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EC number: 273-224-1 | CAS number: 68953-70-8 The complex combination of alkanolamines from the distillation of reaction products of ammonia and oxirane. It consists predominantly of triethanolamine, diethanolamine and higher amines from the reaction of triethanolamine and oxirane.
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to a guideline study
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Evaluation of the developmental toxicity of dermally applied monoethanolamine in rats and rabbits
- Author:
- Liberacki AB, et al.
- Year:
- 1 996
- Bibliographic source:
- Fundamental and Applied Toxicology 31, 117-123
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Principles of method if other than guideline:
- Pregnant Sprague-Dawley rats were exposed dermally to 0, 10, 25, 75 and 225 mg/kg/day of monoethanolamine (MEA) for approximately 6 hr/day on Days 6 through 15 of gestation .
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- 2-aminoethanol
- EC Number:
- 205-483-3
- EC Name:
- 2-aminoethanol
- Cas Number:
- 141-43-5
- Molecular formula:
- C2H7NO
- IUPAC Name:
- 2-aminoethanol
- Details on test material:
- - Analytical purity: 100 % pure as analyzed by Analysis by gas chromotography using flame ionization detection
- supplier: The Dow Chemical Company
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Inc. (Kingston, NY), USA
- Age at study initiation:
- Weight at study initiation: 250-300 g)
- Housing: in wire-bottom cages
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: 2 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22
- Humidity (%): 40-60
Administration / exposure
- Route of administration:
- dermal
- Vehicle:
- water
- Details on exposure:
- TEST SITE
- Area of exposure: shaved skin of the back
- Type of wrap if used: absorbant gauze pad followed by nonabsorbant cotton; an elastic bandage was wrapped securely around the animal to hold the patch in place and to prevent accidental ingestion of the test material via grooming during the exposure.
REMOVAL OF TEST SUBSTANCE
- Washing (if done): water-dampened towel was used to wipe remaining test material off
- Time after start of exposure: 6 hours
TEST MATERIAL
- Amount(s) applied (volume or weight with unit): 1 ml/kg
- Constant volume or concentration used: no - Details on mating procedure:
- - Impregnation procedure: [cohoused]
- If cohoused:
- M/F ratio per cage: 1/1
- Length of cohabitation: over night
- Verification of same strain and source of both sexes: [yes]
- Proof of pregnancy: [sperm in vaginal smear] referred to as [day 0] of pregnancy - Duration of treatment / exposure:
- day 6 - 15 of gestation
- Frequency of treatment:
- 6 hours/day, daily
- Duration of test:
- up to day 21 of gestation
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 10, 25, 75, 225 mg/kg bodyweight
Basis:
nominal conc.
- No. of animals per sex per dose:
- 30-45 rats
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Dose levels selected for these studies were chosen based upon the results of dermal range-finding and teratology probe studies conducted in rats
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: daily
BODY WEIGHT: Yes
- Time schedule for examinations: gestation days 0, 3, 6-16, and 21
FOOD CONSUMPTION: Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
WATER CONSUMPTION: Yes
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 21
- Organs examined: weights of liver, kidneys
- Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes
- Other: Uteri with no visible implantations were stained with a 10% sulfide solution. - Fetal examinations:
- - External examinations: Yes: [all per litter]
- Soft tissue examinations: Yes: [half per litter]
- Skeletal examinations: Yes: [half per litter]
- Head examinations: Yes: [half per litter ]
All fetuses were weighed and examined for evidence of external alterations and palate closure. At least one-half of the rat fetuses in each litter were examined for visceral alterations (Staples,1974). The sex of all live fetuses was determined. The heads of rat fetuses not selected for skeletal examination were removed, placed in Bouin's solution, and subsequently sectioned and examined for craniofacial defects (Wilson, 1965; Van Julsingha and Bennet, 1977). All fetuses were eviscerated and stained with alizarin red-S ( Dawson, 1926; Crary, 1962). Skeletal examinations were conducted only on the rat fetuses not selected for Bouin's examination. - Statistics:
- Continuous data were evaluated for homogeneity of variance using Bartlett's test (Winer, 1971). Based upon the outcome of these tests, a parametric or nonparametric analysis of variance (ANOVA) was performed. If the ANOVA was significant, analysis by Dunnett's test (Steel and Torrie, 1960), the Wilcoxen Rank-Sum test with Bonferroni's correction (Miller, 1966), or a pooled t test was performed as appropriate. The level of statistical significance was set a priori at a = 0.05. Nonparaznetric data were statistically treated using the Kruskal-Wallis test followed by the Mann-Whitney U test (Sokal and Rohlf, 1969), when appropriate. Incidence data for rats were analyzed using the Wilcoxon test as modified by Haseman and Hoel (1974). Fetal sex ratios were analyzed using a binomial distribution test (Steel and Torrie, 1960).
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
Rats administered 225 mg MEA/kg/day exhibited a treatment-related increased incidence of skin irritation at the site of exposure. In general, the dermal irritation followed a progression, beginning with erythema and leading to necrosis, scabs, and scar formation.
No significant dermal irritation or lesions were observed among rats administered lower doses of MEA.
There were no postmortem treatment-related effects observed in any dose group. No significant differences were observed in the feed or water consumption of MEA exposed rats relative to controls.
The body weight gain of rats given 225 mg MEA/kg/day was significantly decreased during the exposure period. No effect on weight gain was observed in dams treated with lower levels of MEA.No effects on liver or kidney weights were observed at any dose level.
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 75 mg/kg bw/day
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
Despite maternal effects observed among dams given 225 mg/kg/day, reproductive parameters among MEA exposed rats were unaffected at this or lower dose levels. There were no differences in pregnancy rate, number of corpora lutea, number of implantations, resorptions, litter size, number of dead fetuses, fetal sex ratio, fetal body weight, or gravid uterine weight among any of the dose groups when compared to controls.
There were no treatment-related increases in the incidence of variations or malformations observed externally, viscerally or at skeletal examination by individual category, or in total variations or malformations when compared to controls. Among controls, the following types of malformations were observed: microphthalmia, retroesophageal right subclavian artery, and an extra cervical rib. No malformed fetuses were observed in the 10 mg/kg/day dose group. Malformations observed in the 25 mg MEA/kg/day dose group included retroesophageal right subclavian artery and an extra cervical rib. A single fetus was malformed in the 75 mg MEA/kg/day dose group. This fetus had multiple craniofacial
malformations consisting of micrognathia, cleft lip and soft palate, and aglossia. No malformations were observed in fetuses from dams administered 225 mg MEA/kg/day.
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 225 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: developmental toxicity
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
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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