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EC number: 200-313-4 | CAS number: 57-11-4
- 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
Link to relevant study record(s)
Description of key information
Readily biodegradable
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
The ready biodegradability of stearic acid (C18, saturated) is assessed in a weight of evidence approach based on the results of the substance on its own and on the results of the closely related read across substance oleic acid (C18, 1 double bond,9-Octadecenoic acid, (Z)-) as well as on QSAR calculations.
Stearic
acid, saturated was tested by Bogers (1989) for ready biodegradability
according to OECD 301B and GLP. At concentrations of 10 and 20 mg/L the
determined degradation values were 72% and 71%, respectively at test
termination (28 d). The pass criterion for ready biodegradability (60%
degradation reached within 10 days once exceeded 10% degradation) was
barely missed. However, the sampling interval was not as narrow as
recommended by the OECD guideline (sampling every second day, followed
by sampling every fifth day) which might have led to the barely missing
of the 10-day window.
The failure of the 10-day window in
biodegradation tests due to the low water solubility/bioavailability as
well as to the inappropriate sampling intervals were already recognized
and discussed within the framework of the SIDS Initial Assessment Report
for the Category “Aliphatic Acids” (OECD, 2009) and judged not to
preclude the ready biodegradability of the fatty acids.
The
analogue substance oleic acid, unsaturated (9-Octadecenoic
acid, (Z)-)
was also assessed for ready biodegradability.
Coenen (1991) conducted a GLP study according to OECD 301B. After 28
days 93% and 75% of oleic acid were biodegraded at concentrations of 10
mg/L and 20 mg/L, respectively und thus passed the 60% degradation
level. Furthermore, at 10 mg/L test substance the 10 day window was met.
According to the criteria for ready biodegradation oleic acid (9-Octadecenoic
acid, (Z)-)
is readily biodegradable. Since the reference substance itself failed
the pass criterion for validity (60% degradation was not reached within
14 d), the study should had been repeated.
Reliable results of the QSAR model BIOWIN v.4.10 (EPI Suite, 2010) predicts ready biodegradability for both substances. This method is based on the application of Bayesian analysis to ready biodegradation data for chemicals, derived collectively from all six OECD301 test methods plus OECD310.
Overall, the substance stearic acid is regarded as readily biodegradable. This judgment is consistent with the hazard assessment presented in the OECD SIDS (2009) for the category “Aliphatic Acids Category” where aliphatic fatty acids with a carbon chain length in the range of C8 – C22 were judged to be readily biodegradable.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.