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EC number: 219-354-4 | CAS number: 2424-01-3
- 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
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 9-Apr-2018 to 9-May-2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- April 13, 2004
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- N-methyldiallylamine
- EC Number:
- 219-354-4
- EC Name:
- N-methyldiallylamine
- Cas Number:
- 2424-01-3
- Molecular formula:
- C7H13N
- IUPAC Name:
- methylbis(prop-2-en-1-yl)amine
Constituent 1
- Specific details on test material used for the study:
- - Source and lot/batch No.of test material: Lot 20160912
- Purity: 99.2%
- Expiration date of the lot/batch: 1-August-2018
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: at room temperature
- Stability under test conditions: test substance stable
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: negative control (0 mg/L), 10, 18, 32, 56, and 100 mg/L
- Volume: 3.6 mL for the regular samples and 1.8 mL for quality control (QC) samples
- Sampling method: Duplicate samples for analysis, and reserve samples, were taken from each concentration before transfer to the replicate test vessels for the initial (T = 0 hours) samples. Two extra samples were taken from the 32 mg/L concentration for analytical QC, and two reserve QC samples were also taken. At test completion (T = 48 hours) test solutions were not pooled, due to the volatility of MTDID 49220, and duplicate samples were taken from at least one individual replicate.
- Sample storage conditions before analysis: Samples were stored in a freezer (≤ -15°C) until analysis at the analytical laboratory of the test facility.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The batch of MTDID 49220 tested was a clear yellow liquid with a purity of 99.2% and was completely soluble in test medium at the concentrations tested. Preparation of the test solutions started with the highest concentration of 100 mg/L, applying a short period of magnetic stirring to accelerate dissolution of the test item in medium. The pH was adjusted from 9.3 - 9.5 to 8.0 - 8.5 with 1M HCl in all tests. The lower concentrations were prepared by subsequent dilutions of the highest concentration in test medium.
- Controls: Test medium without test substance or other additives
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): none, test solutions were clear and colorless at the end of the preparation procedure.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain/clone: Daphnia magna (Straus, 1820), at least third generation, obtained by a cyclical parthenogenesis under specified breeding conditions.
- Source: In-house laboratory culture with a known history
- Age of parental stock: > 2 weeks to < 4 weeks
- Age at study initiation: < 24 hrs
- Feeding during test: No
- Culturing: Adult daphnids were cultured in M7 medium (adjusted ISO medium plus trace elements, micronutrients, and vitamins). Adult daphnids in the cultures were held for at least 14 days, and were not more than 4 weeks old prior to collection of the juveniles for testing. During the period preceding the test, water temperatures were 18 - 22°C. Daphnids in the cultures were fed daily a suspension of freshwater algae. The adults were fed prior to test initiation, but neonates were not fed during the test.
- Health: Daphnids originated from a healthy stock, 2nd to 5th brood, showing no signs of stress such as mortality >20%, presence of males, ephippia or discoloured animals and there was no delay in the production of the first brood.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 180 mg/L as CaCO3 (in test medium)
- Test temperature:
- 20 °C first test
20 - 21 °C second test - pH:
- 8.1 - 8.6 first test
8.0 - 8.4 second test - Dissolved oxygen:
- 7.3 - 8.5 mg/L first test
8.3 - 9.2 mg/L second test - Nominal and measured concentrations:
- Nominal: 0 mg/L, 10 mg/L, 18 mg/L, 32 mg/L, 56 mg/L, 100 mg/L
Measured: see Table 1, 2
Results are based on nominal concentrations since analytically determined concentrations were greater than the nominal values for the first test (109 -157%), and 92-111% of nominal for the second test. - Details on test conditions:
- TEST SYSTEM
- Test vessel: 60 mL airtight, all-glass, closed with no headspace to prevent loss of MTDID 49220 due to volatilization
- Fill volume: 60 mL volume
- Aeration: no
- No. of organisms per vessel: five
- No. of vessels per concentration (replicates): four
- No. of vessels per control (replicates): four
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water:adjusted ISO medium prepared using reverse-osmosis purified water (GEON Waterbehandeling, Berkel-Enschot, The Netherlands)
CaCl2.2H2O - 211.5 mg/L
MgSO4.7H2O - 88.8 mg/L
NaHCO3 - 46.7 mg/L
KCl - 4.2 mg/L
- Culture medium different from test medium: Yes, culture medium was M7 (adjusted ISO medium with addition of M7 trace elements, micronutrients, and vitamins).
