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EC number: 208-060-1 | CAS number: 506-93-4
- 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

Toxicity to terrestrial plants
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to terrestrial plants: long-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 208 (Terrestrial Plants Test: Seedling Emergence and Seedling Growth Test)
- Deviations:
- yes
- Remarks:
- Outcome of test is comparable to outcome of OECD208
- Principles of method if other than guideline:
- Toxic effects of the guanidines on germination and growth of wheat seedlings were determined by placing 200 g of each of the three soils into small pots (15 x 15 x 20 cm). The test compounds were mixed into the separate pot to give 200 µg N/g soil (GuNi 45.9%N; 444µgGuNi/g soil), and 25 seeds of wheat (var. Star) were sown into each pot. Three replications were maintained. The percent germination was determined a week after sowing. The twenty seedlings were then allowed to grow for another two weeks and they were cut at soil surface. The above ground plant portions were dried at 60 °C and dry weights were recorded. The dry weights of plants in each treatment was compared to the respective control and to the urea treatment using a ‘t’ test (Panse and Sukhatme, 1978).
- GLP compliance:
- not specified
- Species:
- Triticum aestivum
- Plant group:
- Monocotyledonae (monocots)
- Details on test organisms:
- Wheat seedlings (var. Star)
- Test type:
- other: wheat germination, seedling growth
- Study type:
- laboratory study
- Substrate type:
- natural soil
- Limit test:
- yes
- Total exposure duration:
- 14 d
- Key result
- Species:
- Triticum aestivum
- Duration:
- 14 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 435 mg/kg soil ww
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: wheat germination, seedling growth
- Validity criteria fulfilled:
- not applicable
- Remarks:
- Data from publication
- Conclusions:
- The effect of Guanidine nitrate on germination and growth of wheat seedlings was tested for 14 days. At a Guanidine nitrate concentration of 200 µg N/g soil, (GuNi 45.9%N; 435mgGuNi/Kg soil) there was no adverse affect in wheat germination. The response of wheat dry matter production was the same as with urea.
- Executive summary:
The effect of Guanidine nitrate on germination and growth of wheat seedlings was tested for 14 days. At a Guanidine nitrate concentration: 200 µg N/g soil, GuNi 45.9%N; 435 mgGuNi/Kg soil) there was no adverse affect in wheat growth and germination. The response of wheat dry matter production was the same as with urea.
- Endpoint:
- toxicity to terrestrial plants: short-term
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- a short-term study does not need to be conducted because an appropriate long-term toxicity study on terrestrial organisms is available
Referenceopen allclose all
Guanidine nitrate concentration: 200 µg N/g soil, (GuNi 45.9%N; 435mgGuNi/Kg soil)
None of the guanidines adversely affect the wheat germination which was >90% in all cases (data not presented). The wheat seedling grew normally for two weeks except with GT which caused death soon after emergence. The toxicity of GT may be due to the thiocyanate group, from ionisation of Guanidine thiocyanate into guanidinium and thiocyanate. The 20 plants in a small soil volume rapidly deplete available soil N in the control, so there was more seedling growth from urea and from more quickly available guanidines (Figure 2). The responses of Guanidine nitrate, Aminoguanidine nitrate and Aminoguanidine carbonate were the same as with urea due to the immediate release of NH4+ or NO3-. Plant growth with Guanidine sulphate, Guanidine acetate, and Guanidine carbonate was lower than with urea, but, more than for the control. A similar trend was observed for DGS. Relatively less N response for Guanidine sulphate, Guanidine acetate, and Guanidine carbonate may be attributed to their slow mineralization (Table 3). However, the results with Dimethylguanidine sulphate are difficult to explain since it was the fastest mineralized derivative. Mineralization of Nitroguanidine and Tetramethyl guanidine was very slow (Table 4). So, their application did not effect plant growth.
Description of key information
The NOEC of Gunanidine nitrate on terrestrial plants is 435mg/kg soil.
Key value for chemical safety assessment
- Long-term EC10, LC10 or NOEC for terrestrial plants:
- 435 mg/kg soil dw
Additional information
The effect of Guanidine nitrate on germination and growth of wheat seedlings was tested for 14 days. At a Guanidine nitrate concentration: 200 µg N/g soil, GuNi 45.9%N; 435mgGuNi/Kg soil) there was no adverse affect in wheat growth and germination. The response of wheat dry matter production was the same as with urea. This test was used for NOEC derivation according to Guidance R7c, p. 112 (2008).
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