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Diss Factsheets
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EC number: 477-470-2 | CAS number: -
- 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
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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:
- 2007-10-29 to 2007-12-04
- 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
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- certified by "Ministerium für Umwelt und Naturschutz, Landwirtschaft und Verbraucherschutz des Landes Nordrhein-Westfalen", Germany
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 50 and 100 mg test item/L (nominal)
- Sampling method: Freshly prepared media and media after 24 h of exposure
- Sample storage conditions before analysis: at 4 °C until analysis, analysis was routinely performed on the day of sampling - Vehicle:
- no
- Details on test solutions:
- test item was added to reconstituted water (M4 medium)
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Strain/clone: Strain of Bundesgesundheitsamt Berlin (Germany)
- Age at study initiation: less than 24 h old at the beginning of the test
- Sex: Female
- Source: bred in the laboratory
- Food and Feeding: daphnids were fed with concentrated algal suspension of Desmodesmus subspicatus during the holding at libitum; not fed during the exposure
ACCLIMATION
- Test animals were bred under similar (or the same) conditions as that used during the exposure period (holding water, temperature etc.), therefore, additional acclimatisation before the test was not necessary. Brood daphnids were maintained in dilution water at the test temperature for at least 48 hours prior to the start of the test. - Test type:
- semi-static
- Water media type:
- freshwater
- Remarks:
- Reconstituted water (M4 medium)
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 266 mg CaCO3/L
- Test temperature:
- 20.1 to 20.8 °C
- pH:
- 7.7 to 7.9
- Dissolved oxygen:
- 8.2 to 8.8 mg/L
- Nominal and measured concentrations:
- nominal: 0 (control), 50 and 100 mg test item/L
measured: only DOC measurements, please see Table 1 in results section - Details on test conditions:
- TEST SYSTEM
- Test vessel: 50 mL glass beakers, fill volume: 20 mL of test medium
- Aeration: none
- Type of test: semi-static
- renewal rate of test solution: every 24 hours
- No. of organisms per vessel: 10 neonates
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 2
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water (M4 medium); Test item was added to the dilution water and then treated for 60 seconds in an ultra turrax and afterwards stirred for 24 h on a magnetic stirrer. Finally undissolved particles of the test item were removed by filtration using folded filters of pore size 7-12 μm.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 : 8 hour light-dark
- Light intensity: < 1000 lux during maintenance
RANGE-FINDING STUDY
In order to select appropriate test concentrations for use in the definitive test, a non-GLP preliminary range-finding test was conducted to determine the approximate toxicity of the test item. No details are reported. - Reference substance (positive control):
- not specified
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks:
- Swimming ability and immobilisation rate
- 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:
- Swimming ability and immobilisation rate
- Details on results:
- - Behavioural abnormalities: no abnormalities
- Other biological observations: none
- Mortality of control: no mortality
- Other adverse effects control: no
- Immobilisation of control: no immobilisation
- Abnormal responses: none - Results with reference substance (positive control):
- not reported
- Reported statistics and error estimates:
- Not reported.
- Validity criteria fulfilled:
- yes
- Remarks:
- The immobilisation and other abnormalities in the controls did not exceed 10% by the end of the test (actual value: 0 %). The dissolved oxygen concentration remained above 3 mg/L throughout the exposure period (actual values: 8.2 - 8.8 mg/L).
- Conclusions:
- In the acute toxicity test with Daphnia magna according OECD TG 202, the EC50 was estimated to be above the highest tested concentration (> 100 mg test item/L).
- Executive summary:
To investigate the acute toxicity of the test item to aquatic invertebrates, a semi-static immobilisation test with Daphnia magna according to OECD TG 202 was carried out in accordance with GLP principles. Twenty animals per treatment and control (divided in 2 replicates with 10 animals in each vessel) were exposed to nominal test item concentrations of 50 and 100 mg/L, respectively. For determination of the test item concentrations, samples were taken from each concentration level and control at the start and at the end of each water renewal period, i.e., after 24 hours of exposure. Concentrations were indirectly determined by measurement of carbon. Carbon dioxide was determined by infrared spectrometry. Biological results and endpoints are based on the nominal concentrations. An untreated control ran in parallel. The immobility or mortality of the Daphnia was determined by visual observation after 24 and 48 hours of exposure. All validity criteria of the test guideline were met, therefore the study is considered to be fully valid. No effects of the test item were found. As a result, the EC50 was estimated to be above the highest tested concentration (> 100 mg test item/L).
Reference
Table 1: Measured concentrations: DOC value [mg/L]
DOC value [mg/L] | 24 h | 48 h | ||
0 h (fresh) | 24 h (aged) | 0 h (fresh) | 24 h (aged) | |
Control | < 5 | < 5 | < 5 | < 5 |
50 mg/L test item | 12.53 | 10.62 | 11.16 | 9.177 |
100 mg/L test item | 24.76 | 21.64 | 20.71 | 16.74 |
Table 2: Immobilisation of test animals
Concentration [mg/L] | Number of Daphnia tested | Number of immobilised Daphnia | Number of immobilised Daphnia |
24 h | 48 h | ||
Control | 20 | 0 | 0 |
50 mg/L test item | 20 | 0 | 0 |
100 mg/L test item | 20 | 0 | 0 |
VALIDITY OF TEST
No immobilisation was observed in the control group and the dissolved oxygen concentration at the end of the test in control and test vessels was more than 3 mg/L in all cases.
All validity criteria were met, therefore the study is considered to be fully valid.
Description of key information
In the acute toxicity test with Daphnia magna according OECD TG 202, the EC50 was estimated to be above the highest tested concentration (> 100 mg test item/L). All validity criteria of the test guideline were fulfilled. The study is thus regarded valid.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Dose descriptor:
- EC50
- Effect concentration:
- > 100 mg/L
Additional information
To investigate the acute toxicity of the test item to aquatic invertebrates, a semi-static immobilisation test with Daphnia magna according to OECD TG 202 was carried out in accordance with GLP principles. Twenty animals per treatment and control (divided in 2 replicates with 10 animals in each vessel) were exposed to nominal test item concentrations of 50 and 100 mg/L, respectively. For determination of the test item concentrations, samples were taken from each concentration level and control at the start and at the end of each water renewal period, i.e., after 24 hours of exposure. Concentrations were indirectly determined by measurement of carbon. Carbon dioxide was determined by infrared spectrometry. Biological results and endpoints are based on the nominal concentrations. An untreated control ran in parallel. The immobility or mortality of the Daphnia was determined by visual observation after 24 and 48 hours of exposure. All validity criteria of the test guideline were met, therefore the study is considered to be fully valid. No effects of the test item were found. As a result, the 48 hour EC50 of the test item was estimated to be > 100 mg/L.
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