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EC number: 267-636-0 | CAS number: 67905-17-3
- 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:
- calculation (if not (Q)SAR)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data is from computational model developed by USEPA
- Justification for type of information:
- Data is from computational model developed by USEPA
- Qualifier:
- according to guideline
- Guideline:
- other: Modeling database
- Principles of method if other than guideline:
- ECOSAR estimates log Kow values using the US EPA's KOWWIN Program for aquatic toxicity.Toxicity of a chemical was measured on the basis of similarity of structure to chemicals for which the aquatic toxicity has been previously measured by structure-activity relationships (SARs) program based upon the octanol /water partition coefficient (Kow). Data from ECOSAR class,neutral organics was used.
The estimation methods in EPI Suite™ have been developed by government, academic, and private sector researchers over many years and represent some of the best techniques currently available. The intended application domain of EPI Suite is organic chemicals, and inorganic as well as organometallic chemicals generally can be considered outside the domain. - GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- other: Fish
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 96 h
- Reference substance (positive control):
- not specified
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.945 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Based on the QSAR prediction done using the EPI Suite ECOSAR version 1.10, the 96 hours LC50 was estimated to be 0.945 mg/l on fish for test substance with mortality effects.
- Executive summary:
Based on the QSAR prediction done using the EPI Suite ECOSAR version 1.10, the 96 hours LC50 was estimated to be 0.945 mg/l on fish for substance test substance with mortality effects.
Reference
Description of key information
An acute toxicity test was conducted for 96 hrs for assessing the effect of test chemical on Zebra fish (Danio rerio). The test was performed in accordance to OECD guideline No. 203 “Fish Acute Toxicity Test”. Zebra fish (Danio rerio) of average length of 1.87 cm was used as a test organism. Test fishes were kept in the test water under natural conditions along with proper feed and aeration for seven days. Test chemical solution was prepared by dissolving 5000 mg of test chemical in 5000 ml of RO water to get the final concentration of 1000 mg/L. which was then analytically determined. The final solubility value obtained after analytical detection was 0.16 mg/L. The remaining test solutions were prepared by dilution from the above stock solution. Limit test was performed at a test chemical concentration of 0.16 mg/l. The analytical determinations were performed by UV-VIS spectrophotometer for selected test concentration at 0 hour and 96 hours. The concentration of the test chemical being tested and was not within the range of ± 20 %. Therefore, the analysis of the results was based on measured concentration. Test fishes were exposed to test chemical in a 7 lit bowl aquaria containing 4 liters of potable water. The test vessels were placed at a temperature of 21-25°C, pH 7.6, dissolved oxygen 8.3 mg/l and under a photoperiod of 16:8 hr light: dark conditions, respectively. The pH and oxygen values were measured at the beginning of the test and every 24 hours thereafter. The lethal concentration was calculated using the concentration/ percentage response curve. After the 96 hours of exposure, there was no mortality in the control group, and the dissolved oxygen concentration was 93% of the air saturation value, thus meeting the validity criteria. The median lethal concentrations [LC50 (96 h)] for test chemical on Danio rerio (Zebra Fish) was determined to be > 0.16 mg/L.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 0.16 mg/L
Additional information
Experimental studyand predicted data of the target chemical and various supporting weight of evidence studies for its read across substance was reviewed for the short term toxicity to fish end point which is summarized as below:
In an experimental study from study report (2020), an acute toxicity test was conducted for 96 hrs for assessing the effect of test chemical on Zebra fish (Danio rerio). The test was performed in accordance to OECD guideline No. 203 “Fish Acute Toxicity Test”. Zebra fish (Danio rerio) of average length of 1.87 cm was used as a test organism. Test fishes were kept in the test water under natural conditions along with proper feed and aeration for seven days. Test chemical solution was prepared by dissolving 5000 mg of test chemical in 5000 ml of RO water to get the final concentration of 1000 mg/L. which was then analytically determined. The final solubility value obtained after analytical detection was 0.16 mg/L. The remaining test solutions were prepared by dilution from the above stock solution. Limit test was performed at a test chemical concentration of 0.16 mg/l. The analytical determinations were performed by UV-VIS spectrophotometer for selected test concentration at 0 hour and 96 hours. The concentration of the test chemical being tested and was not within the range of ± 20 %. Therefore, the analysis of the results was based on measured concentration. Test fishes were exposed to test chemical in a 7 lit bowl aquaria containing 4 liters of potable water. The test vessels were placed at a temperature of 21-25°C, pH 7.6, dissolved oxygen 8.3 mg/l and under a photoperiod of 16:8 hr light: dark conditions, respectively. The pH and oxygen values were measured at the beginning of the test and every 24 hours thereafter. The lethal concentration was calculated using the concentration/ percentage response curve. After the 96 hours of exposure, there was no mortality in the control group, and the dissolved oxygen concentration was 93% of the air saturation value, thus meeting the validity criteria. The median lethal concentrations [LC50 (96 h)] for test chemical on Danio rerio (Zebra Fish) was determined to be > 0.16 mg/L.
In a prediction done using the EPI Suite ECOSAR version 1.10 (2017), the 96 hours LC50 was estimated to be 0.945 mg/l on fish for substance test substance with mortality effects.
Another Prediction done using Danish QSAR database (2018) in which the average value of both models i.e Leadscope and SciMatics SciQSAR model were presented in Battery model. On the basis of this, 96 hours LC50 was estimated to be 0.44 mg/l on Pimephales promelas for test substance with mortality effects.
In a supporting weight of evidence study from peer reviewed journal (Kuo-HsiungL et al, 2002), short term toxicity test was performed to evaluate the effect of test material to fish Cyprinus carpio. The test animals were fed with yeast in a 224 (diameter), 46 (height)-cm circular plastic pool. Before the experiment, the test organisms were acclimatized in aquaria for 2 weeks under conditions similar to those under which the tests were performed. Four carps of 2 to 6 cm in size, were introduced to each 10-L beaker containing 5 L of different concentrations of test chemical i.e, 10, 50, 100, 200, and 500 mg/l. After 48 h of exposure period, median lethal concentration (LC50) values were calculated by using trimmed Spearman Karber method. The median lethal concentration (LC50) of test material on Cyprinus carpio after 48 h was observed to be 0.022 mg/l.
For the test chemical, another short term toxicity test was performed to evaluate the effect of test material to fish Cyprinus carpio (Kuo-HsiungL et al, 2002). The test procedure and conditions were similar as mentioned above. The median lethal concentration (LC50) of test material on Cyprinus carpio after 48 h was observed to be 0.045 mg/l.
Thus, based on the LC50 value, test chemical can be considered as toxic to aq. algae and thus can be considered to be classified in ‘Aquatic acute/chronic 1 category’ as per CLP classification criteria.
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