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EC number: 272-038-8 | CAS number: 68649-95-6
- 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 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:
- April 11, 1988 - April 22, 1988
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well described study, although not GLP, performed according to OECD 203, with the single deviation of no analytical measurements. This deviation does not invalidate the study.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Deviations:
- yes
- Remarks:
- No analytical confirmation of concentrations of test compound in test solutions.
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Stock solutions were prepared by mechanical dissolving (Ultra-Turrax) of the test substance in the required volume of deionised water. This stock solution was transferred into the test medium of one glass tank 2 hours before the start of the test (i.e. the addition of the fish, t=0 h). In the meantime, until the fish were transferred, the contents of each glass tank were mixed thoroughly using a mechanical stirrer in order to facilitate the dissolving and/or dispersing of the test sample.
- Eluate: not relevant
- Differential loading: not relevant
- Controls: controls were untreated
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): not relevant
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)):not relevant
- Evidence of undissolved material (e.g. precipitate, surface film, etc): The following was reported: "In the preparation of the different test batches …. It could be observed that charging the test medium with the test substance led to a dispersion slowly settling up in the course of the test period.” - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: Brachydanio rerio (zebra fish)
- Strain: -
- Source: West Aquarium GmbH & Co. KG, D-3422 Bad Lauterberg, Germany
- Age at study initiation (mean and range, SD): 2 months
- Length at study initiation (length definition, mean, range and SD): 2.0 ± 1.0 cm
- Weight at study initiation (mean and range, SD): no data
- Method of breeding: no data
- Feeding during test: unfed from 24 h prior to the start of the test
- Food type: not relevant
- Amount: not relevant
- Frequency: not relevant
ACCLIMATION
- Acclimation period: 13 days
- Acclimation conditions (same as test or not): yes
- Type and amount of food: Tetra Min® Hauptfutter
- Feeding frequency: twice daily
- Health during acclimation (any mortality observed): no mortality
QUARANTINE (wild caught): not relevant
- Duration: not relevant
- Health/mortality: not relevant - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Post exposure observation period:
- Not relevant.
- Hardness:
- Not measured during study
- Test temperature:
- Overall range during the test 21.2-23.5°C
- pH:
- Overall range during the test 7.7-7.8
- Dissolved oxygen:
- Overall range during the test >85% of saturation
- Salinity:
- Not relevant
- Nominal and measured concentrations:
- Nominal concentrations were 0, 100, 153, 244, 391, 625 and 1000 mg/L.
The nominal concentrations were not verified by chemical analysis. - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass tank
- Type (delete if not applicable): closed with glass plate allowing free air exchange
- Material, size, headspace, fill volume: glass, length 300 mm, width 200 mm, height 220 mm, volume 13.2 L, fill volume 10 L
- Aeration: yes, 1-3 bubbles per second
- Type of flow-through (e.g. peristaltic or proportional diluter): not relevant
- Renewal rate of test solution (frequency/flow rate): not relevant (static test)
- No. of organisms per vessel: ten
- No. of vessels per concentration (replicates): one
- No. of vessels per control (replicates): one
- No. of vessels per vehicle control (replicates): not relevant
- Biomass loading rate: no data
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted water was prepared according to Annex 2 of OECD 203; deionised water used for its preparation was taken from the delivery system of the laboratory.
- Total organic carbon: no data
- Particulate matter: no data
- Metals: no data
- Pesticides: no data
- Chlorine: no data
- Alkalinity: 0.8 mmol/L
- Ca/mg ratio: 4:1
- Conductivity: no data
- Culture medium different from test medium: no
- Intervals of water quality measurement: pH, oxygen and temperature were measured at 0, 1, 24, 48, 72 and 96 hours.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: no data
- Light intensity: no data
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): mortality and fish behavior were observed at 0, 1, 24, 48, 72 and 96 hours.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.5-1.6
- Justification for using less concentrations than requested by guideline: not relevant
- Range finding study: no
- Test concentrations: not relevant
- Results used to determine the conditions for the definitive study: not relevant - Reference substance (positive control):
- no
- Duration:
- 96 h
- Dose descriptor:
- LC0
- Effect conc.:
- 153 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Based on slowly settling dispersions, no chemical analysis of test substance concentrations.
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 198 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Based on slowly settling dispersions, no chemical analysis of test substance concentrations.
- Duration:
- 96 h
- Dose descriptor:
- LC100
- Effect conc.:
- 244 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Based on slowly settling dispersions, no chemical analysis of test substance concentrations.
- Key result
- 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: Based on approximate solubility limit of test substance in test medium.
- Details on results:
- - Behavioural abnormalities: not reported.
- Observations on body length and weight: no data
- Other biological observations: no data
- Mortality of control: 0%
- Other adverse effects control: no data
- Abnormal responses: no data
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: see above.
