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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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
Not acute toxic, no indication for classification
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 1 000 mg/L
Additional information
- Adema DMM (1988). The acute toxicity of Guanidine hydrochloride to Leuciscus idus L. TNO Division of Technology for Society. Report no.: R88/241. Report date: 1988-06-22. [European Chemicals Bureau; IUCLID Dataset, Guanidine chloride (CAS # 50-01-1) p 8 (2000 CD-ROM edition). Available from, as of March 4, 2008: http://esis.jrc.ec.europa.eu/]
The short-term toxicity of Guanidine carbonate (CAS 593-85-1) to fish was investigated in a GLP-compliant study (Fenzl 1998) using zebra fish (Danio rerio) according to the EU C.1 (2008) protocol. The experiment is deemed valid, conclusive and thus suitable for assessment without restrictions. The test organisms were exposed during 96 h to 0 or 100 mg/L. The analytical dose verification revealed > 99 % in the daily sampled probes. Thus the effects were related to nominal concentrations. No mortalities occurred during the test and no differences between treatment and control were observed. Accordingly the 96 h L(E)C0 = 96 h L(C)0 was ≥ 100 mg/L and in consequence the L(E)C50 was found significantly > 100 mg/L. In conclusion the test item was not acute toxic to fish and on the basis of this study no indication for classification is given.
This result is supported by another experimental LC50. Adema (1988) determined the 48 h LC50 of Guanidinium chloride (CAS 50-01-1) to orfe (Leuciscus idus) to be 1758 mg/L, which corresponds to 1658 mg/L of the submission item Guanidine carbonate. Read-across and conversion on the basis of equimolar Guanidinium kation formation seems justified regarding the dissociation behaviour in the environmentally relevant pH range of 4-9 (see discussion of dissociation constant) and the assumed comparable toxicological irrelevance of the chloride and the hydrogen carbonate/carbonate species. Careful extrapolation considering the reduced exposure time suggests the actual LC 50 of Guanidine carbonate in the order of 1000 mg/L.
In summary the acute toxicity of the submission item to fish is irrelevantly low and seem to range more than 10 times above the acute aquatic toxicity cut-off limit of 100 mg/L.
It is thus concluded that Guanidine carbonate is not acute toxic to fish and on the basis of data from the trophic level of secondary consumers in the aquatic environments no classification requirements are indicated.
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