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Diss Factsheets
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EC number: 208-754-4 | CAS number: 540-72-7
- 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
According to REACH Annex VIII, section 9.3.1, column 2 "a study does not need to be conducted if based on the physicochemical properties the substance can be expected to have a low potential for adsorption .e.g, the substance has a low octanol water partition coefficient, or the substance and its relevant degradation products decompose rapidly". Ammonium thiocyanate as a representative member of the category is readily biodegradable according to the results of an OECD 301D test. The thiocyanates in this category all have estimated log Kow values less than zero, indicating a low potential for adsorption. However, SCN- can adsorb to soils with a large anion exchange capacity (Fe, Al and Mn oxides, clay minerals), especially at high temperatures. The surfaces of most soil particles have low anion exchange capacity, thus this mechanism would be of minor relevance.
Key value for chemical safety assessment
Additional information
Two studies have been reviewed for adsorption/desorption potential of thiocyanates. The first study (Misra and Misra, 1991) is based on adsorption tests only, with no tests on desorption potential. This study indicates a potential for adsorption for sodium and ammonium thiocyanates. This test is considered not reliable as there are serious doubts about whether equilibrium was reached in the test, and also on the identity of the anion (CNS- vs SCN-). Due to sodium and potassium cations being normally present in the environment, and also for ionizing substances, it is the cations that are normally adsorbed to the humic acids in soils. The second study (Brown and Morra, 1993) shows the importance of organic carbon in providing an energy source for microorganisms that can degrade thiocyanates in soils, especially at temperatures <= 30oC . At temperatures above 40oC, sorption to soils with a large anion exchange capacity may serve to immobilize SCN- in soils. However due to the fact that most soils surfaces have low anion exchange capacity, this mechanism of adsorption is considered less relevant.
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.
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