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EC number: 201-286-1 | CAS number: 80-51-3
- 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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- fish early-life stage toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2016.08.25-2016.11.11
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- Guideline study (OECD 210) according to GLP
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 210 (Fish, Early-Life Stage Toxicity Test)
- Version / remarks:
- July 26, 2013
- Deviations:
- no
- GLP compliance:
- yes
- Specific details on test material used for the study:
- CAS No. 80-51-3
EC No. 201-286-1
KIT Code No.K-5450
Batch/Lot No. 201512001
Appearance: White fine powder
Purity: 99.5-100 %
Expiry date: December, 2016
Storage conditions: Room temperature/ Protect from moisture and light - Analytical monitoring:
- yes
- Details on sampling:
- The concentrations of 4,4’-Oxybis(benzenesulfonyl hydrazide) (OBSH) in the test solution were verified using a HPLC method (see Analytical Report).
An analysis of the test solution was performed in the controls and each exposure concentration on before starting test, at the start, and on day 3, 10, 17, 24, 31, 38 and 45 (at the end) during the study.
A portion (5 mL) of the test solution was taken from each replicate (control and all test concentrations) on 1 day before starting the test, on the day of egg addition (Day 0), Day 3, 10, 17, 24, 31, 38 and 45. All samples were treated according to the recovery test before analysis. - Vehicle:
- yes
- Details on test solutions:
- Dimethylforamide (DMF) was applied as a solvent
- Test organisms (species):
- Oryzias latipes
- Details on test organisms:
- Ricefish (Oryzias latipes)
Source: Fish culture room, Environmental Toxicology and Chemistry Research Center, Gyeongnam Department of Environmental Toxicology and Chemistry, Korea Institute of Toxicology (KIT)
Fertilized eggs, approximately 1-hour-old (1-2 cells stage) at the start of the study. - Test type:
- flow-through
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 45 d
- Remarks on exposure duration:
- Experimental Starting Date August 25, 2016 Experimental Completion Date: November 11, 2016
- Post exposure observation period:
- not included
- Hardness:
- Day 0: Control mean value 33 mg/L (31-35)
Day 45: Control mean value 37.5 mg/L (37-38) - Test temperature:
- ranging from 24.0-25.1 C
- pH:
- ranging from 7.25-7.88
- Dissolved oxygen:
- ranging from 7.51-8.80 mg/L (91-105% of Air Saturation Value),
- Salinity:
- NA
- Conductivity:
- NA
- Nominal and measured concentrations:
- Nominal: control, solvent control, 0.1; 0.31; 0.98; 3.13; 10 mg/L
meassured concentration: ND; ND; 0.09; 0.30; 1,01; 3.28; 10;22 mg/L - Details on test conditions:
- The definitive test employed five test concentrations, together with a dilution water control and solvent control (100 µL DMF/L)
The concentrations were control, solvent control and nominal concentrations of 0.1, 0.31, 0.98, 3.13, 10 mg/L (factor: 3.2 from highest concentration) based on preliminary acute toxicity test as range-finding test.
The test vessel was Teflon aquaria, with approximate dimensions of 16.0 × 7.0 × 9.0 cm (length, width, height) fitted with a surface overflow (7.0 cm above the base), to hold an approximate volume of 800 mL of exposure medium. At the start of study, each test vessel contained one egg container (4 cm diameter), fitted with mesh ends to permit flow of the test solution in the vessel.
