Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 250-151-3 | CAS number: 30364-51-3
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 17 Sep 2012 - 08 Mar 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- The Department of Health of the Government of the United Kingdom
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: Water samples were taken from the control and each test group (replicates R1 – R4 pooled) at 0 and 48 h for quantitative analysis. Duplicate samples were taken and stored at approximately -20 °C for further analysis if necessary. Samples at the No Observed Effect Concentration and above only were analyzed.
- Sample storage conditions before analysis: The samples were stored at approximately -20 °C prior to analysis. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: An amount of test item (1100 mg) was dispersed in 11 liters of reconstituted water with the aid of a propeller stirrer at a rate of approximately 1500 rpm for a period of 24 hours. After stirring, any undissolved test item was removed via filtration using a 0.2 µm Gelman Acrocap filter (initial approximate 100 mL discarded to pre-condition the filter) to give the 100% v/v saturated solution test concentration. Aliquots (20, 64, 200 and 640 mL) of the 100% v/v saturated solution test concentration were each separately added to a final volume of 2 liters of reconstituted water to give further test concentrations of 1.0, 3.2, 10 and 32% v/v saturated solution. Each prepared concentration was inverted several times to ensure adequate mixing and homogeneity.
- Eluate: no
- Differential loading: no
- Controls: yes, test medium control - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Source: in-house laboratory culture
- Age at study initiation (mean and range, SD): < 24 h
- Method of breeding: Adult Daphnia were maintained in 150 mL glass beakers containing Elendt M7 medium in a temperature controlled room at approximately 20 °C. The lighting cycle was controlled to give a 16 hours light and 8 hours darkness cycle with 20 minute dawn and dusk transition periods. Each culture was fed daily with a mixture of algal suspension (Desmodesmus subspicatus) and Tetramin® flake food suspension. Culture conditions ensured that reproduction was by parthenogenesis. Gravid adults were isolated the day before initiation of the test, such that the young daphnids produced overnight were less than 24 hours old. These young were removed from the cultures and used for testing. The diet and diluent water are considered not to contain any contaminant that would affect the integrity or outcome of the study.
- Feeding during test: no - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Test temperature:
- 20 - 21 °C
- pH:
- 8.1 - 8.5
- Dissolved oxygen:
- > 90% air saturation
- Nominal and measured concentrations:
- nominal: control, 1, 3.2, 10, 32, 100% v/v saturated solution
measured: control: < LOQ; 32% v/v: 1.92 mg/L (0 h) and 1.44 mg/L (48 h); 100% v/v: 5.43 mg/L (0 h) and 4.78 mg/L (48 h) - Details on test conditions:
- TEST SYSTEM
Test vessel
- Type (delete if not applicable): covered to reduce evaporation
- Material, size, headspace, fill volume: glass; size: 250 mL; headspace: 0 mL; fill volume: approximately 250 mL
- Aeration: no
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Photoperiod: 16 h light and 8 h dark
- Light intensity: 509 to 515 lux
EFFECT PARAMETERS MEASURED: Any immobilization or adverse reactions to exposure were recorded at 24 and 48 hours after the start of exposure.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 3.2
- Range finding study
- Test concentrations: 0.1, 1, 10, 100% v/v saturated solution
- Results used to determine the conditions for the definitive study: No immobilization was observed at the test concentrations of 0.10 and 1.0% v/v saturated solution. However, immobilization was observed at 10 and 100% v/v saturated solution. Chemical analysis of the freshly prepared media at 0 hours for the 1.0, 10 and 100% v/v saturated solution test concentrations showed measured concentrations of 0.077, 0.56 and 5.7 mg/L respectively. Analysis of the old media at 48 hours for the 1.0, 10 and 100% v/v saturated solution test concentrations showed measured concentrations of 0.0072, 0.41 and 6.3 mg/L respectively. Whilst a slight decline in measured concentration was observed for the 1.0% v/v saturated solution, this was not thought to affect the validity of the result as the No Observed Effect Concentration for the definitive test was above this concentration. However, the measured concentrations for the 10 and 100% v/v saturated solution test concentrations indicated that the test item was stable under test conditions. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1.7 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other:
- Duration:
- 48 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 5.1 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 2.9 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% Confidence limits: 1.7 - 5.1 mg/L
- Details on results:
- - Mortality of control: 0%
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: The test preparations were observed to be clear colorless solutions for the duration of the test. - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- EC50/LC50: EC50 (48 h): 0.45 mg/L (95% CL: 0.42 - 0.48 mg/L) - Validity criteria fulfilled:
- yes
Reference
Table 1: Cumulative Immobilization data in the definitive test
Nominal concentration [% v/v saturated solution] |
Cumulative Immobilized Daphnia (Initial Population: 5 per replicate) |
|||||||||||
24 h |
48 h |
|||||||||||
R1 |
R2 |
R3 |
R4 |
Total |
% |
R1 |
R2 |
R3 |
R4 |
Total |
% |
|
Control |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1.0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3.2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
10 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
32 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
100 |
5 |
5 |
5 |
5 |
20 |
100 |
5 |
5 |
5 |
5 |
20 |
100 |
Test samples at the No Observed Effect Concentration and above only were analyzed. Analysis of the fresh media test preparations at 0 hours for the 32 and 100% v/v saturated solution test concentrations showed measured concentrations of 1.9 and 5.4 mg/L respectively. Analysis of the old media at 48 hours for the 32 and 100% v/v saturated solution test preparations showed measured concentrations of 1.4 and 4.8 mg/L respectively. Given the slight variation in measured test concentrations it was considered justifiable to base the results on the mean measured test concentrations of the test media in order to give a "worst case" analysis of the data.
Description of key information
EC50 (48 h) = 2.9 mg/L for Daphnia magna (OECD 202)
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 2.9 mg/L
Additional information
Short-term toxicity of Sodium N-methyl-N-(1-oxotetradecyl)aminoacetate (CAS 30364-51-3) towards aquatic invertebrates was investigated in one study according to OECD Guideline 202 and GLP (Harlan, 2013). Daphnia magna was exposed to nominal, filtered test concentrations of 1, 3.2, 10, 32 and 100 % v/v saturated solution for 48 h. Analytical measurements of test concentrations using HPLC-MS resulted in significantly lower measured concentrations (1.7 mg/L and 5.1 mg/L) with respect to nominal concentrations (32 and 100 % v/v saturated solution). Thus, the effect concentrations were based on the arithmetic mean measured concentrations. Effects on daphnids mobility were only observed at the highest concentration (5.1 mg/L, measured), leading to an EC50 (48 h) of 2.9 mg/L (arith. mean measured).
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.