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Diss Factsheets
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EC number: 203-366-1 | CAS number: 106-14-9
- 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
Biodegradation in water: screening tests
Administrative data
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- Not reported
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study conducted according to accepted guidelines and GLP
- Justification for data waiving:
- other:
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 001
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Deviations:
- not applicable
- Qualifier:
- according to guideline
- Guideline:
- ISO Draft (BOD Test for Insoluble Substances)
- Deviations:
- not applicable
- Principles of method if other than guideline:
- The ISO draft (BOD Test for Insoluble Substances) is based on the closed bottle test (OECD Guideline 301D) and the RDA-Blok-test, previously published (Blok J.: "A repetitive die-away (RDA) test combining several biodegradability test procedures". Int. Biodeterior. Bull. 15 (1979):57-63) and ring-tested by the OECD (1988 ring-test on ready biodegradability).
The purpose of the method is the measurement of the aerobic ultimate biodegradability, preferably of poorly soluble organic compounds in an aqueous medium at a test concentration of 100 mg ThoD/L. The extent of degradation is determined as the ratio of the biochemical oxygen demand (BOD) within 28 d to either ThoD or COD. - GLP compliance:
- yes
Test material
- Reference substance name:
- Castor oil, hydrogenated
- EC Number:
- 232-292-2
- EC Name:
- Castor oil, hydrogenated
- Cas Number:
- 8001-78-3
- IUPAC Name:
- 8001-78-3
- Details on test material:
- - Name of test material (as cited in study report): Edanor P 19 or castor oil, hydrogenated
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
None
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): From a sewage treatment plant from Hochdahl predominantly municipal sewage serving for a population equivalent of approximately 27 000.
- Preparation of inoculum for exposure: After addition of a magnetic stirrer the inoculum was stabilised under laboratory conditions for approximately one week.
- Concentration of sludge: 2.5-3.5 mg/L of test medium - Duration of test (contact time):
- 28 d
Initial test substance concentration
- Initial conc.:
- 100 mg/L
- Based on:
- ThOD/L
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium:
P = 116 mg/L
N = 1.3 mg/L
Na = 86 mg/L
K = 122 mg/L
Mg = 2.2 mg/L
Ca = 9.9 mg/L
Fe = 0.05-0.01 mg/L
- Test temperature: 20-25 degree C when the bottles were incubated in the shaker. The temperature was adjusted to 20 ± 0.5 degree C half an hour before each oxygen measurment.
TEST SYSTEM
- Number of culture flasks/concentration: 3
- Method used to create aerobic conditions: The bottles were aerated with compressed air by means of a sintered glass tube until oxygen saturation was reached.
- Measuring equipment:
The COD was determined in a variant of the ISO method 6060 (closed system with a pressure equaliser / Kelkenberg method, Z.f. wasser und abwasserforschung 8, 146, 1975)
The oxygen determination was performed using a oxygen-electrode (WTW; FRG; microprocessor oximeter OXI 2000 with electrode model TriOxmatic EO 200)
- Test performed in closed vessels: Yes
- Other: The bottles were shaking continously to assure steady state oxygen partitioning between liquid and gas
SAMPLING
- Sampling frequency: Weekly
CONTROL AND BLANK SYSTEM
- Inoculum blank: Yes
Reference substance
- Reference substance:
- acetic acid, sodium salt
Results and discussion
% Degradationopen allclose all
- Parameter:
- % degradation (O2 consumption)
- Value:
- 3
- Sampling time:
- 7 d
- Remarks on result:
- other: None
- Parameter:
- % degradation (O2 consumption)
- Value:
- 28
- Sampling time:
- 14 d
- Remarks on result:
- other: None
- Parameter:
- % degradation (O2 consumption)
- Value:
- 54
- Sampling time:
- 21 d
- Remarks on result:
- other: None
- Parameter:
- % degradation (O2 consumption)
- Value:
- 64
- Sampling time:
- 28 d
- Remarks on result:
- other: None
- Details on results:
- For further details on the result, see Tables 1 and 2 and Figure 1 under "attached background material"
BOD5 / COD results
BOD5 / COD
- Parameter:
- COD
- Value:
- 2 440 mg O2/g test mat.
- Results with reference substance:
- Degradation (calculation based on ThoD):
7 d: 82 %
14 d: 92 %
21 d: 94 %
28: d 95 %
Any other information on results incl. tables
None
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- other: Ultimately biodegradable
- Conclusions:
- Under the test conditions, 64 % of castor oil, hydrogenated was degraded within the 28 d test period. The substance could therefore be considered as ultimately biodegradable.
- Executive summary:
The ultimate biodegradability of the test substance was tested in a 28 d two phase closed bottle test (OECD guideline 301 D) / BODIS-test with GLP compliance. The test represents a modification of the closed bottle test especially suited for poorly soluble compounds.
A defined mineral medium was inoculated with a mixed bacterial inoculum, stabilized under laboratory conditions for 1 week and then spiked with a predetermined amount of test substance. The test vessels were glass bottles with a known volume of aqueous test mixture (2/3) and air (1/3). The bottles were shaken continuously to assure steady state oxygen partitioning between liquid and gas phase. The degradation was followed by weekly measurements of the BOD in the aqueous phase for a 28 d period. One blank control and one reference substance, sodium acetate, were run in parallel for validity purposes. The total oxygen uptake in the flasks was calculated from the measured dissolved oxygen concentration divided by the saturation value at normal conditions and multiplied with the total oxygen content.
Under the test conditions, 64 % of the test substance was degraded within the 28 d test period. The substance could therfore be considered as ultimately biodegradable.
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