Twenty fertilized eggs were placed into each egg container, giving a total of 80 eggs per treatment group. Developing embryos were exposed under continuous flow conditions to the test or control media for a period of 45 days (approximately 15 days pre-hatch plus 30 days post-hatch). The egg containers were removed from the test vessels, when all of the eggs had hatched. - Reference substance (positive control):
- not specified
- Duration:
- 45 d
- Dose descriptor:
- EC50
- Remarks:
- hatching rate success
- Effect conc.:
- 4.36 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Remarks:
- 4.36 mg/L (1.44-25.9)
- Duration:
- 45 d
- Dose descriptor:
- LOEC
- Remarks:
- Hatching rate succes
- Effect conc.:
- 3.28 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Duration:
- 45 d
- Dose descriptor:
- NOEC
- Remarks:
- Hatching rate success
- Effect conc.:
- 1.01 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Duration:
- 45 d
- Dose descriptor:
- LC50
- Remarks:
- post hatch survival
- Effect conc.:
- 0.65 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Remarks:
- 0.65 mg/L (0.45-0.89)
- Basis for effect:
- mortality
- Duration:
- 45 d
- Dose descriptor:
- LOEC
- Remarks:
- Post hatch survival
- Effect conc.:
- 0.3 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 45 d
- Dose descriptor:
- NOEC
- Remarks:
- Post hatch survival
- Effect conc.:
- 0.09 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 45 d
- Dose descriptor:
- LC50
- Remarks:
- Overall survival
- Effect conc.:
- 0.42 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Remarks:
- 0.42 mg/L (0.28-0.57)
- Basis for effect:
- mortality
- Duration:
- 45 d
- Dose descriptor:
- LOEC
- Remarks:
- Overall survival
- Effect conc.:
- 0.3 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 45 d
- Dose descriptor:
- NOEC
- Remarks:
- Overall survival
- Effect conc.:
- 0.09 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- The arithmetic mean was used to calculate overall concentration during test period because all measured concentration within 80-120% of nominal concentration. The arithmetic mean measured concentrations were 0.09, 0.30, 1.01, 3.28 and 10.22 mg/L for 0.1, 0.31, 0.98, 3.13, 10 mg/L of nominal concentration during test period.
- Results with reference substance (positive control):
- No data
- Reported statistics and error estimates:
- The data of hatching rate (hatching success) and normal survival (post hatching survival), normality (overall survival), length and weight at the end of the study were subjected to statistical analysis.
The toxicity value (LCX or ECX or ICX), LOEC and NOEC for each response was analyzed using CETIS Version 1.8.7. 15 (Tidepool Scientific Software, USA) by comparisons of each treatment group to the solvent control group.
In the present study, the solvent control was used for all subsequent comparisons because there were no significant differences between dilution water control and solvent control (by Equal Variance t Two-sample Test and Wilcoxon Rank Sum Two-Sample Test). A parametric test was used to determine if data were normally distributed and whether variances were homogeneous across treatments. If these assumptions were violated, non-parametric tests were used to determine the LOEC and NOEC.
The toxicity effects (ECX or LCX or ICX with 95% confidence limits) of each response of treatment groups compared to the solvent control group were analyzed by Linear regression and linear Interpolation method. The LOEC and NOEC were analyzed by Dunnett Multiple Comparison Test - Validity criteria fulfilled:
- yes
- Conclusions:
- 4,4’-Oxybis(benzenesulfonyl hydrazide) (OBSH) had effects on the hatching success depending on expose concentrations.
(95% confidence limit) LC/EC/IC50 LOEC NOEC
Hatching success rate 4.36 (1.44-25.9) 3.28 1.01
Post-hatching survival 0.65 (0.45-0.89) 0.30 0.09
Overall survival 0.42 (0.28-0.57) 0.30 0.09 - Executive summary:
A 45 days laboratory study was conducted with the test substance 4,4’-Oxybis(benzenesulfonyl hydrazide) (OBSH), applying OECD guideline no 210 and following GLP. The results showed that the test substance had effects on the hatching successd epending on expose concentrations.
Hatching success (rate) ranged from 41.3 to 86.3% in the exposure groups compared to 90.0 and 92.5% for the control and solvent control groups. Up to 11 days, more than 80% of embryos survived at any concentration employed in the test (0.1 to 10 mg/L), however from 12 days, number of dead embryos (absence of heart-beat or body movement) increased depending on concentrations. Finally, the survival rate of embryos was 90, 92.5, 86.3, 72.5, 63.8, 43.8 and 41.8% for control, solvent control, 0.09, 0.30, 1.01, 3.28 and 10.22 mg/L (mean measured concentrations), respectively.
LC/EC/IC50 (95% confidence limit)
LOEC
NOEC
Hatching success rate
4.36 (1.44-25.9)
3.28
1.01
Post-hatching survival
0.65 (0.45-0.89)
0.30
0.09
Overall survival
0.42 (0.28-0.57)
0.30
0.09
Reference
Description of key information
A reliable long-term toxicity study (45 d) to fish has been carried out according to OECD 210, resulting in a NOEC (mortality) of 0.09 mg/L (arithmetic mean).
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- NOEC
- Remarks:
- mortality
- Effect concentration:
- 0.09 mg/L
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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