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EC number: 221-067-4 | CAS number: 2997-01-5
- 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:
- 2017-06-27 - 2017-10-26
- 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)
- Version / remarks:
- 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 440/2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: OECD No. 23
- Version / remarks:
- 2000
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Swiss GLP Monitoring Authorities, Date of decission 2015-11-16
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampled concentrations: 6.25, 12.5, 25, 50, and 100 mg/L
- Sampling method: duplicate samples were taken from each test concentration and the control at
the start and at the end of the test (after 48 hours). For the 48-hour stability samples, the contents
of the respective replicates were combined prior to sampling.
- Sample storage conditions before analysis: all samples were frozen (at -20 ± 5 °C)
- Analysed samples: The concentrations of JEFFAMINE® EDR-176 were analyzed in one of the duplicate test medium
samples from the control and the nominal concentrations of 50 and 100 mg/L from both sampling
times (0 and 48 hours). The samples of the lower test concentrations (6.25, 12.5 and 25 mg/L)
were not analyzed since these concentrations were below the 48 hour NOEC determined in this
test and were therefore not relevant for the interpretation of the biological results. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The test medium of the highest nominal concentration of 100 mg/L was prepared by dissolving
101 µL of the test item completely in 1000 mL of test water. This volume is equivalent to a loading rate of
100 mg/L, considering the relative density of the test item of 0.99. The test item was dissolved by intense
stirring for 15 minutes at room temperature. During this stirring period the pH was adjusted from pH 10 to
7.5 with 0.1 M hydrochloric acid solution.
- Eluate:The highest test concentration of 100 mg/L was further diluted with test water to prepare the test
media with the lower test concentrations. The test medium was prepared just before the introduction of
the daphnids (i.e., start of the test).
- Evidence of undissolved material (e.g. precipitate, surface film, etc.):After the dissolving procedure the highest
test concentration of 100 mg/L was a clear solution. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Strain/clone: Daphnia magna Straus
- Source: Daphnia Collection of the University of Basel/Switzerland in 2015
- Age of parental stock: 3-4 Weeks. At the start of the test, the organisms used
in the test were 6 to 24 hours old and were not first brood progeny.
- Feeding during test: no
ACCLIMATION
- Acclimation period: no acclimatisation was necessary, since the bred of the daphnia
was under identical conditions to those of the test.
- Type and amount of food during the breeding: Algal suspension of the green algae
Desmodesmus subspicatus supplied by the Collection of Algal Cultures (SAG, Institute for
Plant Physiology, University of Göttingen, 37073 Göttingen / Germany) and cultivated at
IES Ltd Laboratories under standardized conditions or a mixture of this algal suspension and a
commercial fish diet (Tetra Min® Hauptfutter, supplied by TETRA-GmbH, 49324 Melle / Germany).
- Feeding frequency: three times a week
- Health during acclimation (any mortality observed): The daphnia were healthy, no mortality was observed. - Test type:
- static
- Water media type:
- other: ISO Test water (Medium according to the guideline)
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 2.5 mmol/L = 250 mg/L as CaCO3
- Test temperature:
- 22°C
- pH:
- 7.5-7.9
- Dissolved oxygen:
- at the start of the test at all concentrations and the control: 8.5 mg/L oxygen
at the end of the test at all concentrations and the control: 8.2-8.3 mg/L oxygen - Salinity:
- n.d.
- Conductivity:
- n.d.
- Nominal and measured concentrations:
- nominal concentrations (measured concentrations 0/48h): 6.25, 12.5, 25, 50 (49/48) and
100 (96/96) mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: Beakers
- Type (delete if not applicable): Open (The test vessels were coverd with glass plates to reduce the loss of water by evaporation and to avoid the entry of dust into the solutions.)
- Material, size, headspace, fill volume: glas, 100 mL, open, 50 mL
- Aeration: no
- Renewal rate of test solution (frequency/flow rate): no, static test
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates):4
- No. of vessels per control (replicates):4
- No. of vessels per vehicle control (replicates):no
- Biomass loading rate: 1 Daphnia / 2 mL test media
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: ISO Medium
Ingredients / Properties [mmol/L] / Concentration [mg/L]
CaCl2 × 2H2O / 2.0 / 294
MgSO4 × 7H2O / 0.5 / 123
NaHCO3 / 0.75 / 65
KCl / 0.075 / 5.8
- Alkalinity: 0.8 mmol/L
- Water Hardness: 2.5 mmol/L = 250 mg/L as CaCO3
OTHER TEST CONDITIONS
- Adjustment of pH: 7.5 with 0.1M hydrochloric acid
- Photoperiod:16-hour light to 8-hour dark cycle with a 30-minute transition period
- Light intensity:19 and 20 µE m-2 s-1
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Immobility of the daphnids and other non-lethal effects (e.g. abnormal behavior or appearance) after 24 and 48 hours of exposure.
