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EC number: 241-602-5 | CAS number: 17625-03-5
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- adopted 30. May 2008
- Deviations:
- yes
- Remarks:
- Details on devistions from EU Method C.2 have been reported in section "Any other information on materials and methods incl. tables".
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- adopted 13. Apr. 2004: ”Daphnia sp., Acute Immobilisation Test“.
- Deviations:
- yes
- Remarks:
- Details on devistions from OECD Guideline 202 have been reported in section "Any other information on materials and methods incl. tables".
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Batch no.: 170103
Appearance: White crystalline powder
CAS No.: 17625-03-5
EINECS-No.: 241-602-5
Molecular formula: C7H5SO5Na
Molecular weight: 224.17 g/mol
Purity: > 99.0% (Titration with NaOH, Glass indicating electrode, Calomel reference electrode)
Homogeneity: totally homogeneous
Stability: H2O: 96h; EtOH: unknown; acetone: unknown; CH3CN: unknown; DMSO: unknown
Solubility: H2O: >1 g/L; EtOH: unknown; acetone: unknown; CH3CN: unknown; DMSO: unknown
Production date: 2017
Expiry date: 14. Feb. 2024
Storage: Room Temperature (20 ± 5°C), keep away from humidity - Analytical monitoring:
- yes
- Details on sampling:
- Preparation
A stock solution containing 99.8 mg/L test item in dilution water was prepared. For homogenisation, an ultrasonic bath was used. The lower concentrations were prepared by dilution of this stock solution with dilution water. - Vehicle:
- yes
- Remarks:
- water
- Details on test solutions:
- A stock solution containing 99.8 mg/L test item in dilution water was prepared. For homogenisation, an ultrasonic bath was used. The lower concentrations were prepared by dilution of this stock solution with dilution water.
Treatments: 4.6 / 10 / 22 / 46 / 100 mg/L (nominal concentration)
The concentrations to be tested are based on the result of a non-GLP pre-test.
Test vessels: glass beakers, nominal volume 50 mL, tall shape
Replicates (Treatments): 4 vessels, each containing 20 ± 5 mL test solution and 5 daphnia
Replicates (Blank control): 4 vessels, each containing 20 ± 5 mL dilution water and 5 daphnia. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Species: Daphnia magna
Authority: STRAUS
Strain: Berlin
Sex: female
Age: between 0 and 24 hours
Origin: Umweltbundesamt Berlin
Selection of the test system was made following the proposal of the guidelines.
Animal Husbandry
Daphnia magna is bred in the LAUS GmbH throughout the year. The animals are kept for the use in toxicity tests. They multiply by parthenogenesis, thus being genetically identical. The keeping is performed similar to the method described in the OECD guideline, following SOP 115 002 01 ("Zucht und Hälterung von Daphnia magna STRAUS"), version 13 from 11. Nov. 2019.
Vessels preserving glasses, nominal volume 2 L
Medium: M4-Medium (recipe of ELENDT)
Food: green algae (Desmodesmus subspicatus)
Medium: renewal twice a week
Photo period: 16/8 hours, using neon tubes
Temperature: 20 +/- 2 °C - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- Please, see section "salinity".
- Test temperature:
- The temperature in the experiment was in the range of 19.1 – 21.2 °C and; therefore, fluctuated by more than ± 1 °C. As all validity criteria were met and no immobility in the blank control was occurred, this was stated as uncritical.
- pH:
- Blank control; pH = 7.6 (0 h); pH = 7.9 (48 h)
Nominal Concentration (mg/L) = 4.6; pH = 7.6 (0 h); pH = 7.9 (48 h)
Nominal Concentration (mg/L) = 10; pH = 7.5 (0 h); pH = 7.9 (48 h)
Nominal Concentration (mg/L) = 22; pH = 7.4 (0 h); pH = 7.9 (48 h)
Nominal Concentration (mg/L) = 46; pH = 7.3 (0 h); pH = 7.8 (48 h)
Nominal Concentration (mg/L) = 100; pH = 6.9 (0 h); pH = 7.8 (48 h) - Dissolved oxygen:
- Blank control; O2 = 8.5 (0 h); O2 = 8.2 (48 h)
Nominal Concentration (mg/L) = 4.6; O2 = 8.5 (0 h); O2 = 8.4 (48 h)
Nominal Concentration (mg/L) = 10; O2 = 8.5 (0 h); O2 = 8.5 (48 h)
Nominal Concentration (mg/L) = 22; O2 = 8.6 (0 h); O2 = 8.5 (48 h)
Nominal Concentration (mg/L) = 46; O2 = 8.6 (0 h); O2 = 8.5 (48 h)
Nominal Concentration (mg/L) = 100; O2 = 8.6 (0 h); O2 = 8.4 (48 h) - Salinity:
- Dilution water (Daphnia medium) with the following specification was used (stated in SOP 11800201)
Concentration in mg/L
CaCl2*2H2O = 293.80 mg/L
MgSO4*7H2O = 123.30 mg/L
NaHCO3 = 64.80 mg/L
KCl = 5.80 mg/L - Conductivity:
- Not determined.
