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EC number: 268-103-5 | CAS number: 68002-88-0 This substance is identified by SDA Substance Name: C16-C22 alkyl carboxylic acid and SDA Reporting Number: 21-005-00.
- 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
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
No
study on ready biodegradability is available for fatty acids, C16-22.
Therefore, read across from the key studies of the most relevant
aliphatic fatty acids was performed. According to the Substance Identity
Profile stearic acid (C18), eicosanoic acid (C20) and docosanoic acid
(C22) are the most representative structures for fatty acids, C16-22.
Therefore the data for stearic acid (C18, CAS 143-07-7), oleic acid as
surrogate (C18’, CAS 112-80-1) as well as QSAR predictions on ready
biodegradability of eicosanoic acid (C20, CAS 506-30-9) and docosanoic
acid (C22, CAS 112-85-6) were considered to deduce the biodegradability
of fatty acids, C16-22.
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 small as
recommended by the OECD guideline 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 pass the 60% degradation level. Furthermore, at the lower test concentration of 10 mg/L 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 eicosanoic acid and docosanoic
acid. 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.
These
results are consistent with experimental results published in the HERA
Report for a mixture of C20-C22 aliphatic acids tested according to OECD
301 D. An overall degradation rate of 89% as well as ready
biodegradation was stated for the mixture of C20-C22 aliphatic acids in
the HERA report (a reliability score of 1 is given for the results).
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