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EC number: 813-788-3 | CAS number: 1803551-73-6
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 2008
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- adopted April 13, 2004
- Deviations:
- no
- GLP compliance:
- yes
- Specific details on test material used for the study:
- Stability of test concentration/s during exposure: Examined by chemical analysis (DOC) in the freshly prepared media on 2017-12-12 and 2017-12-13 and in the media after 24 hours of exposure on 2017-12-13 and 2017-12-14 according to the semi-static test conditions.
- Analytical monitoring:
- yes
- Vehicle:
- no
- Details on test solutions:
- PRE-TREATMENT OF TEST ITEM AND PREPARATION OF TEST ITEM CONCENTRATIONS
A stock solution was prepared to give the desired series of test concentrations. 100.3 mg of the test item were added to 1 litre of dilution water on 2017-12-12 and 101.0 mg of the test item were added to 1 litre of dilution water on 2017-12-13 and stirred for 1 h on a magnetic stirrer. The pH was measured to be 6.2 on 2017-12-12 and 6.1 on 2017-12-13.
To produce the different test item concentrations appropriate amounts of the stock solution were diluted with dilution water to a volume of 500 mL. 50 mL of the prepared solutions were taken per replicate and 0.5 mL of dilution water containing 5 daphnids was given to all replicates resulting in the final nominal concentrations. For each test item concentration and the control 4 replicates were prepared. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Name: Daphnia magna STRAUS, parthenogenetic females
Source: Strain of Bundesgesundheitsamt Berlin
Maintenance and Acclimatisation: A population of parthenogenetic females of synchronized age structure has been maintained for more than 20 years in the test facility under constant temperature conditions (20 +/- 2 °C) at a 16 : 8 hour light-dark photoperiod (light intensity: < 20 μE x m-2 x s-1). The culture water (so-called 'M4 medium') was partly renewed once a week. The Daphnia were exclusively fed unicellular green algae (Desmodesmus subspicatus) 'ad libitum'. Mortalities of parent Daphnia during the culture period were recorded daily. The neonates were separated from their parent Daphnia by filtration prior to the acute test. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- The hardness of the dilution water used was 14.6 °dH (= 261 mg/L CaCO3).
- Test temperature:
- 18 - 22 °C with a maximum temperature fluctuation of +/- 1 °C in each individual test.
- pH:
- 6.2 - 8.1
- Dissolved oxygen:
- 8.5 - 8.9 mg/L (94 - 101 %)
- Nominal and measured concentrations:
- nominal: 6.25, 12.5, 25, 50 and 100 mg/L
- Details on test conditions:
- EXPOSURE CONDITIONS
Test vessels: 100 mL glass beakers covered with watch glasses holding 5 neonates in 50 mL of test medium.
Experimental design: 5 test concentrations plus 1 control; 5 neonates per vessel, 4 replicates per concentration/control; no feeding during the exposure period; semi-static system.
Method of initiation: neonates were placed in prepared media.
Photoperiod: 16 h light : 8 h dark
Temperature of incubation unit: 19.4 to 19.8 °C
Aeration: none
Test item concentration/s: 6.25, 12.5, 25, 50 and 100 mg/L
Method of administration: stock solution (100 mg/L)
Medium renewal: daily
Duration of exposure: 48 hours
Criteria of effects: The criterion of adverse effects used in this study was the item-induced alteration of the normal mobility behaviour and the loss of locomotory actions of the neonates, observed at 24 and 48 hours. - Reference substance (positive control):
- no
- Duration:
- 24 h
- Dose descriptor:
- EC0
- Effect conc.:
- 50 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95 % confidence limit: not determined due to mathematical reasons or inappropriate data
- Duration:
- 24 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: 95 % confidence limit: not determined due to mathematical reasons or inappropriate data
- Duration:
- 24 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95 % confidence limit: not determined due to mathematical reasons or inappropriate data
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 12.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95 % confidence limit: 29.5 - 46.8 mg/L
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 37 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95 % confidence limit: 29.5 - 46.8 mg/L
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95 % confidence limit: 29.5 - 46.8 mg/L
- Details on results:
- The results are expressed in terms of nominal concentrations. The substance has not a definite or unique structure and consists of serveral components. The content of the test item during the exposure period was verified by DOC determination.