VEHICLE CONTROL PERFORMED: no, not needed
RANGE-FINDING STUDY without pH adjustment:
- Test concentrations: 1.0 / 10 / 100 mg/L
- Results used to determine the conditions for the definitive study:
48-hour immobilization: 1.0 mg/L / 0%; 10 mg/L / 0%; 100 mg/L / 60%
RANGE-FINDING STUDY with pH adjustment: The pH was adjusted in the 100 mg/L stock solution from pH10 to pH 7.5
- Test concentrations: 1.0 / 10 / 100 mg/L
- Results used to determine the conditions for the definitive study:
48-hour immobilization: 1.0 mg/L / 0%; 10 mg/L / 0%; 100 mg/L / 60% - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate / Separate reference studies under GLP twice a year.
- 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
- Key result
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 50 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Key result
- Duration:
- 48 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities: no abnormalities in the control and up and including the concentration 50 mg/L, at the highest concentration 100 mg/L adverse effect was noted. All surviving daphnids showed slower swimming activity compared to the control
- Mortality of control: no
- Other adverse effects control: no
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: no
- Effect concentrations exceeding solubility of substance in test medium: no
Thus, the correct dosage of the test item JEFFAMINE® EDR-176 was confirmed. The test item was stable in the test media over the test period of 48 hours. Therefore, the endpoint values were related on the nominal concentrations of the test item. The samples from the nominal test concentrations of 6.25 to 25 mg/L were not analyzed, since these concentrations were below the NOEC determined in this test and thus not relevant for the interpretation of the biological results.
During the first 24 hours of the test, no immobilized test organisms were determined in the control and up to and including the highest test item concentration of 100 mg/L. Only an adverse effect was noted at the highest concentration. Two daphnids showed slower swimming activity compared to the control animals. Thus, the 24-hour EC50 was clearly higher than 100 mg/L.
After 48 hours of exposure, no immobilized test organisms were determined and no adverse effects were noted in the control and up to and including the test item concentration of 50 mg/L.
At the highest concentration of 100 mg/L, 20 % of the daphnids were immobile. In addition, adverse effect was noted at this concentration. All surviving daphnids showed slower swimming activity compared to the control animals.
Therefore, the 48-hour EC50 of the test item could not be calculated, because none of the responses exceeded 50%. Thus the EC50 was determined to be >100 mg/L.
The 48-hour EC0 and NOEC of JEFFAMINE® EDR-176 were both 50 mg/L, since no toxic effect was observed up to and including this test concentration.
The EC100 could not be determined due to the low toxicity of the test item. However, concentrations above 100 mg/L were not tested, in accordance with the test guidelines.
No remarkable observations were made concerning the appearance of the test medium. The test media were clear solution throughout the entire test duration.
At the beginning and end of the test period, the dissolved oxygen concentration in the test medium and the control was at least 8.2 mg/L. The pH values were between 7.5 and 7.9. The water temperature during the test was maintained at 22 °C. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Relevant effect levels: 0.19-3.0 mg/L
- Dose-response test: Yes
- ECx: 24-hour EC50: 1.2 mg/L
For evaluation of the quality of the daphnia clone and the experimental conditions, potassium dichromate is tested as a positive control twice a year. The result of the latest positive control test in March 2017 (24-hour EC50: 1.2 mg/L, IES Laboratories Study 20170076) showed that the sensitivity of the test organisms was within the range given by the guideline (24-hour EC50: 0.60-2.1 mg/L). - Reported statistics and error estimates:
- No statistics needed.
