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EC number: 235-426-8 | CAS number: 12225-08-0
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_ecotoxicological-information.png)
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:
- 2011-11-11 to 2011-11-18
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study performed according to relevant guidelines and compliant to GLP
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- and Council Regulation (EC) No. 440/2008 Method C.1
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- according to German Chemikaliengesetzt and directive 88/320/EEC
- Analytical monitoring:
- no
- Details on sampling:
- As the test item is highly insoluble in water, no suitable method for determination of the test item could be established and no analytical determination was carried out. All effect values of the test item are given based on the nominal concentration.
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method:
A stock solution (1 mg/L test item was weighed out) was prepared with dilution water.
Weighing of the test item for day 0 and 1 was carried out 72 h prior to test start and stored in the dark at room temperature until preparation of the saturated solution. Weighing of the test item for day 2 and 3 was carried out after 0 and 24 h of the study, respectively.
The stock solution was stirred for 48 hours with a magnetic stirrer. The undissolved particles were removed by membrane filtration (membrane filter 0.45 µm, RC, MACHEREY-NAGEL). The centrifugation for 20 min at 10000 g was performed at day 0. No pellet was generated, so the procedure was declared insufficient. On the following days only membrane filtration was used.
- Eluate: Dilution water
- Differential loading: None, limit test
- Controls: 7 fish in dilution water (without test item) were tested under the same test conditions as the test replicates. - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: Zebrafish
- Source: All fish used in the test were gained at DR.NOACK-LABORATORIEN from a single brood stock. (supplier: Niedersächsischer Landesbetrieb für Wasserwirtschaft, Küsten- und Naturschutz, An der Scharlake 39, D-31135 Hildesheim)
- Length at study initiation (length definition, mean, range and SD): Average body length: 2.19 cm
- Weight at study initiation (mean and range, SD): Average body weight: 0.209 g
- Method of breeding:Holding was performed at the test facility at 23+/-2 °C and diffuse light (0.1 - 10 µmol photons • m-2 • s-1, natural photoperiod). The water was changed at least once per week. The dissolved oxygen concentration was more than 80 % of the air saturation value. No disease treatments were administered throughout holding and testing. Food was provided 3 times per week. The amount of food was 4 % of the fish body weight per feeding day. The test fish were not fed 24 h before the test started.
- Feeding during test: No feeding during test
ACCLIMATION
- Acclimation period: Zebrafish with at least 12 days of acclimatisation and mortality < 5 % within these days before the study starts were used in the test.
- Acclimation conditions (same as test or not): Same as test
- Type and amount of food: 4 % of the fish body weight per feeding day. The test fish were not fed 24 h before the test started. Food: Sera Vipan; SERA GMBH, D-52518 Heinsberg
- Feeding frequency: 3 times per week.
- Health during acclimation (any mortality observed): No mortality observed, no disease treatments were administered throughout holding and testing.
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 96 h
- Hardness:
- Total Hardness at day 0: 60.5 mg/L
- Test temperature:
- Please refer to "Any other information on materials and methods"
- pH:
- Please refer to "Any other information on materials and methods"
- Dissolved oxygen:
- Please refer to "Any other information on materials and methods"
- Salinity:
- Not measured, freshwater
- Nominal and measured concentrations:
- Please refer to "Any other information on materials and methods"
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Glass aquaria
- Type (delete if not applicable): open, loosely covered by glass tops
- Material, size, headspace, fill volume: glass, 2 L test volume per vessel
- Aeration: Gentle aeration
- Renewal rate of test solution (frequency/flow rate): daily renewal (after 0, 24, 48, 72 hours)
- No. of organisms per vessel: 7
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
- Biomass loading rate: less than 1 g fish per L test solution
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Tap water of local origin was used for holding and testing. The water was filtered on activated charcoal and aerated for at least 24 h to remove possible chlorine.
Nominal water parameters:
Total hardness: 10 - 250 mg CaCO3/L
pH-value: 6.0 - 8.5
- Culture medium different from test medium: no
- Intervals of water quality measurement: pH-value, temperature and oxygen saturation were measured
measurements in all vessels at the beginning of the test and every 24 h (from old and new media). Total hardness of the water was determined at the beginning out of the test control. During the test the water temperature was recorded continuously with a data logger (once per hour).
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: natural
- Light intensity: 0.1 - 10 µmol photons x m-2 x s-1
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Fish were considered dead if there was no visible movement (e.g. gill covers movement) and if touching of the caudal peduncle produced no reaction. Records were kept of visible abnormalities (e.g. loss of equilibrium, swimming behaviour, respiratory function, pigmentation, etc.). Observations were made after 24, 48, 72 and 96 h.
TEST CONCENTRATIONS
- Range finding study: Yes
Cumulative Mortality [%] in the Preliminary Test (non GLP)
(n = 5)
Nominal concentration level
[mg/L] Test Duration [hours]
24 48 72 96
1.00 0 0 0 0
Controls 0 0 0 0 - Reference substance (positive control):
- no
- Duration:
- 96 h
- Dose descriptor:
- EC0
- Effect conc.:
- 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: mortality and sublethal effects
- Remarks on result:
- other: As the test item is highly insoluble in water, no suitable method for determination of the test item could be established.
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: As the test item is highly insoluble in water, no suitable method for determination of the test item could be established.
