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EC number: 202-684-8 | CAS number: 98-59-9
- 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 24-29 Oct 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP compliant, guideline study, available as unpublished report, no restrictions, fully adequate for assessment
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- TNO Triskelion, Utrechtseweg 48 3704 HE Zeist, the Netherlands
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Tosyl chloride
- EC Number:
- 202-684-8
- EC Name:
- Tosyl chloride
- Cas Number:
- 98-59-9
- Molecular formula:
- C7H7ClO2S
- IUPAC Name:
- 4-methylbenzenesulfonyl chloride
- Test material form:
- solid: crystalline
- Details on test material:
- - Name of test material (as cited in study report): Tosyl chloride
- Chemical name 4-methylbenzene-1-sulfonyl chloride
- Molecular formula: C7H7CIO2S
- Molecular weight: 190.6 g/mol
- Colour / Appearance: white to grey crystalline solid
- Storage conditions: ambient temperature, protected from light
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories
- Age at study initiation: approximately 9-11 weeks
- Weight at study initiation: 21.1 - 25.6 g
- Housing: During acclimatisation the animals were group housed in macrolon type III cages (maximally 5 mice/cage). After allocation the animals were housed in macrolon type III cages (4 mice/group/cage) for the main study. For the dose range finding test, one animal was housed in a macrolon type II cage. The cages were provided with wood shavings (Lignocel) as bedding material and shreds of paper (Enviro-dri) and gnaw wood as environmental enrichment
- Diet: Standard diet ad libitum (Rat and Mouse no.3 breeding diet RM3) was purchased from SDS Special Diets Services, Whitham, England.
- Water: domestic mains tap-water, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2, one deviation from the optimal temperature was observed (period of <30 minutes of 24.7°C).
- Humidity (%): 45-65, the actual upper limit during the study period was 99.9%, which was considered not to have affected study integrity.
- Air changes (per hr): ca 10
- Photoperiod (hrs dark / hrs light): 12/12 (light on from 7:00 AM - 7:00 PM)
Study design: in vivo (LLNA)
- Vehicle:
- acetone/olive oil (4:1 v/v)
- Concentration:
- 0, 5, 10, 25% w/v
- No. of animals per dose:
- 4
- Details on study design:
- DOSE FORMULATIONS:
The dose formulations of the test substance in vehicle were freshly prepared on each day of dosing, i.e. day 0, 1 and 2. The formulation was prepared on a weight (test substance)/volume (vehicle) basis. The formulation was mixed (vortex) until visible homogeneity was obtained. Dose formulations were prepared at concentrations selected from the series: 50% and 25% (dose range finding study) and 25%, 10% and 5% (main study). No adjustment was made for the purity of the test substance. The dose formulations were used for dosing of the animals within 2 hours after preparation. Homogeneity, concentration and stability of the test substance in vehicle were not determined in this study.
STUDY DESIGN:
- Dose range finding test: One randomly selected animal was treated in the dose range finding test, each ear with a test substance concentration from the series: 50 and 25%. The test substance formulations were applied on the dorsum of the ears (25 μL on each ear) for three consecutive days, i.e. days 0, 1 and 2. The ears of the animal were observed daily for signs of irritation. Moreover, the animal was also checked for clinical signs and changes in body weight. The animal was sacrificed approximately 24 hours after its third treatment on day 3.
- Main study: On day 0, 1 and 2 the different concentrations of test substance and control substances were administered to the dorsum of both ears (25 μL on each ear by means of a pipette). On day 5 all animals received an intravenous injection of 250 μL of phosphate-buffered saline (PBS) containing 20 μCi of 3H-thymidine in the tail vein. Five hours after the 3H-thymidine injection the animals were sacrificed by intra peritoneal (i.p.) injection with an overdose of sodium pentobarbital and the draining auricular lymph nodes were excised, pooled per animal in PBS and further processed to determine the 3H-thymidine incorporation. Per animal, the paired auricular lymph nodes (ALN) were excised and were placed together in a vial containing 5 mL phosphate buffered solution (PBS). A single cell suspension was prepared by gently rubbing the nodes between the rough ends of microscope slides. The cell suspension was washed twice. The cell pellet obtained after the second wash was resuspended in 3 mL of 5% trichloroacetic acid (TCA) and left overnight (~18 hours) at 2-10ºC. After centrifugation and removal of the supernatant, 1 mL of 1.5 M KOH in 20% EtOH was added to the precipitate and left for 24 hours at room temperature. Thereafter, the solution was transferred into a clean scintillation vial and 20 mL liquid scintillation cocktail (Hionic Fluor, Perkin Elmer) was added. The vial was thoroughly shaken and the number of disintegrations per minute (DPM) was determined by counting for five minutes in a liquid scintillation counter (Perkin Elmer).