- Nominal and measured concentrations:
- Nominal Concentration Test Item (mg/L) = 4.6
Mean Measured Concentration t = 0 h (mg/L) = 4.55
Mean Measured Concentration t = 48 h (mg/L) = 4.97
Nominal Concentration Test Item (mg/L) = 10
Mean Measured Concentration t = 0 h (mg/L) = 10.11
Mean Measured Concentration t = 48 h (mg/L) = 10.85
Nominal Concentration Test Item (mg/L) = 22
Mean Measured Concentration t = 0 h (mg/L) = 22.24
Mean Measured Concentration t = 48 h (mg/L) = 24.51
Nominal Concentration Test Item (mg/L) = 46
Mean Measured Concentration t = 0 h (mg/L) = 45.91
Mean Measured Concentration t = 48 h (mg/L) = 51.60
Nominal Concentration Test Item (mg/L) = 100
Mean Measured Concentration t = 0 h (mg/L) = 100.17
Mean Measured Concentration t = 48 h (mg/L) = 110.17 - Details on test conditions:
- Treatments 4.6 / 10 / 22 / 46 / 100 mg/L (nominal concentration)
The concentrations to be tested are based on the result of a non-GLP pre-test.
Temperature 19.1 – 21.2 °C
Photo period 16/8 hours, using neon tubes
Duration 48 hours
Observation times at 24 and 48 hours
Medium renewal: none
Test vessels glass beakers, nominal volume 50 mL, tall shape
Replicates (Treatments) 4 vessels, each containing 20 ± 5 mL test solution and 5 daphnia
Replicates (Blank control) 4 vessels, each containing 20 ± 5 mL dilution water and 5 daphnia - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 94.59 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95%-confidence interval = 76.81 - 136.18 mg/L
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 70.83 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95%-confidence interval = 58.84 - 85.53 mg/L
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 46 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- Further details on results are reported in section "Any other information on results incl. tables".
- Validity criteria fulfilled:
- yes
- Conclusions:
- Short-term toxicity of sodium 3-sulfobenzoate towards Daphnia magna has been determined according to EU C.2 Method and the following results were determined:
48h-NOEC = 46 mg/L
48h-LOEC = 100 mg/L
24h-EC50 = 94.59 mg/L
48h-EC50 = 70.83 mg/L - Executive summary:
Short-term toxicity of sodium 3-sulfobenzoate towards Daphnia magna has been determined according to EU C.2 Method. One valid experiment was performed. The study was performed using 5 concentrations ranging from 4.6 to 100 mg/L nominal concentration. For each test concentration and the blank control, 20 daphnia were exposed to the test item for 48 hours in a static test system. After 24 and 48 hours, the immobilised daphnia were counted.
The two highest concentrations containing 46 mg/L and 100 mg/L showed toxicity between 15 and 85% immobilisation. One of the animals was immobilised in the blank control. This 5% immobilisation can be neglected.
Potassium dichromate K2Cr2O7 (CAS No. 7778-50-9) was used as positive control in a current reference study to assure that the test conditions are reliable.
The measured concentrations at the beginning and the end of the test lay between 99 % and 112 % of the nominal concentrations. Therefore, the determination of the results was based on the nominal concentrations (see OECD Guidance Doc. No.23).
The following results were determined for the test item sodium 3-sulfobenzoate:
48h-NOEC = 46 mg/L
48h-LOEC = 100 mg/L
24h-EC50 = 94.59 mg/L
48h-EC50 = 70.83 mg/L
Reference
Immobility
In the blank control, one of the daphnia was immobilised. The two highest concentrations containing 46 mg/L and 100 mg/L showed toxicity between 15 and 85% immobilisation.(see table below):
Table. Immobility.
Nominal Concentration in mg/L |
Immobility 24 hours |
Immobility 48 hours |
||||||||
absolute |
in % |
absolute |
in % |
|||||||
Blank control |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
5 |
4.6 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
5 |
10 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
5 |
22 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
5 |
46 |
0 |
0 |
1 |
0 |
5 |
0 |
2 |
1 |
0 |
15 |
100 |
4 |
2 |
4 |
1 |
55 |
5 |
4 |
4 |
4 |
85 |
pH and O2
The pH values and the concentration of dissolved oxygen in the test media and the blank control are given in the following table.