- Details on results:
- - Behavioural abnormalities: Not observed
- Mortality of control: 0%
- Other adverse effects control: Not observed
- Abnormal responses: Not observed
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: No, the test item was clearly dissolved. - Results with reference substance (positive control):
- No reference substance tested
- Reported statistics and error estimates:
- The concentration leading to 0 and 100 % mortality (LC0 and LC100) after 96 h were determined directly from the test results. LC50-values have not to be calculated in a limit test.
- Sublethal observations / clinical signs:
Observations in the Test Vessels
(n=7)
Nominal
concentration level
[mg/L]Effect*)
Test Duration [h]
24
48
72
96
1.00
(1)
7/7
7/7
7/7
7/7
Control
(1)
7/7
7/7
7/7
7/7
*) The number in brackets corresponds to the following observations: (1) = Normal behaviour
Cumulative Mortality [%] in the Test Vessels
Nominal
concentration level
[mg/L]Test Duration [h]
24
48
72
96
1.00
0
0
0
0
Control
0
0
0
0
LC-Values with 95 % Confidence Intervals
based on nominal concentration
Test duration [h]
LC50
p = 95 %
24
> 1.00 mg/L
not applicable
48
> 1.00 mg/L
not applicable
72
> 1.00 mg/L
not applicable
96
> 1.00 mg/L
not applicable
LC100 =
> 1.00 mg/L
Lowest tested concentration level
with 100 % mortality after 96 h
LC0 =
1.00 mg/L
Highest tested concentration level
with 0 % mortality after 96 h
- Validity criteria fulfilled:
- yes
- Conclusions:
- In this study the test item did not cause any effects to zebrafish after 96 h when tested a saturated solution with a nominal concentration level of 1.00 mg/L. The LC0 (0 – 96 h) was 1.00 mg/L.
- Executive summary:
The acute toxicity of the test item to fish (zebrafish) was determined according to OECD-Guideline for Testing of Chemicals No. 203.
A semi-static limit test with daily renewal of the test media was conducted with a saturated solution* of 1.00 mg/L of the test item. Duration of the test was 96 h. 7 test organisms were exposed to the limit concentration and the control. Water quality parameters pH-value, temperature and oxygen-saturation measured after 0, 24, 48, 72 and 96 h were determined to be within the acceptable limits.
As the test item is highly insoluble in water, no suitable method for determination of the test item could be established and no analytical determination was carried out. All effect values of the test item are given based on the nominal concentration. The acute toxicity of the test item is summarised in the following table:
Table 1: LC-Values with 95 % Confidence Intervals
based on nominal concentration
Test duration [h]
LC50
p = 95 %
24
> 1.00 mg/L
not applicable
48
> 1.00 mg/L
not applicable
72
> 1.00 mg/L
not applicable
96
> 1.00 mg/L
not applicable
LC100 =
> 1.00 mg/L
Lowest tested concentration level
with 100 % mortality after 96 h
LC0 =
1.00 mg/L
Highest tested concentration level
with 0 % mortality after 96 h
- Endpoint:
- short-term toxicity to fish
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- see Read-across justification in section 13 for details
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 96 h
- Dose descriptor:
- EC0
- Effect conc.:
- 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: mortality and sublethal effects
- Remarks on result:
- other: As the test item is highly insoluble in water, no suitable method for determination of the test item could be established.
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: As the test item is highly insoluble in water, no suitable method for determination of the test item could be established.
- Validity criteria fulfilled:
- yes
- Conclusions:
- In this study the test item did not cause any effects to zebrafish after 96 h when tested a saturated solution with a nominal concentration level of 1.00 mg/L. The LC0 (0 – 96 h) was 1.00 mg/L.
- Executive summary:
The acute toxicity of the test item to fish (zebrafish) was determined according to OECD-Guideline for Testing of Chemicals No. 203.
A semi-static limit test with daily renewal of the test media was conducted with a saturated solution* of 1.00 mg/L of the test item. Duration of the test was 96 h. 7 test organisms were exposed to the limit concentration and the control. Water quality parameters pH-value, temperature and oxygen-saturation measured after 0, 24, 48, 72 and 96 h were determined to be within the acceptable limits.
As the test item is highly insoluble in water, no suitable method for determination of the test item could be established and no analytical determination was carried out. All effect values of the test item are given based on the nominal concentration. The acute toxicity of the test item is summarised in the following table:
Table 1: LC-Values with 95 % Confidence Intervals
based on nominal concentration
Test duration [h]
LC50
p = 95 %
24
> 1.00 mg/L
not applicable
48
> 1.00 mg/L
not applicable
72
> 1.00 mg/L
not applicable
96
> 1.00 mg/L
not applicable
LC100 =
> 1.00 mg/L
Lowest tested concentration level
with 100 % mortality after 96 h
LC0 =
1.00 mg/L
Highest tested concentration level
with 0 % mortality after 96 h
Referenceopen allclose all
Description of key information
RA from PR208
The acute toxicity of the test item to fish (zebrafish) was determined according to OECD-Guideline for Testing of Chemicals No. 203 (1992).
As the test item is highly insoluble in water, no suitable method for determination of the test item could be established and no analytical determination was carried out.
In this study the test item did not cause any effects to zebrafish after 96 h when tested a saturated solution with a nominal concentration level of 1.00 mg/L. The LC0 (0 – 96 h) was 1.00 mg/L.
Key value for chemical safety assessment
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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