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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
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 2004
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- Study conducted according to OECD 111. In compliance with GLP. No degradation products identified.
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Principles of method if other than guideline:
- NA
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
NA - Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- No data
- Buffers:
- No data
- Estimation method (if used):
- NA
- Details on test conditions:
- Test was conducted at 25 degrees celcius and at 3 different pH (4, 7 and 9)
- Number of replicates:
- no data
- Positive controls:
- not specified
- Negative controls:
- not specified
- Statistical methods:
- no data
- Preliminary study:
- The half life of OBSH at 25 degrees celcius was:
pH 4: 9.2 h
pH 7: 7.9 h
pH 9: 5.8 h
At 37 degrees celcius the half life > 5 days - Transformation products:
- not specified
- Details on hydrolysis and appearance of transformation product(s):
- Hydrolysis products are not identified in this study.
- pH:
- 4
- Temp.:
- 20 °C
- DT50:
- 23.1 h
- pH:
- 7
- Temp.:
- 20 °C
- DT50:
- 17.2 h
- pH:
- 9
- Temp.:
- 20 °C
- DT50:
- 13.9 h
- pH:
- 4
- Temp.:
- 25 °C
- DT50:
- 9.2 h
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 7.9 h
- pH:
- 9
- Temp.:
- 25 °C
- DT50:
- 5.8 h
- pH:
- 4
- Temp.:
- 30 °C
- DT50:
- 3.76 h
- pH:
- 7
- Temp.:
- 30 °C
- DT50:
- 3.72 h
- pH:
- 9
- Temp.:
- 30 °C
- DT50:
- 2.46 h
- Other kinetic parameters:
- no data
- Details on results:
- The half life of OBSH at 25 degrees celcius was:
9.2 h at pH 4
7.9 h at pH 7
5.8 h at pH 9
However, hydrolysis products are not identified in this study. - Validity criteria fulfilled:
- not specified
- Conclusions:
- The half life of OBSH at 25 degrees celcius was:
9.2 h at pH 4
7.9 h at pH 7
5.8 h at pH 9
These data suggest that OBSH is hydrolytically unstable over a range of environmentally relevant pH and temperature conditions. - Executive summary:
The stability of OBSH was tested applying the OECD Guideline no 111. Three different pH were tested (4,7 and 9) at one temperature (25 degrees celcius).
The half life of OBSH at 25 degrees celcius was:
9.2 h at pH 4
7.9 h at pH 7
5.8 h at pH 9
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 7 OCT 2020 to 7 JUNE 2021
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Guideline for testing of chemcial, National Institute of Environmental Research (Notice No. 2020-28 (19, August 2020) - South Korea
- Deviations:
- no
- Principles of method if other than guideline:
- NA
- GLP compliance:
- yes
- Specific details on test material used for the study:
- - Chemicall name: 4,4´-Oxybis(benzenesulfonyl hydrazide) (OBSH)
- CAS No: 80-51-3
- Lot No: 202007001
- Facility code No: 2020/00054
- Received date: 09 September 2020
- Manufacture date: 02 July 2020
- Expiration date: 01 July 2021
- Received quantity: 180.68 g (incl. container weight)
- Molecular formular: C12H14N4O5S2
- Molecular weight: 358.39 g/mol
- Apperance: white fine powder
- Purity: 98.1%
- Solubility: DMSO, DMF
- Storage conditions: Room temperature, protect from light, no exposure to high temperatures - Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- Analysis of the test substance:
Tier 1: The concentration of the test substance for all samples was measured for 5 days at 24 hour intervals.
Tier 2: The concentration of the test substance for all samples was analyzed in time at a minimum of six points normally between 10 % and 90 % hydrolysis of
the test substance.
Tier 3: Identification of hydrolysis products was not performed. - Buffers:
- Buffer solution:
The sterilized buffer solutions of different pH values (pH 4.00, 7.00 and 9.00)
were prepared from the annex (Buffer mixtures of Clark and Lubs) of the OECD test guideline. This buffer solutions were aerated to free from nitrogen for 5 minutes before preparation of the test solution. The pH of each buffer solution was checked with a calibrated pH meter before exposure to the test substance. - Estimation method (if used):
- NA
- Details on test conditions:
- Test conditions
Temperature:
- Tier 1: nominal temperature : 50.0±0.5 ℃, actual temperature : 49.8~50.1 ℃
- Tier 2: nominal temperature : 25.0±0.5 ℃, 50.0±0.5 ℃, 70.0±0.5 ℃, actual temperature : 25.1~25.2 ℃, 50.1~50.2 ℃, 69.9~70.1 ℃.
