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EC number: 906-627-4 | CAS number: -
- 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 aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Non-GLP guideline study without analytical test item concentration verification
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- no
- Remarks:
- The study was not performed according to GLP. However, the quality of the test carried out in this laboratory is highly reliable, with experimental conditions rigorously similar to those recommended in the OECD guidelines.
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Great waterflea
- Source: BIOAGRI Ambiental - Laboratorio de Analise de Ecotoxicidade
- Age at study initiation (mean and range, SD): less than 24 hours
- Feeding during test: no
ACCLIMATION
- Type and amount of food: P. subcapitata
- Feeding frequency: daily 10E6 cells per daphnid - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 237 mg/L CaCO3
- Test temperature:
- 19.3 -19.9 mg O2/L
- pH:
- 7.49 - 7.92
- Dissolved oxygen:
- 6.46 - 8.47 mg O2/L
- Nominal and measured concentrations:
- Nominal initial concentrations: control, 125, 250, 500, 1000, 2000 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Type (delete if not applicable): closed
- Material, size, headspace, fill volume: borosilicate glass, 120 mL, completely filled
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 2
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: M4 medium
- Intervals of water quality measurement: after 0 and 48 hours
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 24 hour darkness
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): mobility
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2 - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 366.02 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CL: 326.28 - 410.61 mg/L
- Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- EC50: 1.39 mg/L after 24 hours of exposure (95% CL: 1.17 - 1.64 mg/L) - Executive summary:
The acute toxicity of the reaction mass to daphnia magna was assessed in an experimental study according to OECD guideline 202 (Daphnia acute immobilization test). The test organisms were exposed the nominal initial concentrations of 0, 125, 250, 500, 1000, 2000 mg/L (test item) for 48 h and the immobility of the test organisms was observed during the test period. As reference substance potassium dichromate was used. The EC 50 (24 h) for the reference substance was 1.39 mg/l. The EC50 (48 h) for the test item was 366.02 mg/l.
Reference
Description of key information
The EC50 (48h) for the reaction mass was 366.02 mg/l. Different values for the single components were achieved.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Dose descriptor:
- EC50
- Effect concentration:
- 366.02 mg/L
Additional information
The acute toxicity of the reaction mass to aquatic invertebrates was assessed in an experimental study according to OECD 202 (Rhodia, 2009). The test organisms were exposed to the nominal initial concentrations of 0, 125, 250, 500, 1000, 2000 mg/L (test item) for 48 h and the immobility of the test organisms was observed during the test period. As reference substance potassium dichromate was used. The EC 50 (24 h) for the reference substance was 1.39 mg/l. The EC50 (48 h) for the test item was 366.02 mg/l.
In two published studies the acute toxicity of the singel component cyclohexanone to daphnia magna (Bringmann 1977,1982) was assessed over 24 h. The EC 50(24h) was determined for 800 and 820 mg/l.
The acute aquatic toxicity of the second component cyclohexanol was assessed in a GLP study according to OECD guideline 202. Analysis of the freshly prepared test concentrations at 0 and 24 hours showed the measured test concentrations to range from 81% to 107% of the nominal values. However, analysis of the old or expired test preparations sampled at 24 and 48 hours showed a marked decline in the measured test concentrations ranging from 49% to 105% of nominal. These results were in line with the preliminary stability analyses indicating that the test solutions were unstable under the test conditions employed. Due to the volatile nature of the test item, losses via this route are possible. After 48 h an EC50 of 17 mg/l was identified referred to the nominal concentrations (SafePharm, 2003).
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