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EC number: 209-813-7 | CAS number: 593-85-1
- 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
Mobile in soil, low adsorption potential acting as kation
Key value for chemical safety assessment
- Koc at 20 °C:
- 20
Additional information
- Doucette WJ (2000). pp. 141-188 In Handbook of Property Estimation Methods for Chemicals. Boethling RS, Mackay D, eds. Boca Raton, FL, U.S.A.: Lewis Publ
- Hollis JM (1991). Mapping the vulnerability of aquifers and surface waters to pesticide contamination at the national/regional scale. Pesticides in Soils and Water: Current Perspectives (A Walker Ed), BCPC Monograph 47:165-74
- HSDB Hazardous Substances Databank (2008). GUANIDINE, CASRN: 113-00-8, Number: 7603. Last Revision Date: 2008-08 -26, Last Review Date: Reviewed by SRP 5/8/2008, Update History: Complete Update on 2008 -08-26, 38 fields added/edited/deleted, Created 20071213
- McCall PJ, Laskowski DA, Swann RL, Dishburger HJ (1981). Measurement of sorption coefficients of organic chemicals and their use, in environmental fate analysis IN Test Protocols for Environmental Fate and Movement of Toxicants. Proceedings of AOAC Symposium, AOAC, Washington DC, U.S.A:94-109
- Meylan WM et al (1992). Environ Sci Technol 26:1560-7
- O'Neil MJ (2006). The Merck Index. 14th ed. Whitehouse Station, NJ: Merck and Co Inc
- Swann RL, Laskowski DA, McCall PJ, Vanderkuy K, Dishburger HJ (1983). A rapid Method for the Estimation of the Environmental Parameters Octanol Water Partition-Coefficient, Soil Sorption Constant, Water to Air Ratio, and Water Solubility. ISSN 0080-181X Residue Reviews 85:17-28
The relevant part of the submission item Guanidine carbonate is the Guanidine (CAS 113-00-8) as discussed in the section on Environmental fate and pathways above. It is present as the Guanidinium kation (see section Dissociation constant). The carbonate, is considered negligible for the environmental assessment and disregarded in the following discussion
Using a structure estimation method based on molecular connectivity indices (Meylan et al 1992), the Koc of Guanidine can be estimated to be ca. 20 (HSDB 2008). According to classification schemes, this estimated Koc value suggests that Guanidine is expected to have “very high mobility” in soils (McCall et al 1981, Swann et al 1983) or falls into the “Mobile” class (Hollis 1991).
The pKa of Guanidine is 12.5 (O'Neil 2006), indicating that this compound will exist almost entirely as a kation in the environment (HSDB 2008). Kations generally adsorb more strongly to soils containing organic carbon and clay than neutral species (Doucette 2000). Guanidine may thus have greater adsorption and less mobility than its estimated Koc value indicates.
In conclusion the “Mobile” class should be assigned.
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