The Tier 2 was performed in a dark and sterile condition in a series of procedures to prevent photolytic effect and biodegradation of the test substance.
Test methods
Tier 1
- Test concentration : 8.2×10-4 M (300.000 mg/L) for pH 4.00, 7.00, 9.00
- Replicate : Duplicate per test sample (pH 4.00, 7.00 and 9.00)
- Temperature : 50.0±0.5 ℃
- Test duration : 5 days
- Test solution : 250 mL per replicate
Tier 2
- Test concentration : 8.2×10-4 M (300.000 mg/L) for pH 4.00, 7.00, 9.00
- Replicate : Duplicate per test sample (pH 4.00, 7.00 and 9.00)
- Temperature : 25.0±0.5 ℃, 50.0±0.5 ℃, 70.0±0.5 ℃
Preparation of test solution:
- Tier 1 (Preliminary test): Considering the purity of the test substance (98.1 %) and solubility (1.69×10^-3 M, 604.7 mg/L, 1 % DMSO), the test solution of nominal concentration (8.2×10^-4 M, 300.000 mg/L) was prepared by dissolving the test substance in the buffer solutions (pH 4.00, 7.00 and 9.00) of 1,000 mL. Nominal concentration of the test substance was not exceed half of the solubility concentration. The test solution of nominal concentration was prepared on the day of exposure.
- Tier 2 (Hydrolysis of unstable substances): Considering the purity of test substance (98.1 %) and solubility (1.69×10^-3 M, 604.700 mg/L, 1 % DMSO), the test solution of nominal concentration (8.2×10^-4 M, 300.000 mg/L) was prepared by dissolving the test substance in the buffer solutions (pH 4.00, 7.00 and 9.00) of 2,000 mL. Nominal concentration of the test substance did not exceed half of the solubility concentration. The test solution of nominal concentration was prepared on the day of exposure.
- Tier 3 (Identification of hydrolysis products)
According to information provided by the sponsor, it is expected that Hydrazine monohydrate and 4,4’-oxybis(benzenesulfonic acid) are the main hydrolysis products. This is based on the molecular structure of 4,4’-Oxybis(benzenesulfonylhydrazide)(OBSH) and available hydrolysis data from previous testing. An analytical method for quantification of Hydrazine monohydrate was conducted in a pilot study using HPLC. However, validation of the analytical method of Hydrazine monohydrate was not possible, because the sensitivity was not good enough (LOD: 32.044 mg/L, LOQ: 97.104 mg/L). Therefore, analytical quantification of hydrazine monohydrate was technically not feasible. Based on molecular formula (H6H2O) and molecular weight (50.06 g/mol), the theoretical concentration of Hydrazine monohydrate is 4.1×10^-5 mg/L when 4,4’-Oxybis(benzenesulfonylhydrazide) (OBSH) is completely hydrolyzed at nominal concentration of 8.2×10^-4 M (300 mg/L) and converted to Hydrazine monohydrate. Since no analytical standard for 4,4’-oxybis(benzenesulfonic acid) can be purchased, it was not possible to analytically quantify the substance in this study. A Tier 3 test was not performed, because it was technically not feasible to analytically quantify the degradation products Hydrazine monohydrate and 4,4’-oxybis(benzenesulfonic acid).
