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EC number: 220-767-7 | CAS number: 2893-78-9
- 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 birds
Administrative data
Link to relevant study record(s)
Description of key information
Several studies acute oral and dietary studies are available in birds with NaDCC and CYA
Key value for chemical safety assessment
Additional information
NaDCC:
Acute oral studies:
In a study with mallard ducks (Fink 1979) birds were given 398, 631, 1000, 1590 and 2510 mg/kg of the test substance. Dieldrin was used as a positive control. The acute oral toxicity LD50 was 1916 mg/kg. In another acute oral study (Robaidek 1985) bobwhite quail were given 633, 844, 1125, 1500 and 2000 mg/kg.of sodium dichloroisocyanurate dihydrate. The LD50 was 1766 mg/kg. In a study with mallard ducks (Robaidek 1984) birds were given 1250, 2500 and 5000 ppm (nominal) of sodium dichloroisocyanurate dihydrate. The dietary LC50 was considered > 5000 ppm.
Dietary studies:
In an eight day dietary study with mallard duck (Fink 1975) Mallard duck were exposed to dietary concentrations of 464, 1000, 2150, 4640 and 10 000 ppm ACL 60 for 5 days. Positive control birds received dietary concentrations of 68, 100, 147, 215 and 316 ppm dieldrin. Negative control birds received the basal diet only. The LC50 was determined to be > 10 000 ppm.
In another dietary study (Fink 1975) bobwhite quail were exposed to dietary concentrations of 464, 1000, 2150, 4640 and 10 000 ppm ACL 60 for 5 days. Positive control birds received dietary concentrations of 10.0, 14.7, 21.5, 31.6 and 46.4 ppm dieldrin. Negative control birds received the basal diet only. The LC50 was determined to be > 10000 ppm.
CYA:
Mallard ducks were exposed to 464, 1000, 2150, 4640 and 10000 ppm nominal concentrations for 5 days and then observed for an additional three days. Negative controls were exposed to a basal diet only. Monosodium cyanurate did not cause any symptoms of toxicity or behavioural abnormalities at the dosage levels tested. There was no mortality at any dosage level, with the exception of an incidental death in the 2150 ppm dosage level. In another study bobwhite quail were exposed to 464, 1000, 2150, 4640 and 10000 ppm dietary concentrations of monosodium cyanurate for 5 days and then observed for an additional three days. Negative controls were exposed to a basal diet only. Monosodium cyanurate did not cause symptoms of the toxicity or behavioural abnormalities at the dosage levels tested. There was no mortality at any dosage level.
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