The 24-hour and 48-hour NOEC, EC0 and EC100 were determined directly from the raw data. The
24-hour and 48-hour EC50 of the test item could not be calculated, because none of the responses
exceeded 50%. The EC50 was, therefore, also determined directly from the raw data. - Validity criteria fulfilled:
- yes
- Conclusions:
- In a valid, reliable and conclusive study according to OECD 202 (2004), the effect of the test substance on the mobility of young daphnids of the species Daphnia magna after 48 hours was determined. The 48-hour EC50 of the test item could not be calculated, because none of the responses exceeded 50%. Thus the EC50 was determined to be >100 mg/L.
The 48-hour EC0 and NOEC of the test substance were both 50 mg/L, since no toxic effect was observed up to and including this test concentration. - Executive summary:
The acute toxicity of the test item JEFFAMINE®EDR-176 on Daphnia magna was determined in a 48‑hour static test according to the OECD Guideline for Testing of Chemicals, No. 202 (2004) and the Commission Regulation (EC) No. 440/2008, Part C.2.
The nominal test item concentrations tested were 6.25, 12.5, 25, 50 and 100 mg/L. Additionally, a control (test water without test item) was tested in parallel.
The measured concentrations of JEFFAMINE®EDR-176 in the test media of the test concentrations of 50 and 100 mg/L were 98 and 96 % of the nominal values, respectively at the start of the test and 96 % for both concentrations at the end of the test.
Thus, the correct dosage of the test item JEFFAMINE®EDR-176 was confirmed. The test item was stable in the test media over the test period of 48 hours. Therefore, the endpoint values were related on the nominal concentrations of the test item. The samples from the nominal test concentrations of 6.25 to 25 mg/L were not analyzed, since these concentrations were below the NOEC determined in this test and thus not relevant for the interpretation of the biological results.
The biological test results (based on nominal concentration) were as follows:
24-hour EC50 > 100 mg/L
24-hour EC0 ≥ 100 mg/L
24-hour EC100 > 100 mg/L
48-hour EC50 > 100 mg/L
48-hour EC0 and 48-hour NOEC: 50 mg/L
48-hour EC100 > 100 mg/L
Reference
Analytical results
Sampling Day/ Sample Age |
Nominal Concentration of Test Item cnom |
Measured Concentration of Test Item x |
Sample Preparation Factor F |
Determined Concentration of Test Item c |
% of Nominal Concentration |
[d/h] |
[mg/L] |
[mg/L] |
[mg/L] |
[%] |
|
0/0 |
Control |
n.d. |
1 |
< LOQ |
n.a. |
(fresh) |
50 |
9.85 |
5 |
49.2 |
98 |
100 |
9.61 |
10 |
96.1 |
96 |
|
2/48 |
Control |
n.d. |
1 |
< LOQ |
n.a. |
(aged) |
50 |
9.59 |
5 |
47.9 |
96 |
|
100 |
9.64 |
10 |
96.4 |
96 |
n.d. = no test item detected
n.a. = not applicable
LOQ: 3.31 mg/L
Biological Results: Effect of JEFFAMINE® EDR-176 on the Mobility of Daphnia magna
Nominal Test Item Concentration |
No. of Daphnids Tested |
Immobilized Daphnids after 24 Hours |
Immobilized Daphnids after 24 Hours |
Immobilized Daphnids after 48 Hours |
Immobilized Daphnids after 48 Hours |
[mg/L] |
|
No. |
[%] |
No. |
[%] |
Control |
20 |
0 |
0 |
0 |
0 |
6.25 |
20 |
0 |
0 |
0 |
0 |
12.5 |
20 |
0 |
0 |
0 |
0 |
25 |
20 |
0 |
0 |
0 |
0 |
50 |
20 |
0 |
0 |
0 |
0 |
100 |
20 |
0(2A) |
0 |
4(16A) |
20 |
A: number of mobile test animals with slower swimming activity compared to the control animals
Description of key information
The acute toxicity of the test item on Daphnia magna was determined in a 48‑hour static test according to the OECD Guideline for Testing of Chemicals, No. 202 (2004) and the Commission Regulation (EC) No. 440/2008, Part C.2.
The biological test results (based on nominal concentration) were as follows:
24-hour EC50> 100 mg/L
24-hour EC0≥100 mg/L
24-hour EC100> 100 mg/L
48-hour EC50> 100 mg/L
48-hour EC0and 48-hourNOEC: 50 mg/L
48-hour EC100> 100 mg/L
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 100 mg/L
Additional information
The test item is not toxic for invertebrate.
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