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Reaction products of diazotised 2-amino-5-{[2-(sulfooxy)ethyl]sulfonyl}benzenesulfonic acid coupled with 4-amino-5-hydroxynaphthalene-2,7-disulfonic acid under acidic conditions, further coupled with diazotised reaction products of 2,4,6-trifluoro-1,3,5-triazine with 2-[(2-anilinoethyl)sulfonyl]ethyl hydrogen sulfate and 2,4-diaminobenzenesulfonic acid (1:1:1) under alkaline conditions, potassium sodium salts
EC number: 948-562-4 | CAS number: -
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Reaction products of diazotised 2-amino-5-{[2-(sulfooxy)ethyl]sulfonyl}benzenesulfonic acid coupled with 4-amino-5-hydroxynaphthalene-2,7-disulfonic acid under acidic conditions, further coupled with diazotised reaction products of 2,4,6-trifluoro-1,3,5-triazine with 2-[(2-anilinoethyl)sulfonyl]ethyl hydrogen sulfate and 2,4-diaminobenzenesulfonic acid (1:1:1) under alkaline conditions, potassium sodium salts
- EC Number:
- 948-562-4
- Molecular formula:
- UVCB
- IUPAC Name:
- Reaction products of diazotised 2-amino-5-{[2-(sulfooxy)ethyl]sulfonyl}benzenesulfonic acid coupled with 4-amino-5-hydroxynaphthalene-2,7-disulfonic acid under acidic conditions, further coupled with diazotised reaction products of 2,4,6-trifluoro-1,3,5-triazine with 2-[(2-anilinoethyl)sulfonyl]ethyl hydrogen sulfate and 2,4-diaminobenzenesulfonic acid (1:1:1) under alkaline conditions, potassium sodium salts
- Test material form:
- solid: particulate/powder
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA/Ca
- Sex:
- female
- Details on test animals and environmental conditions:
- Housing: group
Cage Type: Makrolon Type II (pre-test) / III (main study), with wire mesh top
Bedding: granulated soft wood bedding
Feed: 2018C Teklad Global 18% protein rodent diet (certified), ad libitum
Water: tap water, ad libitum
Environment: temperature 22 ± 2°C, relative humidity approx. 45-65%, artificial light 6.00 a.m. - 6.00 p.m.
Study design: in vivo (LLNA)
- Vehicle:
- other: ethanol/water (3+7 v/v)
- Concentration:
- 5, 10, and 25%
- No. of animals per dose:
- 5
- Details on study design:
- Test Item Administration
Each test group of mice was treated by (epidermal) topical application to the dorsal surface of each ear with test item concentrations of 5, 10, and 25% in ethanol/water (3+7 v/v). The application volume, 25 µL/ear/day, was spread over the entire dorsal surface ( 8 mm) of each ear once daily for three consecutive days. A further group of mice (control animals) was treated with an equivalent volume of the relevant vehicle alone (control animals).
Administration of 3H-methyl-thymidine
Five days after the first topical application (day 6) 250 µL of phosphate-buffered saline containing 20.3 µCi of 3H-methyl thymidine (equivalent to 81 µCi/mL 3HTdR) were injected into each test and control mouse via the tail vein.
Terminal Procedure
Approximately five hours after treatment with 3HTdR all mice were euthanized by using CO2, which was, after harvesting of the lymph nodes, followed by cervical dislocation to ensure death.
Preparation of Single Cell Suspensions
The draining lymph nodes were rapidly excised and pooled per animal (2 nodes per animal). Single cell suspensions (in phosphate buffered saline) of pooled lymph node cells were prepared by gentle mechanical disaggregation through stainless steel gauze (200 µm mesh size). After washing two times with phosphate buffered saline (approx. 10 mL) the lymph node cells were resuspended in 5 % trichloroacetic acid (approx. 3 mL) and incubated at approximately +4 °C for approximately 18 hours for precipitation of macromolecules.
