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EC number: 439-910-1 | CAS number: 93705-66-9
- 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:
- 17 July 1995 to 19 July 1995
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- according to guideline
- Guideline:
- other: Japanese Industrial Standard (JIS K 0102-1993-71.) "Testing methods for industrial waste water".
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- yes
- Remarks:
- HCO-20 and HCO-40
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- HCO-20 and HCO-40 were used as dispersants
- Method: The test material and HC0-20 (20 times amount of the test material) and HC0-40 (20 times amount of the test material) were dissolved in acetone. After acetone was evaporated from it, ion-exchanged water was added to obtain 1000 mg/L of stock solution. - Test organisms (species):
- Oryzias latipes
- Details on test organisms:
- TEST ORGANISM
- Common name: Orange-red killifish
- At reception, fish showing abnormal signs were removed. Then fish were reared according to flow through system for 6 days after an external disinfection.
- Length at study initiation: average 2.6 cm
- Weight at study initiation: average 0.16 g
ACCLIMATION
-Ffish were acclimatised after external disinfections. During the period, abnormal fish were removed. Fish were reared according to flow through system at a temperature of 25 ± 2°C for 19 days. After removing the abnormal fish and performing the external disinfection again, fish were reared according to flow through system for 27 days.
- Fish which had passed the HgCl2-test (Kenji Tabata (1972) Journal of Water and Waste (14) 1297-1303) were subjected to the test. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Test temperature:
- 25 ± 2°C
- pH:
- Initiation: 7.8 - 7.9
Termination: 7.8 - 8.0 - Dissolved oxygen:
- Initiation: 7.6 mg/L
Termination: 6.6 - 6.9 mg/L - Nominal and measured concentrations:
- Nominal: 0.479, 0.638, 0.848, 1.13 and 1.50 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Round glass vessel
- Fill volume: 4L/level
- Renewal rate of test solution (frequency/flow rate): Renewal of test water was performed every 8 - 16 hours
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 1
- No. of vessels per vehicle control (replicates): 1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Underground water pumped up from the ground of the testing laboratory site was used. The water was analysed and measured every 6 months in the laboratory.
- The quality of dilution water was confirmed to meet the ministerial ordinance of the Ministry of Public Welfare (December 21, 1992), the water quality criteria for fisheries (Shadanhozin Nihon Suisansigen Hogokyokai, March 1983), and OECD Guideline for Testing of Chemicals 210, Fish, Early-life Stage Toxicity Test in measured and analysed items. - Reference substance (positive control):
- not specified
- Key result
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 1.18 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Reported statistics and error estimates:
- The 48-hr LC50 value was estimated by Doudoroff method.
- Sublethal observations / clinical signs:
Table 1: Cumulative Mortality
Concentration (mg/L)
Cumulative Mortality (%)
2 Hours
24 Hours
48 Hours
Control
-
0
0
0.479
-
0
0
0.638
-
0
0
0.848
-
0
30
1.13
-
20
40
1.50
-
60
100
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Under the conditions of this study, the 48 hour LC50 value to Oryzias Iatipes was determined to be 1.18 mg/L.
- Executive summary:
The acute toxicity of the test material to fish was investigated in accordance with Japanese Industrial Standard (JIS K 0102-1993-71.) titled "Testing methods for industrial waste water". The testing was performed under GLP conditions.
Oryzias Iatipes (Orange-red killifish) were exposed to the test material for 48 hours in a semi-static test system. Ten fish were treated at each of the following concentrations: 0.479, 0.638, 0.848, 1.13 and 1.50 mg/L.
The 48-hr LC50 value was estimated by Doudoroff method.
Under the conditions of this study, the 48 hour LC50 value was 1.18 mg/L.
Reference
Description of key information
Under the conditions of this study, the 48 hour LC50 value to Oryzias Iatipes was determined to be 1.18 mg/L.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 1.18 mg/L
Additional information
The acute toxicity of the test material to fish was investigated in accordance with Japanese Industrial Standard (JIS K.0102-1993-71.) titled "Testing methods for industrial waste water". The testing was performed under GLP conditions. The study was awarded a reliability score of 2 in accordance with the criteria set forth by Klimisch et al. (1997).
Oryzias Iatipes (Orange-red killifish) were exposed to the test material for 48 hours in a semi-static test system. Ten fish were treated at each of the following concentrations: 0.479, 0.638, 0.848, 1.13 and 1.50 mg/L.
The 48-hr LC50 value was estimated by Doudoroff method.
Under the conditions of this study, the 48 hour LC50 value was 1.18 mg/L.
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