- Effect concentrations exceeding solubility of substance in test medium: yes (see below) - Results with reference substance (positive control):
- not relevant
- Reported statistics and error estimates:
- The LC50 (198 mg/L) was determined graphically by linear extrapolation using the LC0 (153 mg/L) and the LC100 (244 mg/L).
- Sublethal observations / clinical signs:
At all observation times (24, 48, 72 and 96 hours), mortality was 0% in the control and in the test solutions up to and including 153 mg/L, and 100% at 244-1000 mg/L. It was not reported whether any sublethal effects were noted.
Evaluation.
The reported LC50 was 198 mg/L. The test solutions were dispersions, which were observed to be slowly settling up in the course of the test period. The actual concentrations were not confirmed by chemical analysis. All tested concentrations were far above the solubility limit of the test material in water, which is <1 mg/L. The solubility limit in reconstituted test medium may be even less than that in water. Due to the fact that the test solutions were slowly settling dispersions far in excess of the solubility limit, the concentrations of which were not analytically determined, there is no information about the actual concentrations to which the test fish were exposed during the study. However, due to the method of preparation of the test solutions (thorough mixing of stock using Ultra-Turrax mixer, addition of stock to test water, followed by 2 hours of thorough mixing using a mechanical stirrer), it is sufficiently certain that the solubility limit of the test substance in the test water was achieved in all test solutions. Since at 100 and 153 mg/L no fish mortality occurred, the conclusion of the study is that the LC50 is in excess of the solubility limit. The actual LC50 will be one or two orders of magnitude higher, based on the results of the present test. The mortality at 244 mg/L and above is likely to be due to physical effects of the test material (an oil), which above a certain threshold will for example impair the functioning of the gills.
- Validity criteria fulfilled:
- yes
- Remarks:
- see above
- Conclusions:
- Fish acute toxicity test in Brachydanio rerio according to OECD 203: LC50 in excess of the solubility limit (hence in excess of about 1 mg/L); LC50 for exposure to dispersed test material 198 mg/L (no analytical verification of test substance concentrations).
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- April 11, 1988 - April 22, 1988
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well described study, although not GLP, performed according to OECD 203, with the single deviation of no analytical measurements. This deviation does not invalidate the study.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Deviations:
- yes
- Remarks:
- No analytical confirmation of concentrations of test compound in test solutions.
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Stock solutions were prepared by mechanical dissolving (Ultra-Turrax) of the test substance in the required volume of deionised water. This stock solution was transferred into the test medium of one glass tank 2 hours before the start of the test (i.e. the addition of the fish, t=0 h). In the meantime, until the fish were transferred, the contents of each glass tank were mixed thoroughly using a mechanical stirrer in order to facilitate the dissolving and/or dispersing of the test sample.
- Eluate: not relevant
- Differential loading: not relevant
- Controls: controls were untreated
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): not relevant
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)):not relevant
- Evidence of undissolved material (e.g. precipitate, surface film, etc): The following was reported: "In the preparation of the different test batches …. It could be observed that charging the test medium with the test substance led to a dispersion.” - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: Brachydanio rerio (zebra fish)
- Strain: -
- Source: West Aquarium GmbH & Co. KG, D-3422 Bad Lauterberg, Germany
- Age at study initiation (mean and range, SD): 2 months
- Length at study initiation (length definition, mean, range and SD): 2.0 ± 1.0 cm
- Weight at study initiation (mean and range, SD): no data
- Method of breeding: no data
- Feeding during test: unfed from 24 h prior to the start of the test
- Food type: not relevant
- Amount: not relevant
- Frequency: not relevant
ACCLIMATION
- Acclimation period: 13 days
- Acclimation conditions (same as test or not): yes
- Type and amount of food: Tetra Min® Hauptfutter
- Feeding frequency: twice daily
- Health during acclimation (any mortality observed): no mortality
QUARANTINE (wild caught): not relevant
- Duration: not relevant
- Health/mortality: not relevant - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Post exposure observation period:
- Not relevant.
- Hardness:
- Not measured during study
- Test temperature:
- Overall range during the test 21.2-23.6°C
- pH:
- Overall range during the test 7.7-7.9
- Dissolved oxygen:
- Overall range during the test >85% of saturation
- Salinity:
- Not relevant
- Nominal and measured concentrations:
- Nominal concentrations were 0, 100, 153, 244, 391, 625 and 1000 mg/L.
