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EC number: 271-756-9 | CAS number: 68607-24-9
- 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
Endpoint summary
Administrative data
Link to relevant study record(s)
- Endpoint:
- dermal absorption in vitro / ex vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 428 (Skin Absorption: In Vitro Method)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Radiolabelling:
- yes
- Species:
- human
- Sex:
- not specified
- Details on test animals or test system and environmental conditions:
- Human skin membranes were prepared from frozen skin samples, present at TNO
Quality of Life. Human skin (derived from abdomen and/or breast) was obtained from
six donors, directly after surgery.
Donor 1: TNA# 44/09, born in 1961, arrival at TNO on 20 November 2009
Donor 2: TNA 45/09, born in 1968, arrival at TNO on 10 December 2009
Donor 3: TNA 01/10, born in 1954, arrival at TNO on 14 January 2010
Donor 4: TNA 02/10, born in 1969, arrival at TNO on 15 January 2010
Donor 5: TNA 06/10, born in 1983, arrival at TNO on 28 January 2010
Donor 6: TNA 07/10, born in 1973, arrival at TNO on 29 January 2010
The transportation of the skin to the laboratory was carried out as soon as possible after
dissection, while the skin was placed in a plastic container that was kept on ice.
Subcutaneous fat was removed and the skin was stored in aluminium foil at < −18 °C
until use. The skin of donors 2, 3 and 4 was stored overnight at 2 – 10 °C before
subcutaneous fat was removed. Informed consent was provided by all donors.
Upon thawing of the skin, human skin was cut to a thickness of ca 400 μm using a
Dermatome (25 mm, Nouvag GmbH, Germany). The thickness of all skin preparations
was measured with a digimatic micrometer (Mitutoyo Corporation, Japan). - Type of coverage:
- other: not applicable
- Vehicle:
- other: cream rinse formulation (test substance content: 5%) and cationic O/W cream (test substance content: 3%)
- Duration of exposure:
- 30 minutes for the rinse-off product and 24 hours for the leave-on product
- Doses:
- C22-ATQ was applied to the skin surface in two relevant formulations under anticipated in use conditions as follows:
Test group Group size Product Concentration Dose a.i. (microg/cm²) Exposure time
A 18 Cream rinse (rinse off) 5.01 % (w/w) 279 +/- 87 30 min.
B 18 Cationic O/W Cream (leave on) 3.01 % (w/w) 153 +/- 37 24 h
Approximately 3.2 mg of the formulation was applied on each skin membrane (0.64 cm2), i.e. ca 5 mg/cm². - No. of animals per group:
- Three skin membranes from six donors in each test group.
- Control animals:
- no
- Details on in vitro test system (if applicable):
- See below
- Total recovery:
- See below
- Dose:
- 279
- Parameter:
- percentage
- Absorption:
- 0.2 %
- Remarks on result:
- other: total
- Remarks:
- Formulation A (5% Cream rinse)
- Dose:
- 153
- Parameter:
- percentage
- Absorption:
- 0.16 %
- Remarks on result:
- other: total
- Remarks:
- Formulation B (3 % Cationic O/W Cream)
- Conclusions:
- The dermal penetration was investigated according to guideline OECD 428 ( Skin Adsorption; In vitro method). When 5% formulation of behenyl trimethyl ammonium chloride was applied for 30 min on human skin the mean total absorption was 0.20 +/-0.20%. When 3% formulation of behenyl trimethyl ammonium chloride (major component of the registration substance) was applied for 24 h on human skin the mean total absorption was 0.16+/-0.08%.
- Executive summary:
The dermal penetration was investigated according to guideline OECD 428 ( Skin Adsorption; In vitro method). When 3.2 mg of 5% formulation of behenyl trimethyl ammonium chloride was applied for 30 min on human skin membrane (i.e. ca 5 mg/cm2) the mean total absorption was 0.20 +/-0.20%. When the same amount of 3% formulation of behenyl trimethyl ammonium chloride (major component of the registration substance) was applied for 24 h the mean total absorption was 0.16+/-0.08%.
Reference
Results
Integrity of skin membranes
Prior to the determination of the percutaneous absorption of C22-ATQ, the permeation
coefficient (Kp) for tritiated water was determined.
Skin membranes with a Kp value below the cut-off value of 2.5 ×10-3 cm/h (human)
were selected for the study. All replicates of donor 4 were found to have (slightly)
higher Kp values for tritiated water than the cut-off value. Since at that time, these
membranes could not be replaced, these cells were taken along anyway. The individual
data of the absorption of tritiated water through the skin preparations are given in
Appendix 1.
Percutaneous absorption of C22-ATQ
Formulation A (5% Cream rinse):
The mean absorption of C22-ATQ from the 5% cream rinse formulation into the
receptor fluid after 24 hours was 0.063 microg/cm², representing 0.02% of the applied
dose. The mean maximal flux for the absorption of C22-ATQ was 0.013 microg/cm²h.
The lag time was 0.5 h (Table 1, Appendices 4 and 6). A total of 15 replicates from five
donors were considered for the calculations of mean values.
The mean total absorption, defined as the compound-related radioactivity present in the
receptor fluid, the receptor compartment wash and the skin membranes (excluding tape
strips) was 0.20 ± 0.20 % of the dose applied (Appendix 6).
The mean recovery of C22-ATQ was 91.6 ± 15.9 % (Appendix 6).
Formulation B (3 % Cationic O/W Cream)
The mean absorption of C22-ATQ from the 3% Cationic O/W Cream into the receptor
fluid after 24 hours was 0.086 microg/cm², representing 0.06 % of the applied dose. The
mean maximal flux for the absorption of C22-ATQ was 0.004 microg/cm²h. The lag time
was 2.6 h (Table I, Appendices 4 and 6). A total of 14 replicates from five donors were
considered for the calculations of mean values.
The mean total absorption was 0.16 ± 0.08 % of the applied dose. The mean recovery of
C22-ATQ was 102.8 ± 11.8 % (Appendix 6).
For some individual values, the mean recovery did not meet the OECD criteria of 100 ±
10 % or the criteria as set by the SCCP (i.e. ranging from 85 to 115 %). Differences are
most likely caused by the technical difficulties that go together with the adequate
application of small amounts of formulation. However, since the dermal absorption data
are comparable to the other replicates with appropriate recovery levels, the data were
not excluded from the calculations of the mean values.
Description of key information
The dermal penetration was investigated according to guideline OECD 428 ( Skin Adsorption; In vitro method). When 3.2 mg of 5% formulation of behenyl trimethyl ammonium chloride was applied for 30 min on human skin membrane (i.e. ca 5 mg/cm2) the mean total absorption was 0.20 +/-0.20%. When the same amount of 3% formulation of behenyl trimethyl ammonium chloride (major component of the registration substance) was applied for 24 h the mean total absorption was 0.16+/-0.08%.
Key value for chemical safety assessment
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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