Determination of cellular proliferation (incorporation of 3HTdR)
The precipitates were then resuspended in 5 % trichloroacetic acid (1 mL) and transferred to scintillation vials with 10 mL of scintillation liquid and thoroughly mixed. The level of 3HTdR incorporation was then measured in a -scintillation counter. Similarly, background 3HTdR levels were also measured in two 1 mL-aliquots of 5 % trichloroacetic acid. The -scintillation counter expresses 3HTdR incorporation as the number of radioactive disintegrations per minute.
Observations
Clinical Observations
All animals were observed on a daily basis, including pre- and post-dose observations on days 1, 2 and 3. Any clinical signs of systemic toxicity, local skin irritation or signs of ill health during the study were recorded.
Determination of Ear Thickness
In the pre-test, the ear thickness was determined prior to the first application of the test item (day 1), on day 3, and on day 6 prior to sacrifice using a micrometer.
Determination of ear weights
In the pre-test and main experiment, after the lymph nodes have been excised, both ears of mice were punched at the apical area using a biopsy punch (Ø 8 mm corresponding to 0.5 cm2). For each animal both punches were immediately weighed per animal using an analytical balance. The values obtained were taken down manually. The results are described in the report.
Determination of Body Weights
The body weights was recorded on day 1 (prior to dosing) and prior to sacrifice (pre-test) or prior to treatment with 3HTdR (main experiment) - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
Results and discussion
- Positive control results:
- October 2018 (study 1921100): S.I. of 1.41, 2.70, and 10.33 were derived at tested concentrations of 5, 10, 25%, respectively and an EC3 value of 10.6% was calculated.
In vivo (LLNA)
Resultsopen allclose all
- Key result
- Parameter:
- EC3
- Value:
- 17.5
- Parameter:
- SI
- Value:
- 1.6
- Test group / Remarks:
- 5%
- Parameter:
- SI
- Value:
- 2.8
- Test group / Remarks:
- 10%
- Parameter:
- SI
- Value:
- 3.2
- Test group / Remarks:
- 25%
- Cellular proliferation data / Observations:
- In this study Stimulation Indices of 1.6, 2.8, and 3.2 were determined with the test item at concentrations of 5, 10, and 25% in ethanol/water (3+7 v/v). A clear dose response was observed. The EC3 value calculated was 17.5%.
Any other information on results incl. tables
Calculation and Results of Individual Data
Vehicle: ethanol/water (3+7 v/v)
Test item concentration |
DPM values measured |
DPM-BG per animal |
S.I.b) |
||
% |
Group no. |
Animal no. |
|||
--- |
--- |
BG I |
26 |
--- |
--- |
--- |
--- |
BG II |
15 |
--- |
--- |
0 |
1 |
1 |
1044 |
1023.5 |
--- |
0 |
1 |
2 |
913 |
892.5 |
--- |
0 |
1 |
3 |
1192 |
1171.5 |
--- |
0 |
1 |
4 |
1142 |
1121.5 |
--- |
0 |
1 |
5 |
2037 |
2016.5* |
--- |
5 |
2 |
6 |
1658 |
1637.5 |
1.3 |
5 |
2 |
7 |
1646 |
1625.5 |
1.3 |
5 |
2 |
8 |
2049 |
2028.5 |
1.6 |
5 |
2 |
9 |
2028 |
2007.5 |
1.6 |
5 |
2 |
10 |
2388 |
2367.5 |
1.9 |
10 |
3 |
11 |
3268 |
3247.5 |
2.6 |
10 |
3 |
12 |
2872 |
2851.5 |
2.3 |
10 |
3 |
13 |
2785 |
2764.5 |
2.2 |
10 |
3 |
14 |
2471 |
2450.5 |
2.2 |
10 |
3 |
15 |
6091 |
6070.5* |
4.9 |
25 |
4 |
16 |
2857 |
2836.5 |
2.3 |
25 |
4 |
17 |
2963 |
2942.5 |
2.4 |
25 |
4 |
18 |
3195 |
3174.5 |
2.5 |
25 |
4 |
19 |
6198 |
6177.5 |
5.5 |
25 |
4 |
20 |
4807 |
4786.5 |
3.8 |
BG = Background (1 ml 5% trichloroacetic acid) in duplicate
1 = Control Group for the test item and for the positive control item
3-4 = Test Groups
S.I. = Stimulation Index
a) = values corrected for mean background value (BGI and BGII).
