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EC number: 700-151-9 | CAS number: 1101874-33-2
- 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:
- 16-Nov-2009 to 20-Nov-2009
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was performed in accordance with internationally-accepted test guidelines and Good Laboratory Practice standards. However, the test substance could not be quantified in the WAF. Therefore, this study is classified as acceptable with restrictions.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
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:
- other: EU Commission Directive 92/69/EEC, C.2, Acute Toxicity for Daphnia. Commission Regulation (EC) No 440/2008, C.2, Acute Toxicity for Daphnia. Also, design and execution of the study were based in part on OECD document 23, Guidance Document on Aquatic To
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
Reference
- Name:
- Unnamed
- Type:
- Constituent
- Details on test material:
- - Name of test material (as cited in study report): MTDID 8191
- Substance type: UVCB material
- Physical state: Yellowish viscous liquid
- Concentration of oligomers: ≥99.0%
- Purity test date: 21 January 2010
- Lot/batch no.: MK 12/048
- Expiration date of the lot/batch: 27-Jan-2010
- Stability under test conditions: Not reported
- Storage condition of test material: In the refrigerator at about 4 °C
- Other:
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
No surrogate
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling method: After manual shaking, withdrawal of aliquot and dilution with an equal volume of acetonitrile.
- Sample storage conditions before analysis: Samples analyzed immediately
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Dispersions were stirred for 96 hours at room temperature in the dark to dissolve a maximum amount of the test item in the dispersion. After stirring, the dispersions were left to settle for 1 hour and the clear phase of each dispersion was then filtered through a membrane filter (Schleicher & Schuell, Type NC45, pore size 0.45 µm). The undiluted filtrates were tested as water accomodated fractions (WAFs).
- Evidence of undissolved material (e.g. precipitate, surface film, etc): None
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain:Daphnia magna Straus, clone 5
- Source: internal strain originally obtained from University of Sheffield, UK in 1992
- Age at study initiation (mean and range, SD): 6-24 hours
- Feeding during test: No
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 250 mg/L-CaCO3
- Test temperature:
- 20 °C
- pH:
- 7.8
- Dissolved oxygen:
- 8.4-8.6 mg/L
- Salinity:
- Not reported
- Nominal and measured concentrations:
- nominal concentration, 100 mg/L. Test substance could not be quantified
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL glass beaker
- Type (delete if not applicable): covered with glass plate
- Material, size, headspace, fill volume: 50 mL test medium, ca. 50 mL headspace
- Aeration: none
- Renewal rate of test solution (frequency/flow rate): static test
- No. of organisms per vessel: five
- No. of vessels per concentration (replicates): four
- No. of vessels per control (replicates): four
- Biomass loading rate: 1 organism/10 mL
GROWTH MEDIUM
- Standard medium used: yes, ISO 6341 medium
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: purified water
- Total organic carbon: Not reported
- Particulate matter: Not reported
- Metals: Not reported
- Pesticides: Not reported
- Chlorine: Not reported
- Alkalinity: 0.8 mmol/L
- Ca/mg ratio: 4:1
- Conductivity: Not reported
- Culture medium different from test medium: No
- Intervals of water quality measurement: Not reported
OTHER TEST CONDITIONS
- Adjustment of pH: None
- Photoperiod: 16-hour light to 8-hour dark cycle with a 30-minute transition period
- Light intensity: 520 and 680 Lux during the light period
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Parameter: Immobilization
- Observation intervals: At 24 and 48 hrs
- Criterion: Daphnids not being able to swim within 15 seconds after gentle agitation of the test beaker are considered to be immobilized
TEST CONCENTRATIONS
- Spacing factor for test concentrations: Limit test
- Range finding study: Yes, results not reported (non-GLP) - Reference substance (positive control):
- yes
Results and discussion
Effect concentrations
- Duration:
- 48 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: water accomodated fraction
- Basis for effect:
- mobility
- Remarks on result:
- other: No immobilization was observed in treated vessels or controls during the experiment
- Details on results:
- - Behavioural abnormalities: Not reported
- Observations on body length and weight: Not reported
- Other biological observations: Not reported
- Mortality of control: None
- Other adverse effects control: None
- Abnormal responses: None
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: Test substance could not be quantified in test solutions (LOQ = 1.01 mg/L). The test medium was a clear solution through the 48-hours of exposure.
- Effect concentrations exceeding solubility of substance in test medium: No effect detected at an initial nominal loading of 100 mg/L. - Results with reference substance (positive control):
- For evaluation of the quality of the daphnia clone and the experimental conditions, potassium dichromate is tested as a positive control twice a year. The result of the latest positive control test in September 2009 (48-hour EC50: 1.1 mg/L, study C63680) indicated that the sensitivity of the test organisms was within the internal historical range (48-hour EC50 from 1996 to 2009: 0.53-1.1 mg/L).
- Reported statistics and error estimates:
- No statistics. NOELR and EL50 determined from raw data
Any other information on results incl. tables
Table 2, Effect of the test substance on the mobility ofDaphnia magna | |||||
Loading rate (mg/L) | Number of daphnids tested | Immobilized daphnids after | |||
24 hours | 48 hours | ||||
Number | % | Number | % | ||
Control (0) | 20 | 0 | 0 | 0 | 0 |
100 | 20 | 0 | 0 | 0 | 0 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The NOELR of the test substance under assay conditions was 100 mg/L
- Executive summary:
The test substance (CAS# 1101874-33-2) is a UVCB substance of low water solubility. Therefore, toxicity of the substance to the aquatic invertebrate Daphnia magna was determined in a limit test using a water-accommodated fraction (WAF). No immobilization was observed after 48 hours. Therefore, the no observed effect loading rate was 100 mg/L, and the effective loading rate (50%, or EL50) was >100 mg/L.
The study demonstrates was performed in accordance with internationally-accepted test guidelines and Good Laboratory Practice standards. However, the test substance could not be quantified in the WAF. Therefore, this study is classified as acceptable with restrictions.
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