The nominal concentrations were not verified by chemical analysis. - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass tank
- Type (delete if not applicable): closed with glass plate allowing free air exchange
- Material, size, headspace, fill volume: glass, length 300 mm, width 200 mm, height 220 mm, volume 13.2 L, fill volume 10 L
- Aeration: yes, 1-3 bubbles per second
- Type of flow-through (e.g. peristaltic or proportional diluter): not relevant
- Renewal rate of test solution (frequency/flow rate): not relevant (static test)
- No. of organisms per vessel: ten
- No. of vessels per concentration (replicates): one
- No. of vessels per control (replicates): one
- No. of vessels per vehicle control (replicates): not relevant
- Biomass loading rate: no data
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted water was prepared according to Annex 2 of OECD 203; deionised water used for its preparation was taken from the delivery system of the laboratory.
- Total organic carbon: no data
- Particulate matter: no data
- Metals: no data
- Pesticides: no data
- Chlorine: no data
- Alkalinity: 0.8 mmol/L
- Ca/mg ratio: 4:1
- Conductivity: no data
- Culture medium different from test medium: no
- Intervals of water quality measurement: pH, oxygen and temperature were measured at 0, 1, 24, 48, 72 and 96 hours.
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: no data
- Light intensity: no data
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): mortality and fish behavior were observed at 0, 1, 24, 48, 72 and 96 hours.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.5-1.6
- Justification for using less concentrations than requested by guideline: not relevant
- Range finding study: no
- Test concentrations: not relevant
- Results used to determine the conditions for the definitive study: not relevant - Reference substance (positive control):
- no
- Duration:
- 96 h
- Dose descriptor:
- LC0
- Effect conc.:
- 153 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Based on dispersions of the test material, no chemical analysis of test substance concentrations.
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 479 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Based on dispersions of the test material, no chemical analysis of test substance concentrations.
- Duration:
- 96 h
- Dose descriptor:
- LC100
- Effect conc.:
- 625 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Based on dispersions of the test material, no chemical analysis of test substance concentrations.
- Key result
- 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: Based on approximate solubility limit of test substance in test medium.
- Details on results:
- - Behavioural abnormalities: not reported.
- Observations on body length and weight: no data
- Other biological observations: no data
- Mortality of control: 0%
- Other adverse effects control: no data
- Abnormal responses: no data
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: see above.
- Effect concentrations exceeding solubility of substance in test medium: yes (see below) - Results with reference substance (positive control):
- not relevant
- Reported statistics and error estimates:
- The reported LC50 (390 mg/L) was determined graphically by linear extrapolation using the LC0 (244 mg/L) and the LC100 (625 mg/L). This approach is considered to be inaccurate since the data point for 391 mg/L with 20% mortality is ignored. Based on graphical estimation with linear extrapolation between the data points of 391 mg/L (20% mortality) and of 625 mg/L with 100% mortality, the LC50 is estimated to be 479 mg/L.
- Sublethal observations / clinical signs:
After 96 hours, mortality was 0% in the control and in the test solutions up to and including 244 mg/L, 20% at 391 mg/L and 100% at 625 and 1000 mg/L. It was not reported whether any sublethal effects were noted.
Evaluation.
The LC50 was 479 mg/L. The test solutions were dispersions, and the actual concentrations were not confirmed by chemical analysis. All tested concentrations were far above the solubility limit of the test material in water, which is <1 mg/L. The solubility limit in reconstituted test medium may be even less than that in water. Due to the fact that the test solutions were slowly settling dispersions far in excess of the solubility limit, the concentrations of which were not analytically determined, there is no information about the actual concentrations to which the test fish were exposed during the study. However, due to the method of preparation of the test solutions (thorough mixing of stock using Ultra-Turrax mixer, addition of stock to test water, followed by 2 hours of thorough mixing using a mechanical stirrer), it is sufficiently certain that the solubility limit of the test substance in the test water was achieved in all test solutions. Since at 100-244 mg/L no fish mortality occurred, the conclusion of the study is that the LC50 is in excess of the solubility limit. The actual LC50 will be one or two orders of magnitude higher, based on the results of the present test. The mortality at 391 mg/L and above is likely to be due to physical effects of the test material (an oil), which above a certain threshold will for example impair the functioning of the gills.
- Validity criteria fulfilled:
- yes
- Remarks:
- see above
- Conclusions:
- Fish acute toxicity test in Brachydanio rerio according to OECD 203: LC50 in excess of the solubility limit (hence in excess of about 1 mg/L); LC50 for exposure to dispersed test material 479 mg/L (no analytical verification of test substance concentrations).
Referenceopen allclose all
Description of key information
No acute toxicity observed at levels up to the water solubility (2 studies in accordance with OECD 203)
Key value for chemical safety assessment
Additional information
All the tested concentrations in the 2 studies were far above the water solubility limit of the substance. The mortality observed at the higher concentrations is due to physical effects of the material (an oil), which above a certain threshold will impair the functioning of the gills.
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