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EC number: 305-748-4 | CAS number: 95009-22-6
- 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:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- December, 2012 to April, 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study was conducted by a GLP accredited laboratory using OECD Testing Guideline 202.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Cocoa Powder (Low Fat)
- IUPAC Name:
- Cocoa Powder (Low Fat)
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
- Details on test material:
- Test substance name: Cocoa Powder (10 – 12% lipid)
Batch number: ALF092012
Description: Brown solid
Purity: Not applicable – complex mixture
Storage: Room temperature (15 - 30°C), desiccated and protected from light
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
Test solutions
- Vehicle:
- yes
- Details on test solutions:
- Due to the complex nature of the test substance, it was considered that a Water Accommodated Fraction (WAF) approach was the most suitable method of test media preparation. WAFs were prepared by adding a known amount of test substance to a known amount of diluent to give an initial 100 mg/l.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Juvenile Daphnia magna (Straus), less than 24 hours old, were taken from healthy parental laboratory cultures, held and maintained at the test facility. The culture was originally obtained from Smithers Viscient, Shawbury, UK.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- Not provided for the definitive test.
- Test temperature:
- 21.2-21.4°C at the start of the test.
- pH:
- 7.61-7.67 at the start of the test.
- Dissolved oxygen:
- 9.27-9.73 mg/l at the start of the test.
- Nominal and measured concentrations:
- A range-finding/limit test was conducted at nominal concentrations of 1.0, 10 and 100 mg/l loading rate WAF.
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- After 48 hours exposure, no immobilisation was observed at the highest test concentration of 100 mg/l loading rate WAF therefore the EL50 value could not be determined.
Any other information on results incl. tables
Parameter |
Nominal Loading Rate (mg/l) |
|
24 hour |
48 hour |
|
EL50 |
>100 |
>100 |
NOELR |
100 |
100 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- The validity criteria for control immobility (≤10%) and dissolved oxygen (>60% ASV) were both satisified. The test is therefore considered valid.
- Conclusions:
- After 48 hours, the nominal concentration at which no significant (≤10%) dose related immobility occurred was 100 mg/l loading rate WAF. The 48-hour EL50 value was >100 mg/l loading rate WAF. The NOELR was considered to be 100 mg/l loading rate WAF. It is concluded that Cocoa Powder (10 – 12% lipid) was considered not to be toxic to Daphnia magna at 100 mg/l loading rate WAF under the conditions of this test.
- Executive summary:
The potential of the test substance to be acutely toxic to aquatic invertebrates was determined in accordance with the OECD Guideline for Testing of Chemicals 202. The species used in the test was Daphnia magna. Due to the complex nature of the test substance, it was considered that a Water Accommodated Fraction (WAF) approach was the most suitable method of test media preparation. A range-finding/limit test was conducted at nominal concentrations of 1.0, 10 and 100 mg/l loading rate WAF. A control group was also included. The test was conducted under static test conditions. After 48 hours exposure, no immobilisation was observed at the highest test concentration of 100 mg/l loading rate WAF therefore the EL50 value could not be determined. After 48 hours, the nominal concentration at which no significant (≤10%) dose related immobility occurred was 100 mg/l loading rate WAF. The 48-hour EL50 value was >100 mg/l loading rate WAF. The NOELR was considered to be 100 mg/l loading rate WAF. It is concluded that Cocoa Powder (10 – 12% lipid) was considered not to be toxic to Daphnia magna at 100 mg/l loading rate WAF under the conditions of this test.
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