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EC number: 200-238-7 | CAS number: 55-56-1
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
The toxicity of Chlorhexidine base or Chlorhexidine digluconate to aquatic organisms was tested in several studies covering different trophic levels. When Chlorhexidine digluconate was used as test substance, actually Chlorhexidine base was the active component, therefore the results can be converted to equivalents of Chlorhexidine base. All tests were performed according to the OECD Guidelines.
In a study on the acute toxicity of Chlorhexidine base towards fish the LC50was determined to be 1.4 mg/L, employing the zebrafish (Brachydanio rerio) as the test organism.
Acute toxicity towards the water flea Daphnia magna was tested using Chlorhexidine digluconate as test substance. The EC50was established at 0.087 mg a.s./L, corresponding to 0.049 mg Chlorhexidine base/L.
Algal toxicity was found to be higher with an EC50value of 0.081 mg Chlorhexidine digluconate/L and an EC10of 0.030 mg Chlorhexidine digluconate/L, both values related to growth rate. The corresponding concentrations are EC50= 0.046 mg Chlorhexidine base/L and EC10= 0.017 mg Chlorhexidine base/L.
The substance concentration in the medium during the fish test was not measured during the study. However, results from the daphnia test reveal that the test substance concentration was stable over the test period of 48 hours. Therefore, it can be assumed that also during the fish test the test substance concentration was stable under the semistatic conditions with daily renewal of the medium. Measurements during the algae test revealed stability of the test item over 72 hours.
A test on reproduction of Daphnia magna was performed according to the OECD Guideline 211 A, using Chlorhexidine digluconate as test substance. The NOEC for all examined endpoints was found to be 0.02 mg Chlorhexidine digluconate/L, corresponding to 0.012 mg Chlorhexidine base/L.
A study on chronic fish toxicity is not available. However, the available data on acute toxicity indicate that fish is the trophic level with the lowest sensitivity, as the LC50(1.4 mg/L, Brachydanio rerio) is by a factor of >20 higher compared to the EC50of 0.049 mg/L of Daphnia magna and the ErC50of 0.046 mg/L of the algae (Desmodesmus subspicatus). Therefore, it is unlikely that a chronic NOEC from fish would be lower than the NOECs available for the more sensitive taxonomic groups – invertebrates and algae. Furthermore, if avoidable, testing of vertebrates would be ethically questionable and contrary to animal welfare concerns.
The acute toxicity of Chlorhexidine digluconate towards bacteria was tested according to the OECD Guideline 209, by determining the inhibition of respiration of activated sludge. The EC50was established to be 25 mg Chlorhexidine digluconate/L, corresponding to 14 mg Chlorhexidine base/L.
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