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: 16 hours daily
EFFECT PARAMETERS MEASURED: immobilization (including mortality) observed at 24 and 48 hours
RANGE-FINDING STUDY
- Test concentrations: 0 mg/L (control) and 100 mg/L (nominal)
- Results used to determine the conditions for the definitive study: yes - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate (K2Cr2O7)
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other:
- Remarks:
- Result from the first test. 10% immobilization observed at the 56 mg/L test concentration and the 100 mg/L test concentrations at 48 hours.
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other:
- Remarks:
- Result from the second of two tests. 40% immobilization observed at the 100 mg/L test concentation at 48 hours.
- Details on results:
- Test was conducted twice since the result of the first test indicated MTDID 49220 to be less toxic than indicated by the range finding test.
See Tables 3, 4 for detailed results. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Dose-response test: Yes
- ECx: 48-hr EC50 = 0.33 mg/L (95% CI, 0.29 mg/L to 0.38 mg/L)
- Other: The sensitivity of Daphnia magna originating from the batch used in this test, for potassium dichromate fell within the expected range of sensitivity observed during previous years (n > 60; 48-hr EC50 between 0.3 and 1.0 mg/L.) The reference substance test was conducted within one month prior to initiation of the testing of MTDID 49220.
Any other information on results incl. tables
Table 3, Acute immobilization of daphnids after 24 and 48 hours - First Test
Nominal concentration (mg/L) | Number of Daphnia exposed | Response at 24 hours (number) | Response at 24 hours (%) | Response at 48 hours (number) | Response at 48 hours (%) |
0 | 20 | 0 | 0 | 0 | 0 |
10 | 20 | 0 | 0 | 0 | 0 |
18 | 20 | 0 | 0 | 0 | 0 |
32 | 20 | 0 | 0 | 0 | 0 |
56 | 20 | 1 | 5 | 2 | 10 |
100 | 20 | 0 | 0 | 2 | 10 |
Table 4, Acute immobilization of daphnids after 24 and 48 hours - Second Test
Nominal concentration (mg/L) | Number of Daphnia exposed | Response at 24 hours (number) | Response at 24 hours (%) | Response at 48 hours (number) | Response at 48 hours (%) |
0 | 20 | 0 | 0 | 0 | 0 |
10 | 20 | 0 | 0 | 0 | 0 |
18 | 20 | 0 | 0 | 0 | 0 |
32 | 20 | 2 | 10 | 2 | 10 |
56 | 20 | 0 | 0 | 6 | 30 |
100 | 20 | 5 | 25 | 8 | 40 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- Control immobilization was < 10% at the end of the test. The dissolved oxygen concentration was ≥ 3 mg/L in the control and test vessels at the end of the test.
- Conclusions:
- The 48-hour EC50 (immobilization) of MTDID 49220 to Daphnia magna exceeded 100 mg/L. The test was conducted according to OECD TG 202.
- Executive summary:
The 48-hour EC50 of MTDID 49220 to Daphnia magna was examined in a static test conducted according to OECD TG 202. Two tests were conducted in which test solutions were prepared as the control (0 mg/L), and at concentrations of 10, 18, 32, 56 and 100 mg/L (nominal). Nominal concentrations were verified with analysis. No immobilization of daphnids was observed in the controls. At 48 hours, 10% immobilization was observed at 100 mg/L in the first test, and 40% immobilization was observed at 100 mg/L in the second test. Thus, the 48-hour EC50 was > 100 mg/L for MTDID with Daphnia magna. The test was conducted according to internationally accepted test guidelines and was GLP compliant. It is reliable without restriction and suitable for Risk Assessment, Classification and Labeling, and PBT Analysis.
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