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EC number: 264-261-4 | CAS number: 63469-23-8
- 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
- Study period:
- 2011-10-11 to 2011-11-24
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well documented GLP study performed according to OECD Guideline 474 without deviations.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 011
- Report date:
- 2011
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 1,1'-[[3-(dimethylamino)propyl]imino]bispropan-2-ol
- EC Number:
- 264-261-4
- EC Name:
- 1,1'-[[3-(dimethylamino)propyl]imino]bispropan-2-ol
- Cas Number:
- 63469-23-8
- Molecular formula:
- C11H26N2O2
- IUPAC Name:
- 1-{[3-(dimethylamino)propyl](2-hydroxypropyl)amino}propan-2-ol
- Test material form:
- liquid
- Details on test material:
- Details described in study specific records
Constituent 1
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): Jeffcat DPA
- Substance type: Light yellow liquid
- Physical state: Liquid
- Analytical purity: 100%
- Composition of test material, percentage of components: 0.24 wt % water, total amine: 8.8 meq/g
- Lot/batch No.: 0H519
- Stability under test conditions: no data
- Storage condition of test material: The substance is stored at ambient (15 to 30°C) in the dark without desiccant.
- Other: synonym: 2-propanol, 1, 1'-((3-(dimethylamino)propyl)imino)bis- ; CAS# 63469-23-8
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan, Frederick, MD
- Age at study initiation: 7 weeks old
- Weight at study initiation: range:
dose range finding study: males: 31.1 - 34.0 grams, females: 26.3 - 28.1 grams
definitive micronucleus study: males: 29.9 - 34.0 grams, females: 23.9 - 29.9 grams
- Assigned to test groups randomly: yes, in each study, mice were assigned to the appropriate number of treatment groups using a randomization procedure based on equalization of group mean body weights. At the time of randomization, the weight variation of animals did not exceed ± 20% from their group mean.
- Fasting period before study: no
- Housing: Animals were housed in an AAALAC-accredited facility with a controlled environment
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): ± 22°C
- Humidity (%): 50 ± 20%
- Air changes (per hr): The animal rooms were supplied with at least 10 changes of fresh HEPA-filtered air every hour.
- Photoperiod (hrs dark / hrs light): 12 hours light/dark cycle
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: Purified water
- Details on exposure:
- All dose formulations were administered at a dose volume of 20 mL/kg by a single oral administration using appropriate size disposable polypropylene syringes with gastric intubation tubes (needles). The oral route of administration has been routinely used, and is widely-accepted for use in the mammalian bone marrow erythrocyte micronucleus assay.
- Duration of treatment / exposure:
- One single dose
- Frequency of treatment:
- Once
- Post exposure period:
- Dose range finding study: mice were observed after dose administration and daily thereafter for 3 days for clinical signs of toxicity. Body weights were recorded before dose administration on Study Day 0 and on study Days 1 and 3. Following the last observation on Study Day 3, animals were euthanized by exposure to CO2 verified by toe pinch reflex and discarded without further examination.
Definitive micronucleus study: mice were observed after dose administration and throughout the course of the study for clinical signs of toxicity, which were recorded. Bone marrow was collected 24 hours post-dose (all groups) and 48 hours post-dose (vehicle control and high dose group).
Doses / concentrationsopen allclose all
- Dose / conc.:
- 500 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- Dose / conc.:
- 2 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- Dose range finding study: 5 (2000 mg/kg)
Definitive study: 10 (vehicle control), 5 (500 and 1000 mg/kg), 15 (2000 mg/kg), 5 (positive control) - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - cyclophosphamide monohydrate
- Route of administration: oral: gavage
- Doses / concentrations: 50 mg/kg
Examinations
- Tissues and cell types examined:
- Immediately following euthanasia, the femurs were exposed, cut just above the knee, and the bone marrow was aspirated into a syringe containing fetal bovine serum. The bone marrow cells were transferred to a labeled centrifuge tube containing aprpoximately 1 mL fetal bovine serum. The bone marrow cells were pelleted by centrifugation at approximately 100 x g for five minutes and the supernatant was drawn off, leaving a small amount of serum with the remaining cell pellet. The cells were re-suspended and a small drop of bone marrow suspension was spread onto a clean glass slide. Two slides were prepared from each mouse. The slides were air dried and fixed in methanol. One set of slides was stained with a nucleid acid-specific stain, acridine orange, and was used in microscopic evaluation.
