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Diss Factsheets
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EC number: 203-782-3 | CAS number: 110-60-1
- 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:
- weight of evidence
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: very well documented publication
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 987
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Following literature references on teratology research
- GLP compliance:
- yes
Test material
- Reference substance name:
- Ethylenediammonium dichloride
- EC Number:
- 206-369-6
- EC Name:
- Ethylenediammonium dichloride
- Cas Number:
- 333-18-6
- IUPAC Name:
- ethane-1,2-diaminium dichloride
- Details on test material:
- Ethylenediamine dihydrochloride: Approximately 80 kg of EDA • 2HCI were received from Union Carbide Corp. (UCC South Charleston, WV). The sample was prepared from UCC's high-punty-grade ethylenediamine and ACS reagent grade concentrated aqueous HO obtained from Allied Chemical Corp. The synthesis was carried out at approximately 85°C in a 100-gallon glass-lined autoclave at a large-scale pilot plant in South Charleston, West Virginia. Following cooling and crystallization, EDA-2HC1 was recovered by centrifugation and washed with methanol to remove impurities. The yield of EDA • 2HC1 in this process was approximately 45%. The high-purity EDA used in the synthesis was 99.9% pure. On the basis of various analyses (elemental, water, infrared spectroscopy, emission spectrography, and high-pressure liquid chromatography (HPLC). the dihydrochloride was also
shown to be free from impurities.
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Details on test animals or test system and environmental conditions:
- 182 male and 192 female Fischer 344 rats, approximately 58 days of age, were received from Charles River Breeding Laboratories, Inc. (Kingston, NY).
Animals were housed in stainless-steel cages with food and water available ad libitum. Ground diet was supplied in 12-oz opal glass jars, and water was provided by an automatic dispensing system with demand-controlled valves in each cage.
Administration / exposure
- Route of administration:
- oral: feed
- Details on exposure:
- Ethylenediamine dihydrochloride (EDA-2HC1) was fed to groups of 20 (40 controls) timed-pregnant rats on Gestation Days 6 through 15 at 1.0,
0.25,0.05, or 0 g/kg/day. The day of discovery of a vaginal plug was considered gestation day 0.
On Gestation Day 21, the fetuses were delivered by cesarean section, and the standard endpoints for teratogenicity were evaluated.
Ethylenediamine dihydrochloride was added to the diet at concentrations based on established diet consumption data and an established growth curve for pregnant female Fischer 344 rats to produce dosage goals of 1.00, 0.25 and 0.05 g/kg/day. These dosages were selected based on the results of a 90-day study in which the same three dose levels had been used. - Frequency of treatment:
- Ethylenediamine dihydrochloride (EDA-2HC1) was fed to groups of 20 (40 controls) timed-pregnant rats on Gestation Days 6 through 15 at 1.0,
0.25,0.05, or 0 g/kg/day. The day of discovery of a vaginal plug was considered gestation day 0.
On Gestation Day 21, the fetuses were delivered by cesarean section, and the standard endpoints for teratogenicity were evaluated.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
100, 250, 50 and 0 mg/kg/day
Basis:
nominal in diet
- No. of animals per sex per dose:
- 182 male and 192 female Fischer 344 rats, approximately 58 days of age, were received from Charles River Breeding Laboratories,
Inc. (Kingston, NY).
Examinations
- Statistics:
- The unit of statistical comparison was the pregnant female. Results of the quantitative continuous variables (e.g., maternal body weight gain and
liver weights) were compared using the following tests: Bartlett's test for homogeneity of variance (Sokal and Rohlf, 1981), analysis of variance and Duncan's multiple range test (Snedecor and Cochran, 1967). Whenever the F value for the analysis of variance was significant, the Duncan's multiple range test was used to denote which groups differed significantly from the control group. Where Bartlett's test indicated heterogeneous variances and for other nonparametric data, the Kruskal-Wallis test (Sokal and Rohlf, 1981) followed by individual Mann-Whitney U tests (Sokal and Rohlf, 1981) were used. Frequency data were compared by Fisher's exact test (Sokal and Rohlf, 1981). Fetal weights and lengths were compared using a nested analysis of variance (Sokal and Rohlf, 1981) and the method of Weil (1970).
Results and discussion
Results: maternal animals
Effect levels (maternal animals)
- Dose descriptor:
- NOAEL
- Effect level:
- ca. 250 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- NOAEL= 250 mg/kg /day during gestation (effect: maternal toxicity)
- Executive summary:
There was no evidence of teratogenicity in Fischer 344 rats from EDA-2HC1 ingestion during organogenesis.
The dose of 1000 mg/kg/day during gestation resulted in maternal toxicity, leading to reduced fetal weight, crown-rung length and increased litter resorption.
NOAEL = 250 mg/kg/day
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