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EC number: 202-845-2 | CAS number: 100-37-8
- 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
- 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 according to GLP
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Qualifier:
- according to guideline
- Guideline:
- other: US EPA Guidelines from 1985
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 2-diethylaminoethanol
- EC Number:
- 202-845-2
- EC Name:
- 2-diethylaminoethanol
- Cas Number:
- 100-37-8
- Molecular formula:
- C6H15NO
- IUPAC Name:
- 2-(diethylamino)ethanol
- Details on test material:
- - Name of test material (as cited in study report): diethylaminoethanol
- Analytical purity: > 99%
- Lot/batch No.: G-9-A
- Physical state: clear colourless liquid
- Storage condition of test material: ambient temperature in the dark
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Olac Limited, England
- Age at study initiation: 4-5 week old mice
- Weight at study initiation: 17.7 - 27.8 g
- Diet: Laboratory animal diet LAD 1 (Biosure, Manea, Cambridgeshire, England), ad libitum
- Water: Drinking water was supplied to each cage via a polythene bottle and sipper-tube
- Acclimation period: at least four days prior to treatment
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21 ± 2 °C
- Humidity (%): 55 ± %
- Air changes (per hr): 15
- Photoperiod 12 hrs dark / 12 hrs light
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- 0.9 % saline
- Details on exposure:
- Dosing volume: 10 mL/kg
Sampling times: 24 hr (all groups), 48 hr (control + high dose) and 72 hr (control + high dose). - Duration of treatment / exposure:
- single oral dose
- Frequency of treatment:
- only one application
- Post exposure period:
- 24 hr (20 and 100 mg/kg bw dose)
72 hr (control + high dose)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
20, 100 and 500 mg/kg bw
Basis:
actual ingested
- No. of animals per sex per dose:
- five/sex/dose/sampling time
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- chlorambucil, 30 mg/kg bw in 10% aqueous ethanol
Examinations
- Tissues and cell types examined:
- Animals were inspected daily throughout the acclimatisation period and the dosing period for signs of ill-health or reaction to treatment. Any deviation from normal was recorded. All animals were weighed on the day of treatment and again immediately before termination, and bodyweights were recorded. In addition, the animals in the preliminary toxicity test were weighed immediately prior to dosing and daily thereafter until termination.
The frequency of micronucleated cells per at least 1000 polychromatic erythrocytes, as well as the frequency of micronucleated cells per at least 1000 mature erythrocytes was determined. The ratio of polychromatic to mature cells was also determined. - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
The doses were chosen based on a preliminary toxicity test using 2 animals/sex/group treated with 312.5, 625, 1250 and 2500 mg/kg bw.
DETAILS OF SLIDE PREPARATION:
Animals were killed by cervical dislocation following carbon dioxide inhalation. Femurs from each animal were rapidly dissected out and cleaned of adherent tissu . The epiphyses were cut off to obtain access to the marrow canal. Marrow cells were flushed out with 2.5 ml foetal calf serum using a syringe and needle. The recovered cells were centrifuged at 1000 rpm for five minutes . The bulk of the supernatant fluid was discarded and the cell pellet resuspended in the remaining fluid. Single drops of the cell suspension were transferred to clean, dry slides, two or three smears (for the preliminary toxicity test or main micronucleus test respectively) prepared, and the slides left to air-dry. Following fixation in methanol for ten minutes, they were stained manually, using the Schmid (May-Grunwald and Giemsa) staining technique.
- Statistics:
- Mann-Whitney U-test.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- at 100 mg/kg bw 1 male had hunched posture and piloerection. At 500 mg/kg bw, signs of toxicity were more pronounced and 1 male needed to be killed in extremis 42 hrs post-dosing.
- Vehicle controls validity:
- valid
- Negative controls validity:
- not specified
- Positive controls validity:
- valid
- Additional information on results:
- TOXICITY
No adverse reactions to treatment were recorded for any animal exposed to diethylaminoethanol at 20 mg/kg bw. However, one male mouse dosed at 100 mg/kg bw showed signs including hunched posture and piloerection. One male mouse treated at 500 mg/kg bw was killed in extremis approximately 42 hours after dosing; signs included rales, piloerection, hunched posture and swollen abdomen. Sixteen of the remaining animals dosed at this level showed adverse reactions to treatment intermittently after dosing including rales (13 mice), piloerection (11), hunched posture (10) and irregular respiration (1).
EFFECT ON PCE/NCE RATIO PCE/NCE ratio (males and females combined):
at 24 hours: 0.9 (all doses); 0.8 (saline control);
at 48 hours: 0.9 (500 mg/kg bw ); 0.9 (saline control);
at 72 hours: 0.7 (500 mg/kg bw ); 0.7 (saline control);
GENOTOXIC EFFECTS
Mean number of micronucleated PCE/1000 PCE (males and females combined):
- 0.9 % saline control: 1.2, 0.6 and 0.6 at 24, 48 and 72 hours, respectively;
- 20 mg/kg bw: 0.8 at 24 hours;
- 100 mg/kg bw: 0.7 at 24 hours;
- 500 mg/kg bw: 0.6, 0.8 and 0.3 at 24, 48 and 72 hours, respectively.
STATISTICAL RESULTS
Frequencies of micronucleated polychromatic erythrocytes were not significantly different from controls at any dose or sampling time.
PRELIMINARY STUDY
The PCE/NCE ratio in the preliminary study was 0.9, 0.8 and 0.5 in the 312.5 mg/kg bw , 625 mg/kg bw and 1250 mg/kg bw dose groups, respectively. This indicated that the test substance reached the bone marrow.
POSITIVE CONTROL
Positive controls gave the expected response.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
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