |
29 (17-40) |
28 (18-44) |
19 (13-24) |
5 females |
1.5 |
57 |
27 |
29 |
30 (18-43) |
11 (3-20) |
9 (3-13) |
|
Test substance |
5 males |
1000 |
42 |
33 |
58 |
2.4 (1-4) |
2 (1-4) |
1.2 (0-3) |
5 females |
1000 |
53 |
42 |
54 |
0.6 (0-2) |
2.6 (0-5) |
1.2 (0-3) |
|
PCE = polychromatic erythrocytes NCE = normochromatic erythrocytes |
Applicant's summary and conclusion
- Conclusions:
- The results of the present micronucleus test did not provide any evidence of chromosomal damage and/or damage to the mitotic apparatus caused by oral administration of high doses of the test substance.
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