Table. pH and O2-values.
Nominal Concentration in mg/L |
pH |
O2-Concentration in mg/L |
||
0 h |
48 h |
0 h |
48 h |
|
Blank control |
7.6 |
7.9 |
8.5 |
8.2 |
4.6 |
7.6 |
7.9 |
8.5 |
8.4 |
10 |
7.5 |
7.9 |
8.5 |
8.5 |
22 |
7.4 |
7.9 |
8.6 |
8.5 |
46 |
7.3 |
7.8 |
8.6 |
8.5 |
100 |
6.9 |
7.8 |
8.6 |
8.4 |
Analytical Determinations
At the start and at the end of the test, the content of the test item in the test solutions was determined using HPLC.
The QC samples were measured in duplicate at the beginning and end of each sequence.
The measured concentrations lay between 99 % and 112 % of the nominal concentrations. Therefore, the determination of the results was based on the nominal concentrations (see OECD Guidance Doc. No.23).
The measured concentrations for treatment and blank control are given in the following tables.
Table. Raw Data and Measured Concentrations.
Nominal |
Area |
Area |
Dilution Factor |
Measured Concentration |
Measured Concentration |
mg/L |
|
|
|
mg/L |
mg/L |
QC 10 mg/L |
6.0378 |
5.8189 |
-- |
10.000 |
10.000 |
QC 10 mg/L |
6.0167 |
5.7777 |
-- |
10.000 |
10.000 |
Blank control |
n.a. |
n.a. |
-- |
0.00 |
0.00 |
Blank control |
n.a. |
n.a. |
-- |
0.00 |
0.00 |
4.6 |
2.8690 |
2.8862 |
-- |
4.608 |
4.906 |
4.6 |
2.7926 |
2.9607 |
-- |
4.483 |
5.034 |
10 |
6.1080* |
6.3426 |
-- |
9.873 |
10.853 |
10 |
6.1079 |
6.3419 |
-- |
9.873 |
10.852 |
22 |
6.8563 |
7.1405 |
2 |
22.180 |
24.452 |
22 |
6.8932 |
7.1763 |
2 |
22.300 |
24.575 |
46 |
10.0878* |
5.9947 |
5 |
81.718 |
51.273 |
46 |
5.6804 |
6.0708 |
5 |
45.891 |
51.927 |
100 |
6.1695 |
6.4418 |
10 |
99.734 |
110.237 |
100 |
6.2229 |
6.4337 |
10 |
100.603 |
110.099 |
46 |
5.6902** |
-- |
5 |
45.971 |
-- |
10 |
6.3973** |
-- |
-- |
10.344 |
-- |
QC 10 mg/L |
11.6296* |
5.8392 |
-- |
10.000 |
10.000 |
QC 10 mg/L |
6.2389 |
5.9513 |
-- |
10.000 |
10.000 |
n.a. not analysable
* Results not used, because interference signals
** Repetition of measurement due to interference signals
Table. Mean of Measured Concentrations and % of Nominal Concentration.
Nominal |
Mean Measured Concentration |
Mean Measured Concentration |
% of Nominal |
% of Nominal t = 48 h |
mg/L |
mg/L |
mg/L |
% |
% |
4.6 |
4.55 |
4.97 |
99 |
108 |
10 |
10.11 |
10.85 |
101 |
109 |
22 |
22.24 |
24.51 |
101 |
111 |
46 |
45.91 |
51.60 |
100 |
112 |
100 |
100.17 |
110.17 |
100 |
110 |
Description of key information
Short-term toxicity of sodium 3-sulfobenzoate towards Daphnia magna has been determined according to EU C.2 Method. One valid experiment was performed. The study was performed using 5 concentrations ranging from 4.6 to 100 mg/L nominal concentration. For each test concentration and the blank control, 20 daphnia were exposed to the test item for 48 hours in a static test system. After 24 and 48 hours, the immobilised daphnia were counted.
The two highest concentrations containing 46 mg/L and 100 mg/L showed toxicity between 15 and 85% immobilisation. One of the animals was immobilised in the blank control. This 5% immobilisation can be neglected.
Potassium dichromate K2Cr2O7 (CAS No. 7778-50-9) was used as positive control in a current reference study to assure that the test conditions are reliable.
The measured concentrations at the beginning and the end of the test lay between 99 % and 112 % of the nominal concentrations. Therefore, the determination of the results was based on the nominal concentrations (see OECD Guidance Doc. No.23).
The following results were determined for the test item sodium 3-sulfobenzoate:
48h-NOEC = 46 mg/L
48h-LOEC = 100 mg/L
24h-EC50 = 94.59 mg/L
48h-EC50 = 70.83 mg/L
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 70.83 mg/L
Additional information
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