- Reported statistics and error estimates:
- The EC 50 was calculated by probit analysis using the statistics programme ToxRatPro Version 2.10 (released 2010-09-10).
- Validity criteria fulfilled:
- yes
- Remarks:
- The immobilisation and other abnormalities in the controls did not exceed 10 % by the end of the test. The dissolved oxygen concentration remained above 3 mg/L throughout the exposure period.
- Conclusions:
- The acute toxicity of RFR 6634 to Daphnia magna under semi-static conditions was determined to be EC50 = 37 mg/L after 48 hours.
- Executive summary:
A study was performed to assess the acute toxicity of RFR 6634 to Daphnia magna STRAUS under semi-static conditions.
The study was conducted in accordance with the Council Regulation (EC) No 440/2008, Method C.2 ‘Acute toxicity for Daphnia’ (2008) which is equivalent to OECD Guideline for Testing of Chemicals No. 202 'Daphnia sp., Acute Immobilisation Test' (adopted April 13, 2004).
The Daphnia were exposed to a range of concentrations, nominally 6.25, 12.5, 25, 50 and 100 mg/L of RFR 6634 dissolved in dilution water. Auxiliary used to prepare the test media was a magnetic stirrer.
Observations were made on the swimming ability and the immobilisation rate, respectively, after 24 and 48 hours of exposure. The following values were determined:
Time EC50 [h] [mg/L] 24 > 100 48 37.0 The results are expressed in terms of nominal concentrations. The substance has not a definite or unique structure and consists of serveral components. The content of the test item during the exposure period was verified by DOC determination.
The hardness of the dilution water used was 14.6 °dH (= 261 mg/L CaCO3).
Reference
Analysis (DOC)
Nominal concentration | 0 h | 24 h | 0 h | 24 h |
[mg/L] | 2017 -12 -12 | 2017 -12 -13 | 2017 -12 -13 | 2017 -12 -14 |
control | -- | -- | -- | < 2 |
6.25 | 4.1803 | 4.3940 | 3.8539 | 3.7476 |
12.5 | 7.8568 | 7.5472 | 7.2924 | 7.1740 |
25 | 15.064 | 13.294 | 12.729 | 12.422 |
50 | 29.869 | 27.079 | 25.468 | 25.002 |
100 | 57.324 | 53.113 | 51.046 | 50.392 |
Results of the probit analysis
Results of the probit analysis: Selected effective concentrations (ECx) of the test item and their 95%- confidence limits (according to Fieller`s theorem).
Parameter | EC10 | EC20 | EC50 |
Value [mg/L] | 16.531 | 21.799 | 37.006 |
lower 95%-cl | 10.377 | 15.248 | 29.498 |
upper 95%-cl | 21.730 | 27.551 | 46.833 |
Slope function after Litchfield and Wilcoxon: 1.875
Description of key information
A study was performed to assess the acute toxicity of RFR 6634 to Daphnia magna STRAUS under semi-static conditions.
The study was conducted in accordance with the Council Regulation (EC) No 440/2008, Method C.2 ‘Acute toxicity for Daphnia’ (2008) which is equivalent to OECD Guideline for Testing of Chemicals No. 202 'Daphnia sp., Acute Immobilisation Test' (adopted April 13, 2004).
The Daphnia were exposed to a range of concentrations, nominally 6.25, 12.5, 25, 50 and 100 mg/L of RFR 6634 dissolved in dilution water. Auxiliary used to prepare the test media was a magnetic stirrer.
Observations were made on the swimming ability and the immobilisation rate, respectively, after 24 and 48 hours of exposure. The following values were determined:
Time | EC50 |
[h] | [mg/L] |
24 | > 100 |
48 | 37.0 |
The results are expressed in terms of nominal concentrations. The substance has not a definite or unique structure and consists of serveral components. The content of the test item during the exposure period was verified by DOC determination.
The hardness of the dilution water used was 14.6 °dH (= 261 mg/L CaCO3).
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 37 mg/L
Additional information
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