For another analysis of hydrolysis product 4,4’-oxybis(benzenesulfonic acid) (non-GLP), the samples for each pH were collected in conical tubes (about 5 ml) at the end of the Tier 2 test and delivered to an external lab (please refer to the attached document for details). Since analytical standard for 4,4'-oxybis(benzenesulfonicacid) could not be purchased, the structure was predicted using both a liquid-chromatography mass spectrometer(LC-MS) (please refer to the attached document). 4,4'-oxybis(benzenesulfonicacid) was monitored using a positive and negative electrospray mode recording set at m/z 330.9 and 328.9 respectively, which are consistent with [M+H]+ and [M-H]- molecular ions. - Duration:
- 5 d
- pH:
- 4
- Temp.:
- 25 °C
- Initial conc. measured:
- ca. 300 mg/L
- Remarks:
- Nominal concentration: 8.2×10-4 M (300 mg/L); Also tested at 50 and 70 °C
- Duration:
- 5 d
- pH:
- 7
- Temp.:
- 25 °C
- Initial conc. measured:
- ca. 300 mg/L
- Remarks:
- Nominal concentration: 8.2×10-4 M (300 mg/L); Also tested at 50 and 70 °C
- Duration:
- 5 d
- pH:
- 9
- Temp.:
- 25 °C
- Initial conc. measured:
- ca. 300 mg/L
- Remarks:
- Nominal concentration: 8.2×10-4 M (300 mg/L); Also tested at 50 and 70 °C
- Number of replicates:
- duplicate per test sample (pH 4, 7 and 9)
- Positive controls:
- no
- Negative controls:
- no
- Statistical methods:
- no
- Test performance:
- An analytical method for quantification of Hydrazine monohydrate was conducted in a pilot study using HPLC. However, validation of the analytical method of Hydrazine monohydrate was not possible, because the sensitivity was not good enough (LOD: 32.044 mg/L, LOQ: 97.104 mg/L). Therefore, analytical quantification of hydrazine monohydrate was technically not feasible.
Since analytical standard for 4,4'-oxybis(benzenesulfonicacid) could not be purchased, the structure was predicted using both a liquid-chromatography mass spectrometer(LC-MS) (please refer to the attached document). As a result, no mass values(m/z) of the substance were detected, and no expected fragmentation values were detected. Therefore, the measurement results showed that structural interpretation linkage and interpretation were not possible and that the substance could not be quantified properly. - Transformation products:
- not measured
- Remarks:
- technically not feasible
- No.:
- #1
- No.:
- #2
- Details on hydrolysis and appearance of transformation product(s):
- Hydrolysis products could not be analytically identified. However, theoretical concentration of the two hydrolysis products can be calculated (25°C) using the measured rate constants. Please refer to the Executive Summary.
- Key result
- pH:
- 4
- Temp.:
- 25 °C
- Hydrolysis rate constant:
- ca. 0.059 h-1
- DT50:
- ca. 11.7 h
- Type:
- (pseudo-)first order (= half-life)
- Key result
- pH:
- 4
- Temp.:
- 50 °C
- Hydrolysis rate constant:
- ca. 0.079 h-1
- DT50:
- ca. 8.8 h
- Type:
- (pseudo-)first order (= half-life)
- Key result
- pH:
- 4
- Temp.:
- 70 °C
- Hydrolysis rate constant:
- ca. 0.104 h-1
- DT50:
- ca. 6.7 h
- Type:
- (pseudo-)first order (= half-life)
- Key result
- pH:
- 7
- Temp.:
- 25 °C
- Hydrolysis rate constant:
- ca. 0.088 h-1
- DT50:
- ca. 7.9 h
- Type:
- (pseudo-)first order (= half-life)
- Key result
- pH:
- 7
- Temp.:
- 50 °C
- Hydrolysis rate constant:
- ca. 0.1 h-1
- DT50:
- ca. 6.9 h
- Type:
- (pseudo-)first order (= half-life)
- Key result
- pH:
- 7
- Temp.:
- 70 °C
- Hydrolysis rate constant:
- ca. 0.133 h-1
- DT50:
- ca. 5.2 h
- Type:
- (pseudo-)first order (= half-life)
- Key result
- pH:
- 9
- Temp.:
- 25 °C
- Hydrolysis rate constant:
- ca. 0.118 h-1
- DT50:
- ca. 5.9 h
- Type:
- (pseudo-)first order (= half-life)
- Key result
- pH:
- 9
- Temp.:
- 50 °C
- Hydrolysis rate constant:
- ca. 0.15 h-1
- DT50:
- ca. 4.6 h
- Type:
- (pseudo-)first order (= half-life)
- Key result
- pH:
- 9
- Temp.:
- 70 °C
- Hydrolysis rate constant:
- ca. 0.273 h-1
- DT50:
- ca. 2.5 h
- Type:
- (pseudo-)first order (= half-life)
- Other kinetic parameters:
- NA
- Details on results:
- Results of Tier 1:
The half life of OBSH at 25 degrees celcius was:
pH 4: 11.7 h
pH 7: 7.9 h
pH 9: 5.9 h
The half life of OBSH at 50 degrees celcius was:
pH 4: 8.8 h
pH 7: 6.9 h
pH 9: 4.6 h
The half life of OBSH at 70 degrees celcius was:
pH 4: 6.7 h
pH 7: 5.2 h
pH 9: 2.5 h
Results of Tier 2:
During the test period, the actual temperature values in water bath for 25.0 (pH 4.00, 7.00 and 9.00), 50.0 (pH 4.00, 7.00 and 9.00) and 70.0 ℃ (pH 4.00, 7.00 and 9.00) were maintained constantly in range of 25.1~25.2 ℃, 50.1~50.2 ℃ and 69.9~70.1 ℃, respectively.The pH values of the test solution for pH 4.00 (25.0, 50.0 and 70.0 ℃), 7.00 (25.0, 50.0 and 70.0 ℃) and 9.00 (25.0, 50.0 and 70.0 ℃) were 4.02~4.09, 7.03~7.05 and 8.94~9.07, respectively.
