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EC number: 432-520-2 | CAS number: 232938-43-1
- 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
Specific investigations: other studies
Administrative data
- Endpoint:
- mechanistic studies
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study meets basic scientific principles. The principles of the method are similar to OECD guideline 455. Instead of transfected hERα-HeLa-9903 cells, stably transfected MCF-7 ERE-Luc cells were used in the current study. At the highest positive control concentration the induction of luciferase activity was not maximal. Some discrepancies between study protocol and raw data were obvious (e.g. concentration range of 17-beta-estradiol from 0-300 pM was stated in the study protocol. Raw data however, suggested a dose range from 0 to 150 pM). Data on cytotoxicity are not well documented. Although some deviations to OECD guideline 455 occurred, the study is considered to be acceptable with restrictions.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 000
- Report date:
- 2000
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: OECD guideline 455 (Stably Transfected Human Estrogen Receptor-α Transcriptional Activation Assay for Detection of Estrogenic Agonist-Activity of Chemicals) (2009)
- Deviations:
- yes
- Remarks:
- Instead of transfected hERα-HeLa-9903 cells, stably transfected MCF-7 ERE-Luc cells were used. The luciferase activity after treatment with positive control was not maximal.
- Principles of method if other than guideline:
- The method based on principles similar to OECD guideline 455. However, instead of transfected hERα-HeLa-9903 cells, stably transfected MCF-7 ERE-Luc cells were used. Therefore, no acceptable range values as given in the OECD guideline 455 for hERα-HeLa-9903 cells are available. It is however mentioned in the guideline, that despite the assay using the hERα-HeLa-9903 cell line, further ER transcriptional activation assays are currently being developed and validated.
- GLP compliance:
- no
- Type of method:
- in vitro
- Endpoint addressed:
- not applicable
Test material
- Reference substance name:
- -
- EC Number:
- 432-520-2
- EC Name:
- -
- Cas Number:
- 232938-43-1
- Molecular formula:
- C21 H20 N2 O6 S2
- IUPAC Name:
- 3-{[(4-methylbenzenesulfonyl)carbamoyl]amino}phenyl 4-methylbenzene-1-sulfonate
Constituent 1
Administration / exposure
- Route of administration:
- other: test substance is added to the growth medium
- Vehicle:
- ethanol
- Details on exposure:
- The MCF-7 luciferase induction assay is an in vitro technique to identify estrogenic and anti-estrogenic compounds. Human breast carcinoma MCF-7 cells stably transfected with an estrogen receptor-controlled luciferase reporter gene construct were used in this study (MCF-7 ERE-Luc; Pons et al., Biotechniques 9; 450-457, 1990). These cells express firefly luciferase in response to estrogen agonists. Luciferase activity is measured using a plate-scanning luminometer. The technique has been modified from the published procedure to be conducted in 96-well plates. The potential to induce luciferase activity was assessed by comparing the response after treatment with the response after treatment wit positive control (E2).
Cell Culture
Human breast carcinoma cells (MCF-7 ERE-Luc) were seeded into 96 well culture plates and cultured in medium supplemented with either defined fetal bovine serum (FBS for routine culturing) or charcoal-stripped FBS (for treatment and exposure period).
Cells were routinely cultured at 37° C and 5% CO2 in a humidified atmosphere.
Treatment of Cells and Luciferase Assay
24 hr after seeding, medium was changed to a medium containing reduced estrogen (dextran-coated charcoal-stripped FBS) and cells were dosed with either no treatment (blanks), solvent only, Estrogen (E2), or test substances.
Cells were dosed in triplicate with E2 in ethanol (0-150 pM final concentration) or test compounds dissolved in ethanol at doses of 0 - 6500 µM. Luciferase activity was measured by incubating cells with LucLiteTM reagent (Packard Instruments) for twenty minutes at room temperature. Light production, a measure of luciferase activity, was determined with a luminometer at 30° C. Confluence of wells was verified microscopically. A normalization to protein was stated to be not necessary. Therefore, luciferase activity is reported as either relative light units (RLU) or percent of solvent control. According to the standard operation protocol (included in the study report) viability of cells was assessed prior the measurement of luminescence to exclude cytotoxicity. - Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- cells were exposed to test substance in medium for 3 days
- Frequency of treatment:
- continous fore 3 days
- Post exposure period:
- none
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0.065, 0.65, 6.5, 65, 650, 6500 µM
Basis:
nominal conc.
Examinations
- Examinations:
- Increase in luciferase activity was measured as marker for ER-alpha induction.
- Positive control:
- 17-beta-estradiol (E2) in concentrations of 0.5, 1.5, 5, 15, 50, 150 pM was used as positive control.
Nonylphenol (a substance known for estrogenicity) was used in concentrations of 0.5, 5, 50, 500, 5000 and 50000 nM.
Results and discussion
- Details on results:
- A slight increase of luciferase activity was seen at concentrations close to the solubility limit of the test substance (at and above 65 µM the luciferase activity was 115 to 122 % of control). Since the luciferase activity at the highest positive control concentration was not maximal, relative potencies compared to 17-beta-estradiol were only estimated. Relative potency of this sample was calculated to be approximately E+7-fold less potent than E2. In comparison, nonylphenol (a substance known for its estrogenicity) was about 1E+4 to3E+4 less active then 17-beta-estradiol.
Any other information on results incl. tables
Table1: ER-alpha dependent increase in luciferase activity (RLU and % of control)
|
17-beta-estradiol (E2) |
Controls |
|||||||
Concentration[pM] |
0.5 |
1.5 |
5 |
15 |
50 |
150 |
Blank |
solvent |
Mean |
Mean RLU (xE-2) |
1.96 |
2.50 |
3.31 |
4.76 |
5.80 |
6.24 |
2.14 |
2.29 |
2.22 |
% of control |
88 |
113 |
149 |
215 |
262 |
282 |
97 |
104 |
100 |
|
TEST SUBSTANCE |
Controls |
|||||||
Concentration [µM] |
0.065 |
0.65 |
6.5 |
65 |
650 |
6500 |
Blank |
solvent |
Mean |
Mean RLU (xE-2) |
1.88 |
2.08 |
2.25 |
2.54 |
2.70 |
2.71 |
2.14 |
2.29 |
2.22 |
% of control |
85 |
94 |
102 |
115 |
122 |
123 |
97 |
104 |
100 |
The luciferase activities seen after treatment with test substance (RLU) corresponded to -8.5, -3.5, 0.8, 8.0, 11.9 and 12.2 % of maximal luciferase activity at 6.5E-8, 6.5E-7, 6.5E-6, 6.5E-5, 6.5E-4 and 6.5E-3 M. The calculation based on luciferase activities (RLU) after subtraction of background activity (control = 0.222 RLU).Data regarding cytotoxicity given in the study protocol were not well documented.
Applicant's summary and conclusion
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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