OBSERVATIONS:
The general condition and behaviour of the animals were checked at least once daily during the study. All findings including any abnormalities were recorded in the morning, when applicable before dosing and in case of changes in clinical signs also in the afternoon. Body weights were determined at allocation, at the start (day 0) and at the end (day 5) of the study. The animals were sacrificed on day 5 for excision of the auricular lymph nodes. The animals were macroscopically examined including the auricular lymph nodes and the ears. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- Statistical evaluation of the data (body weights and 3H-thymidine incorporation) were performed by one-way ANOVA, followed by Dunnett’s multiple comparison tests in case of a significant result. In case of difference of variance between the different groups, log-transformation of the data before statistical evaluation was considered. Body weights and 3H-thymidine incorporation of the test groups 2, 3 and 4 or the positive control group were compared with the vehicle control animals. Probability values of p<0.05 were considered significant.
Results and discussion
- Positive control results:
- The stimulation index of Hexyl Cinnamic Aldehyde (25% in vehicle v/v) was 4.42.
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Remarks:
- Concentration 0 % w/v
- Value:
- 1
- Parameter:
- SI
- Remarks:
- Concentration 5 % w/v
- Value:
- 11.82
- Parameter:
- SI
- Remarks:
- Concentration 10 % w/v
- Value:
- 23.13
- Parameter:
- SI
- Remarks:
- Concentration 25 % w/v
- Value:
- 17.38
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: see Remark
- Remarks:
- Concentration (% w/v) Disintegrations per minute (group means) 0 : 1672 5 : 19763 10 : 38675 25 : 29067
Any other information on results incl. tables
- Dose range finding test: Application of a 50% Tosyl chloride formulation resulted in redness of the skin of the (left) ear. The redness had not resolved before application of the next dose (approximately 24 hours after the previous) and persisted for at least 24 hours after the last (third) dosing. No indication of an increase in the degree of irritation was observed after repeated application. The right ear, dosed with a 25% Tosyl chloride formulation, showed similar redness and was also persistent for at least 24 hours after the last (third) application. Comparable with the 50% concentration, no indication of an increase in the degree of irritation was observed after repeated application of the 25% concentration. After the third dosing, redness was observed in the skin on the head between both ears, which had disappeared within 24 hours. This was considered a spread of the signs of irritation outside the area of application. The signs of irritation were indicative of absorption of the test substance through the skin, and the results showed that there was no (clear) difference in degree of irritation between a 50% and 25% formulation. To prevent an interference of the irritable state of the animal on the stimulation of the proliferation of lymphocytes in the auricular lymph node as much as possible, a 25% concentration was selected as the highest concentration to be tested in the main study. The concentrations to be used in the main study were thus selected to be 25%, 10% and 5% Tosyl chloride (w/v).
- Main study: Signs of erythema of the ears were observed in all animals of groups 3 and 4. In the animals of group 3, erythema of the ears was observed from day 2 until the end of the study period (day 5), whereas in group 4 erythema was observed from day 0 until the end of the study period. No aberrant body weights or body weight gains were observed and no statistical significant difference was found between the vehicle and the different test groups and between the vehicle and the positive control group.
Applicant's summary and conclusion
- Interpretation of results:
- sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- Under the experimental conditions of this study, evidence was obtained that Tosyl chloride has sensitising potential when dermally applied at concentrations of 5% and higher.
- Executive summary:
In a GLP-compliant OECD Guideline 429 study, skin sensitisation properties of Tosyl chloride were studied in mice. Three test groups of 4 female mice each were treated with 5, 10, and 25% w/v by means of open application of 25 μL to the dorsum of each ear (total 50µL) for three consecutive days. Three days after the last treatment, all animals received an intravenous injection of 3H-thymidine. Five hours later, the 3H-thymidine incorporation in the draining auricular lymph nodes was determined. The results were compared with those of a negative control group which was treated with the vehicle (acetone/olive oil, 4:1 v/v). Group mean 3H-thymidine incorporations of 19763, 38675 and 29067 DPM were found in the auricular lymph nodes of animals treated with respectively 5, 10 and 25% Tosyl chloride. The group mean value in the vehicle control animals was 1672 DPM. The calculated stimulation indices (SI), representative of the change in 3H-thymidine incorporation in Tosyl chloride treated animals compared to controls, were 11.82, 23.13 and 17.38 for the tested doses of 5, 10 and 25% Tosyl chloride, respectively. Since the SI was >3 after 5% Tosyl chloride, the limiting value required for classification as a skin sensitiser, it was concluded that Tosyl chloride should be regarded as a skin sensitiser.
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