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Diss Factsheets
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EC number: 241-629-2 | CAS number: 17647-86-8
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP and guideline compliant study report
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2016
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reporduction / Developmental Toxicity Screening Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Potassium N,N-dimethylglycinate
- EC Number:
- 241-629-2
- EC Name:
- Potassium N,N-dimethylglycinate
- Cas Number:
- 17647-86-8
- Molecular formula:
- C4H8NO2.K
- IUPAC Name:
- potassium 2-(dimethylamino)acetate
- Details on test material:
- - Name of test material (as cited in study report): Potassium N,N-dimethylglycinate
- Physical state: solid, white
- Analytical purity: 99.76 area-% (HPLC) minus water content and potassium hydroxide = 94.2 g/100 g (1H-NMR)
- Lot/batch No.: 212922-3
- Expiration date of the batch: 04 Sep 2016
- Storage condition of test material: at room temperature, highly hygroscopic
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Research Models and Services, Germany GmbH
- Age at study initiation: about 11-12 weeks (males and females)
- Housing: individually in polycarbonate cages type III
- Diet (e.g. ad libitum): ad libitum, ground Kliba maintenance diet mouse-rat “GLP”, meal, supplied by Provimi Kliba SA, Kaiseraugst, Switzerland
- Water (e.g. ad libitum): ad libitum, deionized water
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24°C
- Humidity (%): 30 - 70%
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: drinking water
- Vehicle:
- water
- Details on mating procedure:
- In general, each of the male and female animals was mated overnight in a 1:1 ratio for a maximum of 2 weeks. Throughout the mating period, each female animal was paired with a predetermined male animal from the same test group. The animals were paired by placing the female in the cage of the male mating partner from about 16.00 h until 06.30 - 09.00 h of the following morning. Deviations from the specified times were possible on weekends and public holidays and were reported in the raw data. A vaginal smear was prepared after each mating and examined for the presence of sperm. If sperm was detected, pairing of the animals was discontinued. The day on which sperm was detected was denoted gestation day (GD) 0 and the following day "GD 1".
- Duration of treatment / exposure:
- males: 29 days
females: 53 days - Frequency of treatment:
- daily
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
1500, 4000, 12000 ppm
Basis:
nominal in water
- Remarks:
- Doses / Concentrations:
1592, 4246, 12739 ppm
Basis:
other: content of the test substance (94.2 g/100 g)
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent no treatment
Examinations
- Maternal examinations:
- WATER CONSUMPTION
During pre-mating water consumption was significantly decreased between study day 0 and 3 in male animals of test group 3 (12000 ppm, -47.2%) and in female animals of the same test group 3 between study day 0 and 3 (-29.9%) as well as between study day 10 and 13 (-29.3%). Whereas no effect can be seen in both sexes after the first two weeks of administration, it can be concluded, that the reason for this finding was assessed to be caused by the taste of the test item in the highest concentration, which the animals get accustomed to. So these findings were considered as treatment related, but not adverse. During gestation and lactation no significant findings were observed.
FOOD CONSUMPTION
Food consumption was significantly decreased (-23.7%) in male animals of test group 3 (12000 ppm) during pre-mating between study day 0 and 7. No further effects were seen in food consumption. This finding was considered as treatment-related, but based on the degree of change as well as on its transient character it was assessed as not adverse.
BODY WEIGHT DATA
Male animals of test group 3 (12000 ppm) showed a slight significant lower body weight on pre-mating days 7 (-6.0%) and 13 (-5.0%). The body weight change in male animals of test group 3 (12000 ppm) was decreased (-90.4%) during pre-mating between day 0 and 7. The overall value for pre-mating body weight change was decreased significantly (-42.3%). No further alterations of the body weight were observed after the first two weeks of administration in males. These findings were considered as treatment-related, but based on the degree of change as well as on its transient character they were assessed as not adverse. Body weights and body weight changes were not significantly affected in female animals during pre-mating, mating, post-mating and gestation. - Fetal examinations:
- Pup number and status at delivery
The mean number of delivered F1 pups per dam was evenly distributed about test groups 0 - 3. The respective values reflect the normal range of biological variation inherent in the strain used in this study. Each one stillborn pup was found in the litter of dams Nos. 133 and 138 of test group 3 (12000 ppm). This incidence were within the normal range of the historical control data.
Pup viability/ mortality
The viability index indicating pup mortality during lactation (PND 0 - 4) was 100.0% (test groups 1 and 3) and 99.0% (test groups 0 and 2) based on 1 pup of the control group (0 ppm) was found dead and one pup of test group 2 (4000 ppm) was missing (cannibalized). These findings reflected the normal range of biological variation inherent in the strain of rats used for this study as all respective values were within the range of the historical control data.
Sex ratio
The sex distribution and sex ratios of live F1 pups on the day of birth and PND 4 did not show substantial differences between the control and the test substance-treated groups; slight differences were regarded to be spontaneous in nature.
Pup clinical observations
The surviving F1 pups of any test group did not show adverse clinical signs up to scheduled sacrifice on PND 4. However, in test group 2 (4000 ppm) one female pups could be assessed only until PND 1 because it was missed (cannibalized) on PND 2 and in test group 3 (12000 ppm) one male and one female pup from different litters could not be assessed because they were stillborn on PND 0.
Pup body weight data
Mean pup body weights/pup body weight changes of all pups in all test groups were comparable to the control group. One female runt was seen in test group 0 (0 ppm) and two female runts were seen in test group 2 (4000 ppm). These values were within the range of the biological variation inherent in the strain of rats used for this study.
Pup necropsy observations
One male pup of test group 3 (12000 ppm) and one female pup of control group (0 ppm) showed post mortem autolysis. Furthermore, in test group 2 (4000 ppm) one female pup could not be assessed because it was missing (cannibalized). These findings were assessed as being spontaneous in nature and thereby not related to treatment. No other findings were seen in any pup of any test group. - Statistics:
- Kruskal-Wallis Test; Wilcoxon-Test
Results and discussion
Results: maternal animals
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 731 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- NOAEL
- Effect level:
- 960 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- NOAEL
- Effect level:
- 12 000 ppm
- Based on:
- test mat.
- Basis for effect level:
- other: developmental toxicity
Results (fetuses)
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of this Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test, the oral administration via drinking water of Potassium N,N-dimethylglycinate to Wistar rats revealed no signs of general systemic toxicity in male and female parental animals up to a concentration of 12000 ppm (731 mg/kg bw/d in males and 960 mg/kg bw/d in females).
Thus, the no observed adverse effect level (NOAEL) for general systemic toxicity was 12000 ppm in male and in female parental animals (731 mg/kg bw/d in males and 960 mg/kg bw/d in females).
The no observed adverse effect level (NOAEL) for reproductive performance and fertility was 12000 ppm (731 mg/kg bw/d) in male and 12000 ppm (960 mg/kg bw/d) in female Wistar rats. The NOAEL for developmental toxicity in the F1 progeny was 12000 ppm.
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