The hydrolysis rate constant (kobs) and half-life (t0.5) for the exposure conditions (25, 50 and 70 ℃ for pH 4.00, 7.00 and 9.00) of the test substance were calculated by the concentration of the test substance according to the
exposure time (see table on key results above). - Results with reference substance:
- NA
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The stability of OBSH was tested applying the OECD Guideline no 111. Three different pH were tested (4, 7 and 9) at 3 temperatures (25 °C, 50°C and 70°C).
The hydrolysis half-life of OBSH at 25 °C was 11.7 hours (pH 4); 7.0 hours (pH 7) and 5.9 hours (pH 9).
The hydrolysis half-life of OBSH at 50 °C was 8.8 hours (pH 4); 6.9 hours (pH 7) and 4.6 hours (pH 9).
The hydrolysis half-life of OBSH at 70 °C was 6.7 hours (pH 4); 5.2 hours (pH 7) and 2.5 hours (pH 9).
The results from this key study is in agreement with the reported half-lives in the study reported in the OECD SIDS document (section 5.1.12 - Hydrolysis.03).
Based on the molecular structure of OBSH and available hydrolysis data from previous tests (section 5.1.2 – hydrolysis), it is expected that hydrazine and 4,4’-oxybis(benzenesulfonic acid) are the main hydrolysis products. This is in agreement with the assessments stated in the recent CLH report for harmonized classification of OBSH.
No standard form for 4,4’-oxybis(benzenesulfonic acid) can be purchased, so it was not possible to analyse for the substance.
Evaluation of hydrazine was performed using Hydrazine monohydrate as standard. Hydrazine monohydrate was dissolved in the buffer solutions (pH 4, 7, 9) and then analyzed using HPLC. A quite poor sensitivity was found for this substance with a LOD of 32.044 mg/L and a LOQ of 97.104 mg/L. The hydrazine is not expected to dissipate to a very high degree during the study (it will in natural surface waters), so would be expected that at detection but not a quantification of the hydrazine would be expected. Even so, there has been analytical problems for a proper identification of hydrazine in the samples after hydrolysis. - Executive summary:
Hydrolysis rates:
The stability of OBSH was tested applying the OECD Guideline no 111. Three different pH were tested (4, 7 and 9) at 3 temperatures (25 °C, 50°C and 70°C).
The hydrolysis half-life of OBSH at 25 °C was 11.7 hours (pH 4); 7.0 hours (pH 7) and 5.9 hours (pH 9).
The hydrolysis half-life of OBSH at 50 °C was 8.8 hours (pH 4); 6.9 hours (pH 7) and 4.6 hours (pH 9).
The hydrolysis half-life of OBSH at 70 °C was 6.7 hours (pH 4); 5.2 hours (pH 7) and 2.5 hours (pH 9).
The results from this key study is in agreement with the reported half-lives in the study reported in the OECD SIDS document (section 5.1.12 - entry Hydrolysis.03).
This enables the estimation of the coefficient for the rate constant expression of hydrolysis:
khydrolysis= kalkaline×[OH-]+kneutral+kacid×[H+]
Temperature (°C(
*kH(hr-1(mol/l)-1
KOH(hr-1(mol/l)-1
kN(hr-1)
25
-282
3001.463
0.087
40
-212
5071.421
0.010
70
-284
14538.71
0.132
*the negative kH actual indicates that there is no acid catalyzed hydrolysis.
