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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
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1998
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Comparable to guideline study with acceptable restrictions No data are provided regarding the nature of the radiochemical impurities in the 14C-labelled chlorhexidine. Therefore, it must be considered that impurities, e.g. breakdown products of lower molecular weight, may have penetrated through the skin at a higher amount than chlorhexidine itself and contributed to the 14C-activity which was found in urine and faeces. This would have led to an overestimation of the percutaneous absorption of chlorhexidine. After the 24 h application of the test substance, excess material was wiped off but the animals were not washed. Since the animals were housed in the metabolism cages in pairs, it must also be considered that some remaining radioactivity at the site of application could have been licked up by the other animal leading to oral uptake and contributing to the excretion of radioactivity with the faeces. This would also contribute to an overestimation of the percutaneous absorption of chlorhexidine. Furthermore, the distribution of 14C-labelled chlorhexidine in blood and organs was not measured. However, the data on excretion and residual 14C-contents at the application site and in the skin patch clearly indicate that the overall amount of chlorhexidine in the body will be very small.
Data source
Reference
- Reference Type:
- publication
- Title:
- Percutaneous absorption and tissue distribution of 1-(3,4-dichlorobenzyl)-5-octylbiguanide (OPB-2045) in rats
- Author:
- Kudo S, Furukawa M, Okumura H, Umehara K, Odomi M & Miyamoto G
- Year:
- 1 998
- Bibliographic source:
- Xenobiotic Metabolism and Disposition 13, 13-20
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 427 (Skin Absorption: In Vivo Method)
- Deviations:
- not applicable
- GLP compliance:
- no
Test material
- Reference substance name:
- Chlorhexidine
- EC Number:
- 200-238-7
- EC Name:
- Chlorhexidine
- Cas Number:
- 55-56-1
- Molecular formula:
- C22H30Cl2N10
- IUPAC Name:
- N',N'''''-hexane-1,6-diylbis[N-(4-chlorophenyl)(imidodicarbonimidic diamide)]
- Details on test material:
- Non-radioactive chlorhexidine:
Source: Sigma-Aldrich, Japan
Purity: no data
14C-labelled chlorhexidine:
Source: Amersham, Japan
Radiochemical purity: >= 97.2 %
Specific activity: 655 kBq/mg
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 14C
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Kanagawa, Japan
- Age at study initiation: 5-6 w
- Weight at study initiation: 188-245 g
- Individual metabolism cages: no (in pairs)
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: ca. 1 w
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 23 +/- 2
- Humidity (%): 60 +/- 10
- Photoperiod (hrs dark / hrs light): 12 / 12
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- water
- Duration of exposure:
- 24 hrs
- Doses:
- The test solution was prepared by mixing of gluconic acid with a 14C-labelled chlorhexidine solution at a 2:1 molar ratio and diluting to a final concentration of 0.04 (w/v) % a 14C-chlorhexidine (pH 4.74). 0.3 ml of the test solution was applied to a 2.5 cm-square patch, placed on the shaved back skin of the animals, covered with cloth tape, and held by elastic adhesive bandage.
- No. of animals per group:
- 3 m
- Control animals:
- no
- Details on study design:
- In the same study, the percutaneous absorption, distribution, and excretion of 14C-labelled 1-(3,4-dichlorobenzyl)-5-octylbiguanide (OPB), a related biguanide biocide, was also studied.
Results and discussion
- Signs and symptoms of toxicity:
- not examined
- Dermal irritation:
- not specified
Percutaneous absorption
- Remarks on result:
- other: see table below
Any other information on results incl. tables
No differences in percutaneous absorption were observed between animals with intact or damaged skin.
Results of percutaneous absorption study in rats following single dermal application of14C‑(biguanide labelled)-chlorhexidine digluconate
Percentage of total14C-dose* |
||
Intact skin |
Damaged skin |
|
Urinary excretion (0-168 h) |
0.1+.0.1 |
0.3±.0.1 |
Faecal excretion (0-168 h) |
4.2±1.8 |
3.5±1.7 |
Urine + faeces (0-168 h) |
4.2±2.0 |
3.8±1.8 |
Application site (after 168 h) |
1.5±0.5 |
2.7±1.6 |
Skin patch (after 24 h) |
97.7±5.5 |
97.2±7.7 |
Total recovery |
103.4 |
103.7 |
*: Mean ± SE of 3 animals.
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of the assay, the percutaneous absorption of chlorhexidine is low.
- Executive summary:
In this study the percutaneous absorption of 14C-labelled chlorhexidine after 24 h occlusive application to undamaged and damaged skin of rats was studied. Measurements of recovery for chlorhexidine in skin patches, skin area, urine, and faeces was done.
Under the conditions of the assay, the percutaneous absorption of chlorhexidine is quite low. More than 97 % of the applied radioactivity was removed with the skin patch and there were no significant differences in toxicokinetics between undamaged and damaged skin.
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