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EC number: 688-332-8 | CAS number: 199119-58-9
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
Description of key information
Koc (adsorption) ranged from 119 to 584, kf (adsorption) ranged from 4.09 to 20.75, Koc (desorption) ranged from 164 to 850, kf (desorption) ranged from 1.16 to 30.2295/36/EC Annex I: 7.1 & 7.1.2, , Brandelli, 2000.
Koc (desorption) ranged from 32.3 to 116.2 on day 0 and between 237.5 and 7906.3 on day 85, EPA 163-1, Lowery, 2000.
Koc (adsorption) average 79, Koc (desorption) ranged from 29 to 147, average 121, Koc (desorption) ranged from 103 to 2809, average 121, EPA 163-1, Schwartz, 1999.
The KOC Adsorption value used in the risk assessment was calculated as the arithmetic mean of the 3 soils in Brandelli (2000): 119, 584 and 417 l/kg and the 5 soils from the Schwartz study (1999): 78, 29, 147, 33, 110 and give a KOC of 190 L/kg.
Key value for chemical safety assessment
- Koc at 20 °C:
- 190
Additional information
Three studies have been provided on a weight of evidence basis to address the adsorption, desorption capacity of the test material. Brandelli (2000), Lowery (2000) and Schwartz (1999) determined the Koc values for both adsorption and desorption via the batch equilibrium method.
Brandelli (2000) determined the Koc and kf (Freundlich adsorption constants) of the test material in three representative soils. Adsorption constants ranged from Koc 119 to 584 and kf 4.09 to 20.75, desorption constants ranged from Koc 164 to 850 and kf 1.16 to 30.22. Lowery (2000) determined the Koc values for desorption in five representative soils, assessing the effect of increasing time. On Day 0 Koc values ranged from 32.3 to 116.2 in comparison to Day 85 where Koc values ranged from 237.5 to 7906.3. Schwartz (1999) determined the Koc values for both adsorption and desorption in five representative soil samples. Adsorption values ranged from Koc 29 to 147, with an average of 79, desorption values ranged from Koc 103 to 2809, with an average of 121.
All three studies were performed according to GLP and standardised guidelines, with a high level of reporting and have thus been assigned a reliability score of 1 in line with the principles for assessing data quality set out by Klimisch (1997). All studies are considered to be reliable, relevant and adequate for risk assessment purposes.
[LogKoc: 2.28]
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