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EC number: 200-306-6 | CAS number: 57-00-1
- 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 fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- December 2005
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.1 (Acute Toxicity for Fish)
- Deviations:
- no
- GLP compliance:
- yes
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
- Name of test material (as cited in study report): creatine monohydrate
- Molecular formula (if other than submission substance): C4H9N3O2 * H2O
- Physical state: colourless - light yellow powder
- Analytical purity: > 99.9 %
- Purity test date: 2004-11-18
- Lot/batch No.: 309931
- Expiration date of the lot/batch: 2006/03
- Stability under test conditions: stable
- Storage condition of test material: ambient temperature
- Water solubility: 14 g/L - Analytical monitoring:
- yes
- Details on sampling:
- For determination of the actual test substance concentration samples were taken immediately before the introduction of the fish and after approximately 4, 24, 48, and 96 hours after begin of exposure.
- Vehicle:
- no
- Details on test solutions:
- TEST MEDIUM PREPARATION:
The test medium with nominal 100 mg/L was prepared by dissolving 500.4 mg test substance in 5 L dilution water. - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: Zebrafish (Brachydanio rerio)
- Source: Fa. Amazonas Aquarium, A-2840 Grimmenstein, Austria
- Age at study initiation (mean and range, SD):
- Length at study initiation: 2.63 +/- 0.11 cm (mean of control group at the end of the study)
The total lengths of the animals of the control group were determined for documentation of the appropriate size. As the allocation of the fish to their groups was performed using a randomisation procedure the control group was regarded as representative for the entity of all fish used.
- Weight at study initiation: 0.55 +/- 0.12 g (mean of control group at the end of the study)
- Feeding during test: no (last feeding about 24 h prior to start of exposure)
ACCLIMATION
- Acclimation period: approx. 25 weeks
- Acclimation conditions (same as test or not): similar to test conditions. However, fish were kept in bigger glass vessels (47 x 29 x 31 cm³; 40 L) and water was purified by recirculation through filter wool
- Type and amount of food: TetraMin (Tetra Werke, Dr. rer. nat. Ulrich Baensch GmbH, Melle, Germany)
- Feeding frequency: daily
- Health during acclimation:
* Mortalities > 10 % of population in 7 days: rejection of batch.
* Mortalities 5 - 7 % of population: acclimatisation continued for 7 additional days.
* Mortalities < 5 % of population: acceptance of batch.
OTHER:
- Allocation to test groups: random - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 96 h
- Post exposure observation period:
- n.a.
- Hardness:
- 250 mg CaCO3/L (checked in control vessel at the start of the test)
- Test temperature:
- 20 °C (throughout the test)
Determined in control and test medium before introduction of the fish and then approx. 24, 48, 72, and 96 h after the start of the test. - pH:
- Control medium: 7.5 -7.6
Test medium: 7.9 - 8.0
Determined in control and test medium before introduction of the fish and then approx. 24, 48, 72, and 96 h after the start of the test. - Dissolved oxygen:
- > 86 % of the air saturation value throughou the test period;
Determined in control and test medium before introduction of the fish and then approx. 24, 48, 72, and 96 h after the start of the test. - Salinity:
- n.a.
- Nominal and measured concentrations:
- Nominal concentrations: 0 (control) and 100 mg/L
Measured geometric mean concentration: 96.6 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass vessels (29 x 20 x 24 cm³) filled with 5 L of control and test medium
- Type (delete if not applicable): closed (test vesels covered with transparent plastic lid)
- Aeration: no
- No. of organisms per vessel: 7
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
- Biomass loading rate: 1.0 g fish/L maximum
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: local tap water was mixed 1:1 with deionised water to achieve the appropriate water hardness as required by the guideline. Residue analysis of the tap water showed that it was free of pesticides.
- Pesticides: none
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: light/dark = 16/8
- Light intensity: no data
EFFECT PARAMETERS MEASURED
- All animals were observed for alterations and behavioural changes at introduction of the fish and after approx. 2, 4, 24, 48, 72, and 96 h.
(Visual observations were made at the same time as the animal observation. Any change (like change in colour or precipitation) was recorded. )
TEST CONCENTRATIONS
- Test concentrations: 0, 100 mg/L - Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- Creatine Monohydrate
- Basis for effect:
- behaviour
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 96.1 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Remarks:
- Creatine Monohydrate
- Basis for effect:
- behaviour
- Key result
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- Creatine Monohydrate
- Basis for effect:
- behaviour
- Key result
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 96.1 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Remarks:
- Creatine Monohydrate
- Basis for effect:
- behaviour
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 84.6 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat. (dissolved fraction)
- Remarks:
- Effect concentration calculated from effect concentration of creatine monohydrate.
- Basis for effect:
- behaviour
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 84.6 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat. (dissolved fraction)
- Remarks:
- Effect concentration calculated from effect concentration of creatine monohydrate.
- Basis for effect:
- behaviour
- Details on results:
- MORTALITY:
All animals survived until the scheduled termination of the test (96 h after start).