b) = Stimulation Indices relative to the mean of the control group (Group 1)
* = statistical outlier value
Calculation of Stimulation Indices per Dose Group
Test item concentration |
Group Calculation |
||
Mean DPM per |
SD |
S.I. |
|
Vehicle Control Group (ethanol/water (3+7 v/v)) |
1245.1 |
444.2 |
1.0 |
5% Reactive Blue F07-0195 |
1933.3 |
310.4 |
1.6 |
10% Reactive Blue F07-0195 |
3476.9 |
1477.5 |
2.8* |
25% Reactive Blue F07-0195 |
3983.5 |
1458.8 |
3.2* |
a) Mean DPM/animal was determined by dividing the sum of the measured values from lymph nodes of all animals within a group by the number of animals in that group (5 animals)
* statistically significant if compared to vehicle control (p<0.05).
Calculation of the EC3 value
|
Test item concentration % |
S.I. |
Test Group 3 |
10 (a) |
2.8 (b) |
Test Group 4 |
25 (c) |
3.2 (d) |
EC3 = (a-c) [(3-d)/(b-d)] + c = 17.5% |
a,b,c,d = Co-ordinates of the two pairs of data lying immediately above and below the S.I. value of 3 on the LLNA dose response plot.
Viability / Mortality
No deaths occurred during the study period.
Clinical Signs
No symptoms of local skin irritation at the ears of the animals and no signs of systemic toxicity were observed during the study period.
Body Weights
The body weight of the animals, recordedprior to the first application and prior to treatment with3HTdR, was within the range commonly recorded for animals of this strain and age.
The individual body weight values are included in Appendix 2.
Ear Weights
The measured ear weight of all animals treated was recorded on test day 6 (after necropsy). A biologically relevant or statistically significant increase in ear weights was not observed.
The individual data are included in Appendix 3.
Applicant's summary and conclusion
- Interpretation of results:
- Category 1B (indication of skin sensitising potential) based on GHS criteria
- Conclusions:
- The test item was found to be a weak skin sensitiser under the test conditions of this study.
- Executive summary:
In order to study a possible skin sensitising potential of the test item, three groups each of five female mice were treated once daily with the test item at concentrations of 5, 10, and 25% in ethanol/water (3+7 v/v) by topical application to the dorsum of each ear for three consecutive days. The highest concentration tested was the highest concentration that could technically be achieved. A control group of five mice was treated with the vehicle (ethanol/water (3+7 v/v)) only. Five days after the first topical application the mice were injected intravenously into a tail vein with radio-labelled thymidine (3H-methyl thymidine). Approximately five hours after intravenous injection, the mice were sacrificed, the draining auricular lymph nodes excised and pooled per animal. Single cell suspensions of lymph node cells were prepared from pooled lymph nodes, which were subsequently washed and incubated with trichloroacetic acid overnight. The proliferative capacity of pooled lymph node cells was determined by the incorporation of3H-methyl thymidine measured in ab-scintillation counter.
All treated animals survived the scheduled study period and no signs of systemic toxicity or local skin irritation were observed. A relevant increase in ear weights was not observed.
A test item is regarded as a sensitiser in the LLNA if the exposure to one or more test concentration resulted in a 3-fold or greater increase in incorporation of3HTdR compared with concurrent controls, as indicated by the Stimulation Index (S.I.). The estimated concentration of test item required to produce a S.I. of 3 is referred to as the EC3 value.
In this study Stimulation Indices of 1.6, 2.8, and 3.2 were determined with the test item at concentrations of 5, 10, and 25% in ethanol/water (3+7 v/v). A clear dose response was observed. The EC3 value calculated was 17.5%.
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