- Details of tissue and slide preparation:
- To control for bias, bone marrow slides were coded using a random number table by an individual not involved with the scoring process. Using a fluorescent microscope and medium magnification, an area of acceptable quality was selected such that the cells were well spread and stained. using oil immersion (1000 X), the following cell populations and cellular components were evaluated and enumerated:
- polychromatic erythrocytes (PCEs; 2000 PCEs per animal were scored)
- normochromatic erythrocytes (NCEs; number of NCEs and micronucleated NCEs determined by scoring 1000 total erythrocytes per animal)
- micronuclei
The proportion of polychromatic erythrocytes to total erythrocytes were also determined per total of 1000 erythrocytes (PCEs/ECs ratio) for each animal. - Evaluation criteria:
- The incidence of micronucleated polychromatic erythrocytes per 2000 PCEs for each mouse and per 10000 PCEs for each treatment group was determined.
- Statistics:
- Statistical significance was determined using the Kastenbaum-Bowman tables which are based on the binomial distribution (Kastenbaum and Bowman, 1970). All analyses were performed separately for each sex and sampling time. In order to quantify the proliferation state of the bone marrow as an indicator of bone marrow toxicity, the proportion of polychromatic erythrocytes to total erythrocytes was determined for each mouse and treatment group (PCEs/ECs ratio). The proportion of polychromatic erythrocytes to total erythrocytes in test substance animals should not be less than 20% of the control value. The test substance was judged negative if no statistically significant increase in the incidence of micronucleated polychromatic erythrocytes in the test substance groupos relative to the concurrent negative (vehicle) groups is obersved. The test substance would have been considered to induce a positive response if the incidence of micronucleated polychromatic erythrocytes at one or more doses is statistically elevated relative to the vehicle control (p< = 0.05, binomial distribution, Kastenbaum-Bowman Tables).
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Remarks:
- apart from piloerection in all animals.
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
No mortality was observed. Piloerection was seen at a dose of 2000 mg/kg, in all males following dose administration and on Study Day 1, and in 3/5 females on Study Day 1. No appreciable changes in the group mean body weights were seen.
RESULTS OF DEFINITIVE STUDY
No mortality was observed in any of the treatment groups. All mice in the control substance (vehicle or positive) groups and all female mice in the 500 and 1000 mg/kg treatment groups appeared normal during the study period. Piloerection was seen in all male mice at 500, 1000 and 2000 mg/kg. This clinical sign persisted in the male mice at 2000 mg/kg at 24 hours post dose.
No appreciable reductions in the ratio of polychromatic erythrocytes to total erythrocytes in the test substance groups relative to the respective vehicle control groups were observed, suggesting that the test substance did not inhibit erythropoiesis.
No statistically significant increase in the incidence of micronucleated polychromatic erythrocytes in test substance groups relative to the respective vehicle control groups was observed in male or female mice at 24 or 48 hours after dose administration (p > 0.05, binomial distribution, Kastenbaum-Bowman Tables).
CP, the positive control, induced a statistically significant increase in the incidence of micronucleated PCEs (p≤ 0.05, binomial distribution, Kastenbaum-Bowman Tables) in both male and female mice. The number of micronucleated PCEs in the vehicle control groups did not exceed the historical vehicle control range. Based upon this, all criteria for a valid test were met as specified in the protocol.
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of the study conduct, a single oral administration of the test substance at doses up to and including 2000 mg/kg did not induce a significant increase in the incidence of micronucleated polychromatic erythrocytes in bone marrow. Therefore, the test substance was concluded to be negative in the micronucleus test using male or female ICR mice.
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