ANIMAL OBSERVATION:
All animals of the test substance group and the negative control group were inconspicuous in behaviour and appearance until the scheduled termination of the test (96 h after start).
ACTUAL TEST SUBSTANCE CONCENTRATION
After 48 h the actual test substance concentration was 90.71 mg/L (88.2 % of the actual starting concentration) and it was 92.44 mg/L after 72 h (89.9 % of the actual starting concentration). At 96 h the actual test substance cocentration was 95.1 mg/L (92.5 % of the actual starting concentration). The actual test substance concentrations show that the test substance was stable during the whole experiment. For the 96-h exposure period the geometric mean concentration between start and end of the exposure was 96.1 mg/L. The effective concentrations have been determined and expressed as the geometric mean of the measured concentrations. This is in accordance with the criteria of the respective guidelines.
VISUAL OBSERVATION OF THE TEST MEDIA
The test media were clear during the whole exposure time. - Results with reference substance (positive control):
- n.a.
- Reported statistics and error estimates:
- n.a.
- Sublethal observations / clinical signs:
Table 1: Mortality
Group
Nominal test substance concentration [mg/L]
Total number of dead fish at hours after start of exposure
0
24
48
72
96
Control
0
0
0
0
0
0
Test substance
100
0
0
0
0
0
Table 2: Water quality of the control and the test medium
Nominal test substance concentration (mg/L)
Parameter
Hours after start of exposure
0
24
48
72
96
Control (0)
Temperature
20
20
20
20
20
Oxygen
98
88
87
88
87
pH
7.5
7.6
7.6
7.6
7.6
Test substance (100)
Temperature
20
20
20
20
20
Oxygen
99
89
89
87
86
pH
7.9
7.9
8.0
7.9
7.9
- Validity criteria fulfilled:
- yes
- Conclusions:
- The 96h LC50 of creatine monohydrate for Brachydanio rerio is > 96.1 mg/L. (based on mean actual concentration).
The corresponding LC50 (96-h) of creatine for Brachydanio rerio is > 84.6 mg/L. - Executive summary:
The acute toxicity of Creatine Monohydrate to Zebrafish (Brachydanio rerio) was determined in a 96 hours static test following the pattern of 92/69/EEC C.1 (“Acute Toxicity for Fish”).
A limit test with a nominal concentration of 100 mg test substance/L dilution water was performed. The dilution water was local tap water which was mixed 1:1 with deionised water to achieve the appropriate water hardness as required by the guideline. The total hardness was 250 mg CaCO3/L. This water was used for fish-keeping and for the dilution water for the control and the test media.
7 fish each were used per test substance group and control group (dilution water only).
No mortality and no adverse effect were noted in the test substance group animals and in the control group. pH and temperature were throughout the test period. The dissolved oxygen concentration was always higher than 80 % of the air saturation value at the given temperature. The actual test substance concentration was always > 80 % of the actual starting concentration and the nominal concentration, respectively. The effective concentrations have been determined and expressed as the geometric mean of the measured concentrations.
The LC50 (96-h) of “creatine monohydrate” for Brachydanio rerio was > 96.1 mg/L (based on mean actual test substance concentration). LC0 (96-h) as well as the NOEC, based on mean actual test substance concentration, were ≥ 96.1 mg/l.
The corresponding LC50 (96 -h) of creatine for Brachydanio rerio based on mean actual test substance concentration is > 84.6 mg/L.
Reference
Description of key information
In a test on the acute toxicity of creatine monohydrate to Danio rerio
no toxic effects could be observed at the highest concentration tested
(100 mg/L nominal creatine monohydrate).
Key value for chemical safety assessment
Additional information
The acute toxicity of Creatine Monohydrate to Zebrafish (Danio rerio) was determined in a 96 hours static test following the pattern of 92/69/EEC C.1 (“Acute Toxicity for Fish”).
A limit test with a nominal concentration of 100 mg test substance/L dilution water was performed. The dilution water was local tap water which was mixed 1:1 with deionised water to achieve the appropriate water hardness as required by the guideline. The total hardness was 250 mg CaCO3/L. This water was used for fish-keeping and for the dilution water for the control and the test media.
7 fish each were used per test substance group and control group (dilution water only).
No mortality and no adverse effect were noted in the test substance group animals and in the control group. pH and temperature were throughout the test period. The dissolved oxygen concentration was always higher than 80 % of the air saturation value at the given temperature. The actual test substance concentration was always > 80 % of the actual starting concentration and the nominal concentration, respectively. The effective concentrations have been determined and expressed as the geometric mean of the measured concentrations.
The LC50 (96-h) of “creatine monohydrate” for Brachydanio rerio was > 96.1 mg/L (based on mean actual test substance concentration). LC0 (96-h) as well as the NOEC, based on mean actual test substance concentration, were ≥ 96.1 mg/l.
The corresponding LC50 (96 -h) of creatine for Brachydanio rerio based on mean actual test substance concentration is > 84.6 mg/L.
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