Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 614-585-0 | CAS number: 68551-65-5
- 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

Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to microorganisms, other
- Remarks:
- Study was a toxicity control conducted as part of a CO2 evolution test in accordance with OECD Guideline 301B.
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 10 September 2012 to 22 November 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- The analogue approach is used for the hazard assessment of toxicological endpoints for the registration of the target substance trimethylolpropane ricinoleate (CAS 68551-65-5) based on generation of different breakdown/metabolic products, resulting not only in similar physical and biological systems (Scenario 2 of the Read-Across Assessment Framework (RAAF, ECHA, 2015) but also consequently in similar physico-chemical, environmental fate and ecotoxicological properties. The source compounds are fatty acids, C16-18 and C18-unsatd., esters with pentaerythritol (CAS 85711-45-1) and pentaerythritol ricinoleate (CAS 78-22-8). It is proposed that the different alcohols resulting from ester hydrolysis of the source compounds and the target substance will not result in significant variation in environmental or biological effects.
Neither target nor source compounds are classified for hazardous effects associated with aquatic toxicity. The use of reliable experimental data, all evaluated as reliable according to Klimisch scores of 1 or 2, to estimate the ecotoxicity of the registered substance is adequate for the purposes of fulfilling the data requirements of registration and classifying potential hazards. Similar grouping into categories has been accepted by other regulatory agencies (U.S. EPA, 2010; U.S. FDA for food notifications). Thus, this read-across approach is adequate for the purposes of risk assessment and classification and labeling. - Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- other:
- Version / remarks:
- According to OECD 301B and EU C.4-C Toxicity test performed as part of a ready biodegradability CO2 evolution test performed according to OECD 301B and EU C.4-C
- Deviations:
- no
- Principles of method if other than guideline:
- Toxicity test performed as part of a ready biodegradability CO2 evolution test performed according to OECD 301B and EU C.4-C
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- The test substance is listed as Fatty acids, C16-18 and C18-unsatd., esters with pentaerythritol. The test substance is a yellow to amber colored liquid. The test substance was obtained from the Sponsor, Oleon NV and stored in a tightly closed vessel at room temperature in dry conditions.
- Analytical monitoring:
- yes
- Vehicle:
- no
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- Activated sludge from a biologic sewage treatment plant treating mostly domestic sewage was used. The sludge was taken from the activation basin of the ESN (Stadtentsorgung Neustadt) sewage treatment plant, Im Altenschemel, NW-Lachen-Speyerdorf on 19 October 2012. The sludge was filtrated, washed with tap water twice, then washed with and re-suspended in test medium. It was then aerated for > 12 hours.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 28 d
- Nominal and measured concentrations:
- A toxicity control, containing the test item at a nominal concentration of 26.7 mg/L and aniline at a nominal concentration of 25.3 mg/L corresponding to a combined total of 40.4 mg carbon/L was prepared to assess any toxic effect of the test item on the sewage sludge micro-organisms used in the test.
- Reference substance (positive control):
- yes
- Remarks:
- Aniline.
- Key result
- Duration:
- 14 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 26.7 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: inhibition of CO2 evolution.
- Details on results:
- At a test substance concentration of 26.7 mg/L and a reference substance concentration of 25.3 mg aniline /L, the toxicity control attained 61% degradation after 14 days, thereby confirming that the test substance did not exhibit an inhibitory effect on the sewage treatment micro-organisms used in the test (i.e., test substance and reference substance attained ≥ 25% degradation by Day 14 for the test substance to be considered as non-inhibitory).
- Validity criteria fulfilled:
- yes
- Remarks:
- IC content <1% (protocol ≤ 5%); CO2 emitted by controls 14.0 mg/L (protocol <70 mg/L; difference replicates 14.5% (protocol ≤20 %); degradation positive control >60% at 11 d (protocol ≤14 d), degradation toxicity d 14, 61% (protocol > 25%).
- Conclusions:
- The test substance is considered as not toxic towards the inoculum at a concentration of 26.7 mg/L. Degradation in the toxicity flask was 61% after 14 days. The guideline indicates that the test item can be considered as toxic towards the inoculum if degradation in the toxicity flask is below 25% after 14 days. Therefore, the NOEC = 26.7 mg/L.
Reference
Description of key information
The key study was a toxicity control as part of a CO2 evolution test conducted on an analogue substance in accordance with OECD Guideline 301B. The test substance was shown to be non-inhibitory toward the inoculum at a concentration of 26.7 mg/L. Degradation in the toxicity flask was 61% after 14 days. Therefore, the NOEC was reported as = 26.7 mg/L.
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 26.7 mg/L
Additional information
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.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.