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EC number: 436-120-9 | CAS number: 99627-05-1
- 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:
- from 2004-06-04 to 2004-12-06
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.1 (Acute Toxicity for Fish)
- Version / remarks:
- 1992
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: Samples were taken from all concentrations: 0 (control), 1, 1.8, 3.2, 5.6 and 10 mg/L
- Sampling method: Samples were measured at the start and at the end (96 h) of the test.
- Sample storage conditions before analysis: at room temperature - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The test medium (reconstituted water and test material) was freshly prepared. A stock preparation with a test material concentration of 100 mg/L was prepared. Therefore, the calibrated flask with test material and vehicle, reconstituted water, was stirred with a magnetic stirrer for one hour. The stock preparation was diluted with reconstituted water to the different test media concentrations.
- Sampling: Samples were taken from all concentrations. After preparation of the test media the analytical values were determined. The maintenance of the test material concentrations was confirmed by determination of further samples after a period of 96 hours.
- Controls: Blank control performed with the test solution without the test substance.
- Evidence of undissolved material: No - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: Zebra fish
- Source: West-Aquarium Institute of Toxicology, Merck KGaA, Germany
ACCLIMATION
- Acclimation period: > 14 days
- Acclimation conditions: Same as the test. The zebra fish were acclimatized to the conditions of the laboratory and were kept in reconstituted water.
- Type and amount of food during acclimation: The zebra fish were fed with a commercial flake diet, JBL Novo Bel® (JBL GmbH & Co. KG, Neuhofen). Furthermore the fish got daphnia and frozen mosquitolarva
- Feeding frequency during acclimation: 2-3 times a week.
- Health during acclimation: No mortality was observed.
FEEDING DURING TEST
No feeding was performed during die test - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Remarks on exposure duration:
- None
- Post exposure observation period:
- None
- Hardness:
- n.a
- Test temperature:
- 24 to 26 °C
- pH:
- 7.56 - 7.91
- Dissolved oxygen:
- The dissolved oxygen concentrations were > 60 % oxygen saturation throughout the study.
- Salinity:
- n.a.
- Conductivity:
- n.a
- Nominal and measured concentrations:
- - Nominal concentrations: 0 (control), 1, 1.8, 3.2, 5.6 and 10 mg/L
- Measured concentrations: The analytically determined concentrations were 1.0, 1.7, 3.1, 5.5 and 9.7 at the start of the test and 0.9, 1.6, 3.0, 5.3 and 9.5 at the end of the test. The measured concentrations were determined between 94 - 100 % at the start and 89 - 95 % at the end of the test. - Details on test conditions:
- TEST SYSTEM
- Test vessel: All-glass aquaria
- Type: open
- Aeration: yes
- No. of organisms per vessel: 7
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 2
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstitued water according to OECD guideline 203 (1984)
- Culture medium different from test medium: No
- Intervals of water quality measurement: The temperature was measured continuously during the test. pH- values and oxygen concentrations were measured after 0, 24, 48, 72 and 96 hours.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 12 hours light - 12 hours dark regime
EFFECT PARAMETERS MEASURED: The fish were observed for signs of toxicity or death after 24, 48, 72 and 96 hours,
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.8
- Range finding study : not performed - Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 7.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95 % C.L. (6.0 -9.4 mg/L)
- Details on results:
- - Observations on body length and weight: not observed
- Behavioural abnormalities: yes. Signs of toxicity were seen in the concentrations 3.2, 5.6 and 10.0 mg/L. They started in the higher concentrations after 3 hours and lasted up to the end of the experimental part . These consisted of absence of escape reflex, swimming slightly irregular, or at the water surface, or even at the bottom of the aquarium, fish were lying on the side/back, showed temporary restlessness, and accelerated respiration.
- Mortality of control: no mortality occurred in the control test.
