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Diss Factsheets
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EC number: 200-312-9 | CAS number: 57-10-3
- 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
Palmitic acid is readily biodegradable
Key value for chemical safety assessment
Additional information
Palmitic acid was tested according to the ISO 10708 (BODIS test)
which is apparently similar to the “closed bottle test”, OECD 301 D.
Three replicates with palmitic acid at concentrations of 100 mg/L COD
were incubated with non-adapted activated sludge. The oxygen consumption
was monitored during the 28 day test period. The results clearly showed
that palmitic acid was degraded by 65% in average at day 28 (Börner,1994).
According to the opinion of the SCIENTIFIC COMMITTEE ON
HEALTH AND ENVIRONMENTAL RISKS on “Compatibility of the ISO
standard 10708 (biodegradability test method) with the ultimate
biodegradability requirements imposed through Annex III of Regulation
648/2004 of Parliament and of the Council”, the BODIS-Test/ISO 10708
shows the same variability and biodegradation results obtained with
other OECD screening tests (SCHER, 2005). Since the pass criterion of
60% degradation within 28 days of the ISO 10708 is consistent with those
obtained with the OECD ready biodegradability methods, palmitic acid can
be regarded as readily biodegradable.
The well anaerobic biodegradability of palmitic acid is shown in
the following tests.
Wierich (1992) showed in an anaerobic biodegradation study with 98% pure
palmitic acid according to ECETOC Technical Report no 28 (today ISO
11734) a 77% degradation in 69 days.
The anaerobic degradation of palmitic acid was investigated by Nuck and Federle (1995) in an mixture of anaerobic sewage sludge and mineral salts. The radioactive labeled test substance was monitored for the production of labeled carbon dioxide and methane over the time (30 d). Palmitic acid was significantly mineralized: At test end 67.5% of the labeled test substance was recovered as carbon dioxide and 20.9% as methane. In sum, palmitic acid was mineralized in sludge up to 88.4% under anaerobic conditions within 30 days.
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