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Diss Factsheets
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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
Repeated dose toxicity: dermal
Administrative data
- Endpoint:
- sub-chronic toxicity: dermal
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1988
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was conducted with chlorhexidine diacetate and not with the chlorhexidine base. Due to the fact that it is a simple salt form showing even a higher solubility and therefore a possibly higher dermal absorption, the results derived from this studies are considered to be predictive also for chlorhexidine base. This internal company report is not available for publicity. However, methods and results have been reported in a summarised format by Cal EPA and US EPA.
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 988
- Reference Type:
- secondary source
- Title:
- Summary Of Toxicology Data. Chlorhexidine Diacetate
- Author:
- Cal EPA
- Year:
- 2 003
- Bibliographic source:
- Medical Toxicology Branch. Department Of Pesticide Regulation. California Environmental Protection Agency
- Reference Type:
- secondary source
- Title:
- Reregistration Eligibility Decision (RED). Chlorhexidine Diacetate
- Author:
- US EPA
- Year:
- 1 996
- Bibliographic source:
- Office of Prevention, Pesticides and Toxic Substances (OPPTS). United States Environmental Protection Agency (US EPA), Washington, D.C.
Materials and methods
- Principles of method if other than guideline:
- No detailed information available
- GLP compliance:
- not specified
- Limit test:
- yes
Test material
- Reference substance name:
- Chlorhexidine di(acetate)
- EC Number:
- 200-302-4
- EC Name:
- Chlorhexidine di(acetate)
- Cas Number:
- 56-95-1
- IUPAC Name:
- N',N'''''-hexane-1,6-diylbis[N-(4-chlorophenyl)(imidodicarbonimidic diamide)] diacetate
- Details on test material:
- -Purity: 97.7 %
-Lot/batch No.: R4796
Constituent 1
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- -Age at study initiation: ca. 12 weeks
No further detailed information available
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- water
- Details on exposure:
- The test substance was applied moistened with 2 ml of water to the intact dorsal dermal surface and the treatment area was covered with a gauze dressing and wrap.
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 13 consecutive weeks
- Frequency of treatment:
- 6 h/d on 5 d/week
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 250, 500 or 1000 mg/kg bw/d
Basis:
- No. of animals per sex per dose:
- 10 m / 10 f
- Control animals:
- yes
- Details on study design:
- The dose selection was justified as being a limit dose of 1000 mg/kg bw/d and choosing logarithmically spaced doses for the mid- and low-dermal doses.
No further detailed information available.
Examinations
- Observations and examinations performed and frequency:
- see below
- Sacrifice and pathology:
- No further detailed information available.
- Statistics:
- Fishers exact test
Results and discussion
Results of examinations
- Details on results:
- Body weight and food consumption were slightly lowered during the initial 2 weeks of the study. At all doses minimal dermal irritation such as erythema, edema, desquamation and fissuring was observed. There were no adverse effects on ophthalmology or haematology.
In females treated with >= 500 mg/kg bw/d the activities of aspartate aminotransferase and of alanine aminotransferase were increased at the end of the study.
The incidence of hepatocellular degeneration/necrosis in males was 0, 0, 0, 1 and 0, 1, 5, and 7 in females. However, the liver necrosis was graded as minimal in all animals and the incidence of 1/10 at 250 mg/kg bw/d was not statistically significant.
Effect levels
- Dose descriptor:
- NOEL
- Effect level:
- 360 mg/kg bw/day
- Sex:
- male/female
- Basis for effect level:
- other: A dermal NOEL was not established as there were local effects at all doses in both sexes. For systemic effects a NOEL of 250 mg/kg bw/d (corresponding to 360 mg chlorhexidine digluconate/kg bw/d) was derived based on liver findings at higher doses.
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of the assay, dermal application of chlorhexidine diacetate to rabbits for 13 weeks led to minimal liver necrosis in animals dosed with >= 500 mg/kg bw/d. A dose of 250 mg/kg bw/d was associated with local effects such as irritation but there were no statistically significant systemic effects.
- Executive summary:
For chlorhexidine digluconate itself there are no standardized studies available performed according to recent guidelines. Therefore, data for chlorhexidine diacetate have been taken into further consideration.
In a 13 -week dermal toxicity study with NZW rabbits, chlorhexidine acetate was applied at doses of 0, 250, 500, or 1000 mg/kg bw/d to the intact dorsal dermal surface on 6 h/d and 5 d/week under occlusive conditions.
Body weight and food consumption were slightly lowered during the initial 2 weeks of the study. At all doses minimal dermal irritation such as erythema, edema, desquamation and fissuring was observed. There were no adverse effects on ophthalmology or haematology.
In females treated with >= 500 mg/kg bw/d the activities of aspartate aminotransferase and of alanine aminotransferase were increased at the end of the study.
The incidence of hepatocellular degeneration/necrosis in males was 0, 0, 0, 1 and 0, 1, 5, and 7 in females. However, the liver necrosis was graded as minimal in all animals and the incidence of 1/10 at 250 mg/kg bw/d was not statistically significant.
A dermal NOEL was not established as there were local effects at all doses in both sexes. For systemic effects a NOEL of 250 mg/kg bw/d (corresponding to 360 mg chlorhexidine digluconate/kg bw/d) was derived based on liver findings at higher doses.
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