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EC number: 430-110-8 | CAS number: 183476-82-6
- 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 aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- July 16 - November 02, 2008
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study has been performed according to OECD and EC guidelines and according to GLP principles. Study performed without analytical support.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- no
- Principles of method if other than guideline:
- ISO 6341 15 (Water quality - Determination of the Inhibition of the Mobility of Daphnia magna Straus (Cladocera, Crustacea))
- GLP compliance:
- yes (incl. QA statement)
Test material
- Details on test material:
- - Name of test material (as cited in study report): Nikkol VC-IP
- Substance type: Colourless liquid (determined at NOTOX)
- Physical state: Liquid
- Stability under test conditions: stability in water unknown
- Storage condition of test material: At room temperature in the dark
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not applicable.
Sampling and analysis
- Analytical monitoring:
- no
- Details on sampling:
- Not applicable.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- Preparation of test solutions started with a loading rate of 100 mg/l. This solution was stirred for 24 hours, which resulted in a slightly hazy
dispersion containing undissolved material and an oily-like floating layer on the surface. The dispersion was consequently left to stabilise for ~ 30
minutes after which the middle fraction was collected and, in order to remove the majority of non-dissolved material, filtered through a glass-filter
(Schleicher & Schuell GF92; in the final combined limit/range-finding test). The lower test concentrations were prepared by subsequent dilution of the filtrate in test medium. The final test solutions were all clear and colourless.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Source: In-house laboratory culture with a known history.
- Age at study initiation (mean and range, SD): < 24 hours
- Method of breeding: With newborn daphnids, i.e. less than 3 days old, by placing about 250 of them into 5 litres of medium in an all-glass culture
vessel.
- Feeding during test: no feeding
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- No post exposure observations.
Test conditions
- Hardness:
- 180 mg/l expressed as CaCO3
- Test temperature:
- 19.4 - 20.7 °C
- pH:
- 7.9 - 8.1 (measured)
- Dissolved oxygen:
- 8.8-9.0 (measured) mg/l
- Nominal and measured concentrations:
- Nominal 1.0, 10 and 100% of a glass-filter filtered solution prepared at a nominal loading rate of 100 mg/l.
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 ml, all-glass
- Aeration: No aeration of the test solutions
- No. of organisms per vessel: 5 per vessel containing 80 ml of test solution
- No. of vessels per concentration (replicates): 4 for the highest concentration; 2 each for the lower concentrations
- No. of vessels per control (replicates): 4 each for the control
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Adjusted ISO medium
- Total organic carbon: Unknown
- Culture medium different from test medium: yes, for culturing M7 medium is used
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: 16 hours daily
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : EC50 based on immobility (including mortality) daily
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 10
- Range finding study: study was a combined limit/range finding test
- Test concentrations: Nominal 1.0, 10 and 100% of a glass-filter filtered solution prepared at a nominal loading rate of 100 mg/l. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- other: > solubility in testmedium
- Nominal / measured:
- nominal
- Basis for effect:
- mobility
- Remarks on result:
- other: Solubility in medium is unknown and solubility in water is < 0.09 mg/l.
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- < 0.09 mg/L
- Nominal / measured:
- nominal
- Basis for effect:
- mobility
- Remarks on result:
- other: Solubility in medium is unknown and solubility in water is < 0.09 mg/l.
- Details on results:
- Under the conditions of the present study NIKKOL VC-IP caused no immobilisation of daphnids after 24 hours of exposure. After 48 hours of
exposure 75% of daphnids were immobilized in the filtered solution prepared at a loading rate of 100 mg/l. In the lower treatments (1 and 10 % dilutions of a filtered solution prepared at a loading rate of 100 mg/L) no daphnids were immobilised. - Results with reference substance (positive control):
- - Results with reference substance valid: Yes
- Immobility after 48h: 0% at 0.10 mg/l; 0% at 0.18 mg/l; 5% at 0.32 mg/l; 15% at 0.56 mg/l; 100% at 1.0 and 1.8 mg/l
- EC50/LC50: 48h-EC50 was 0.62 mg/l with a 95% confidence interval between 0.53 and 0.77 mg/l. - Reported statistics and error estimates:
- No data.
Any other information on results incl. tables
Table Incidence of immobility in the final combined limit/range-finding test
Test group Nikkol VC-IP (% filtrate)1 |
Vessel number |
Number Daphnia exposed |
Response at 24 h |
Response at 48 h |
||
number |
Total % |
number |
Total % |
|||
control |
A B C D |
5 5 5 5 |
0 0 0 0 |
0 |
0 0 0 0 |
0 |
1.0 |
A B |
5 5 |
0 0 |
0 |
0 0 |
0 |
10 |
A B |
5 5 |
0 0 |
0 |
0 0 |
0 |
100 |
A B C D |
5 5 5 5 |
0 0 0 0 |
0 |
3 4 4 4 |
75 |
1. Test groups represent dilutions of a glass-filter filtered loading rate of 100 mg/l.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Under the conditions of the present study NIKKOL VC-IP caused no immobilisation of daphnids after 24 hours of exposure. After 48 hours of
exposure 75% of daphnids were immobilized in the filtered solution prepared at a loading rate of 100 mg/l. In the lower treatments no daphnids were
immobilised. The 24-hour EC50 is expected to be higher than the maximum solubility and the 48-hour EC50 is < 0.09 mg/l.
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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