- Other adverse effects control: not observed
- Abnormal responses: yes
- Any observations that might cause a difference between measured and nominal values: no
- Effect concentrations exceeding solubility of substance in test medium: no - Results with reference substance (positive control):
- not performed
- Sublethal observations / clinical signs:
Table 1: Nominal and corresponding analytical concentrations in % during the study
Nominal concentration
[mg/l]Analytical concentration in % during the test
Start
96 h
1.0
100
90
1.8
94
89
3.2
97
94
5.6
98
95
10.0
97
95
Table 2: pH values and oxygen concentrations
Nominal concentration [mg/l]
pH value
O2 [%]
0 h
24 h
48 h
72 h
96 h
0 h
24 h
48 h
72 h
96 h
Control
7.86
7.58
7.71
7.69
7.58
94.7
82.4
78.8
85.4
82.0
1.0
7.83
7.56
7.72
7.67
7.59
95.3
88.7
84.9
83.8
88.0
1.8
7.84
7.61
7.69
7.67
7.60
94.9
89.7
85.9
83.9
85.6
3.2
7.85
7.63
7.64
7.60
7.61
95.7
86.6
83.3
81.9
84.2
5.6
7.86
7.64
7.64
7.60
7.60
93.7
78.1
72.4
73.0
78.9
10.0
7.91
7.66
--
--
--
94.8
61.2
--
--
--
Table 3: Nominal concentrations and number of deaths/exposed fish
Nominal concentration [mg/l]
Dead / exposed fish
24 h
48 h
72 h
96 h
Control
0 / 7
0 / 7
0 / 7
0 / 7
1.0
0 / 7
0 / 7
0 / 7
0 / 7
1.8
0 / 7
0 / 7
0 / 7
0 / 7
3.2
0 / 7
0 / 7
0 / 7
0 / 7
5.6
0 / 7
0 / 7
0 / 7
0 / 7
10.0
7 / 7
7 / 7
7 / 7
7 / 7
- Validity criteria fulfilled:
- yes
- Conclusions:
- The acute toxicity of the test substance to Danio rerio was determined by a static test. Under the given conditions of this study the 96 h LC50 value for fish was in the range of 1 to 10 mg/L (7.5 mg/L). and the EC0 was < 1.8 mg/L.
- Executive summary:
The objective of this study was to determine the acute fish toxicity of the test material using zebra fish (Danio rerio) according to OECD 203 (1992) under GLP conditions. For this purpose, 7 zebra fish per test material group and further 7 zebra fish in a control group were exposed over 96 hours, under defined conditions. The fish were observed for signs of toxicity or death. Zebra fish (Danio rerio) were exposed to aqueous test material solutions of nominal 1.0, 1.8, 3 .2, 5.6, and 10.0 mg/L in an open static system. Samples were taken from all concentrations. The samples were analyzed using HPLC with UV-detection and external calibration for quantification. The maintenance of the test material concentrations was confirmed by determination of further samples after a period of 96 hours. The analytically determined concentrations were between 94- 100 % at the start and 89 - 95 % at the end. During the experimental phase of the study, the test material concentrations could be maintained at > 80 % of the initial concentrations. Therefore, the LC50 values had to be calculated with the nominal concentrations. No signs of toxicity were seen in the control group and in the zebra fish exposed to concentrations of 1.0 and 1.8 mg/L. Signs of toxicity were seen in the concentrations 3.2, 5.6, and 10.0 mg/L. They started in the higher concentrations after 3 hours and lasted up to the end of the experimental part. These consisted of absence of escape reflex, swimming slightly irregular, or at the water surface, or even at the bottom of the aquarium, fish were lying on the side/back, showed temporary restlessness, and accelerated respiration. Deaths occurred only in the highest concentration, after an exposure period of about 6-23 hours. Under the given conditions of this study the 96 h LC50 value for fish was in the range of 1 to 10 mg/L (7.5 mg/L) and the EC0 was < 1.8 mg/L.
Reference
Description of key information
The acute toxicity of the test substance to Zebra fish (Danio rerio) was determined by static test according to OECD 203 under GLP conditions. The LC50 was determined to be 7.5 mg/L (reference 6.1.1-1).
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 7.5 mg/L
Additional information
The objective of this study was to determine the acute fish toxicity of the test material using zebra fish (Danio rerio) according to OECD 203 (1992) under GLP conditions. For this purpose, 7 zebra fish per test material group and further 7 zebra fish in a control group were exposed over 96 hours, under defined conditions. The fish were observed for signs of toxicity or death. Zebra fish (Danio rerio) were exposed to aqueous test material solutions of nominal 1.0, 1.8, 3.2, 5.6, and 10.0 mg/L in an open static system. Samples were taken from all concentrations. The samples were analyzed using HPLC with UV-detection and external calibration for quantification. The maintenance of the test material concentrations was confirmed by determination of further samples after a period of 96 hours. The analytically determined concentrations were between 94 - 100 % at the start and 89 - 95 % at the end. During the experimental phase of the study, the test material concentrations could be maintained at > 80 % of the initial concentrations. Therefore, the LC50 values had to be calculated with the nominal concentrations. No signs of toxicity were seen in the control group and in the zebra fish exposed to concentrations of 1.0 and 1.8 mg/L. Signs of toxicity were seen in the concentrations 3.2, 5.6, and 10.0 mg/L. They started in the higher concentrations after 3 hours and lasted up to the end of the experimental part. These consisted of absence of escape reflex, swimming slightly irregular, or at the water surface, or even at the bottom of the aquarium, fish were lying on the side/back, showed temporary restlessness, and accelerated respiration. Deaths occurred only in the highest concentration, after an exposure period of about 6 - 23 hours. Under the given conditions of this study the 96 h LC50 value for fish was in the range of 1 to 10 mg/L (7.5 mg/L) and the EC0 was < 1.8 mg/L.
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