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EC number: 207-312-8 | CAS number: 461-58-5
- 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 aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 12-14 September 1984
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- yes
- Remarks:
- exposure period extended to 48h
- GLP compliance:
- yes
- Remarks:
- The study was carried out under conditions of good laboratory practice. Within reason there have been no circumstances that might have affected the quality and integrity of the study.
- Specific details on test material used for the study:
- PHYSICO-CHEMICAL PROPERTIES
- Melting point: 209 -211 °C
- Water solubility (under test conditions): 3.2 g/100 g water
- Stability in water: Dicyandiamid is stable in neutral aqueous solution for temperatures < 80 °C
OTHER PROPERTIES (if relevant for this endpoint)
- Results of test for ready biodegradability: Dicyandiamid is not readily biodegradable - Analytical monitoring:
- no
- Details on sampling:
- No analytical monitoring.
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- first stock solution: 2000 mg Dicyandiamid dissolved in 1l
- from this solution 2.4, 4.5, 8.0, 14, 25, 45, 80, 140 and 250 ml were taken and diluted with dilution water to 0.5 l to prepare the corresponding test solutions, concentration range 10 - 1000 mg/l
- second stock solution: 10000 mg Dicyandiamd in 1l
- from second stock solution 90, 160, 280 and 500 ml were taken and diluted to 0.5l to prepare the more concentrated test soloutions in the concentration range 1800 - 10000 mg/l - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Cultured in the laboratory under standard conditions
- Age at study initiation (mean and range, SD): less than 24 h
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- Not applicable
- Hardness:
- CaCO3: 210 mg/l
- Test temperature:
- 19 +/- 1 °C
- pH:
- 7.8 - 8.3
- Dissolved oxygen:
- > 6.3 mg/l
- Salinity:
- No data
- Nominal and measured concentrations:
- Nominal concentrattions:
- 13 concentrations: 0, 10, 18, 32, 56, 100, 180, 320, 560, 1000, 1800, 3200, 5600, 10000
Concentrations were not measured - Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Material, size, headspace, fill volume: 100 ml all-glass beakers, each containing 100 ml test solution
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
DILUTION WATER
- The dilution water used was DSWL, prepared from groundwater
- Composition:
- Na: 1.19 mmol/l
- K: 0.20 mmol/l
- Ca: 1.36 mmol/l
- Mg: 0.73 mmol/l
- Cl: 2.72 mmol/l
- SO4: 0.73 mmol/l
- HCO3: 1.37 mmol/l
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- mobility and swimming behaviour (see tables 1 and 2) - Reference substance (positive control):
- no
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 8 118 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95 % CL: 5952 - 11073
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 3 177 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95 % CL: 2506 - 4028
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- 10 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: swimming behaviour
- Details on results:
- - Behavioural abnormalities: Although in the test solution containing 180 mg/l until and including 3200 mg/l most living animals were mobile according to the definition given in OECD 202, they were swimming less active and with more irregular movements compared to the control animals
- Results with reference substance (positive control):
- No reference substance
- Reported statistics and error estimates:
- - Calculation of EC50 (24h and 48h) EC100 and NOEC (both 48h)
- calculation of the 95 % CL for EC50 (24h and 48h)
- slope of concentration-effect curve was 0.47 - Validity criteria fulfilled:
- yes
- Remarks:
- No immobilization of daphnids w as observed in the control. During the biological phase of the study no unexpected phenomena were recorded.
- Conclusions:
- The 24h EC50 (immobilization) was found to be 8118 mg/l, and the 48 h EC50 3177 mg/l.
At 1000 mg/l all animals were mobile after 48h, at 10000 mg/l all animals were immobile after 48h.
Therefore, it can be concluded that Dicyandiamide is practically non-toxic to Daphnia magna. - Executive summary:
The acute toxicity of Dicyandiamid to the fresh-water crustacean Daphnia magna was determined as laid down in OECD Guideline No. 202, but the exposure period was extended to 48h.
Test concentrations of nominal 0, 10, 18, 32, 56, 100, 180, 320, 560, 1000, 1800, 3200, 5600 and 10000 mg/l Dicyandiamd were selected for this study. Four replicates were evaluated per test concentration and control.
The 24h EC50(immobilization) was found to be 8118 mg/l, and the 48 h EC503177 mg/l. At 1000 mg/l all animals were mobile after 48h, at 10000 mg/l all animals were immobile after 48h.
The slope of the concentration-effect curve was 0.47.
After 48 h exposure at 100 mg/l, the number of mobile animals and their condition, visually assessed, were the same as those of the control animals.
The estimation of the following toxicity values were based on nominal test concentrations:
NOEC(48h): 100 mg/l (based on swimming behaviour)
NOEC(48h): 1000 mg/l (based on mobility)
EC50(48 h): 3177 mg/l
Reference
Description of key information
The acute toxicity of Dicyandiamid to the fresh-water crustacean Daphnia magna was determined as laid down in OECD Guideline No. 202, but the exposure period was extended to 48h.
Test concentrations of nominal 0, 10, 18, 32, 56, 100, 180, 320, 560, 1000, 1800, 3200, 5600 and 10000 mg/l Dicyandiamd were selected for this study. Four replicates were evaluated per test concentration and control.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 3 177 mg/L
Additional information
The 24h EC50(immobilization) was found to be 8118 mg/l, and the 48 h EC50 3177 mg/l. At 1000 mg/l all animals were mobile after 48h, at 10000 mg/l all animals were immobile after 48h.
The slope of the concentration-effect curve was 0.47.
After 48 h exposure at 100 mg/l, the number of mobile animals and their condition, visually assessed, were the same as those of the control animals.
The estimation of the following toxicity values were based on nominal test concentrations:
NOEC(48h): 100 mg/l (based on swimming behaviour)
NOEC(48h): 1000 mg/l (based on mobility)
EC50(48 h): 3177 mg/l
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