And dependency of temperature according to an Arrhenius equation:
khydrolysis= khydrolysis,0×exp(-A/T), T being the absolute temperature.
pH
khydrolysis,0 (hr-1)
A (K)
4
1.3732
1255.6
7
0.6248
920.77
9
4.1035
1882.7
Hydrolysis products:
Based on the molecular structure of OBSH and available hydrolysis data from previous tests (section 5.1.2 – hydrolysis), it is expected that hydrazine and 4,4’-oxybis(benzenesulfonic acid) are the main hydrolysis products. This is in agreement with the assessments stated in the recent CLH report for harmonized classification of OBSH.
After the 5 days study at an initial concentration of OBSH of 300 mg/L, the below degree of degradation of OBSH and theoretical concentration of the two hydrolysis products can be calculated (25°C) using the measured rate constants:
pH
-
4
7
9
OBSH
Mg/L
0.25
0.0080
0.00023
Hydrazine
Mg/L
83.7
83.8
83.8
4,4’-oxybis(benzenesulfonic acid)
Mg/L
276
277
277
No standard form for 4,4’-oxybis(benzenesulfonic acid) can be purchased, so it was not possible to analyse for the substance.
Evaluation of hydrazine was performed using Hydrazine monohydrate as standard. Hydrazine monohydrate was dissolved in the buffer solutions (pH 4, 7, 9) and then analyzed using HPLC. A quite poor sensitivity was found for this substance with a LOD of 32.044 mg/L and a LOQ of 97.104 mg/L. The hydrazine is not expected to dissipate to a very high degree during the study (it will in natural surface waters), so would be expected that at detection but not a quantification of the hydrazine would be expected. Even so, there has been analytical problems for a proper identification of hydrazine in the samples after hydrolysis.
Referenceopen allclose all
Specific identification of hydrolysis products was not possible. Based on the molecular structure of OBSH and available hydrolysis data from previous tests (see 5.1.2 – hydrolysis), it is expected that hydrazine and 4,4’-oxybis(benzenesulfonic acid) are the main hydrolysis products. It was not possible to analyse for 4,4’-oxybis(benzenesulfonic acid).
Evaluation of hydrazine was performed using Hydrazine monohydrate as standard. Hydrazine monohydrate was dissolved in the buffer solution (pH 4, 7, 9) and then analyzed. But the degradation occurred quite rapidly, and it seems that the peak of the target was overlapped with the buffer solution. Also, the detection limit was higher than the real concentration, so it was concluded that the analysis was impossible and technically unfeasible.
Specifically, Hydrazine monohydrate was analyzed by HPLC as a hydrolysis product of OBSH. As a result of the analysis of Hydrazine monohydrate, the sensitivity was not good when it was analyzed by HPLC, the LOD was 32.044 mg/L and the LOQ was 97.104 mg/L.
Overall, the following results was derived:
- OBSH concentration: 8.2×10-4 M(300 mg/L)
- Hydrazine monohydrate molecular weight: 50.06 g/mol
- When OBSH is completely hydrolysed and converted to Hydrazine monohydrate, the concentration is 4.1×10-5 mg/L.
Description of key information
The stability of OBSH was tested applying the OECD Guideline no 111. Three different pH were tested (4,7 and 9) at one temperature (25 degrees celcius). The half life of OBSH at 25 degrees celcius was:
11.7 h at pH 4
7.9 h at pH 7
5.9 h at pH 9
Key value for chemical safety assessment
- Half-life for hydrolysis:
- 7.9 h
- at the temperature of:
- 25 °C
Additional information
Data from a new study is available supporting the already available data on hydrolysis of OBSH.
Hydrolysis rates
The stability of OBSH was tested applying the OECD Guideline no 111. Three different pH were tested (4, 7 and 9) at 3 temperatures (25 °C, 50°C and 70°C).
The hydrolysis half-life of OBSH at 25 °C was 11.7 hours (pH 4); 7.0 hours (pH 7) and 5.9 hours (pH 9).
The hydrolysis half-life of OBSH at 50 °C was 8.8 hours (pH 4); 6.9 hours (pH 7) and 4.6 hours (pH 9).
The hydrolysis half-life of OBSH at 70 °C was 6.7 hours (pH 4); 5.2 hours (pH 7) and 2.5 hours (pH 9).
The results from the key study is in agreement with the reported half-lives in the study reported in the SIDS document (entry Hydrolysis.03).
This enables the estimation of the coefficient for the rate constant expression of hydrolysis.
khydrolysis= kalkaline×[OH-]+kneutral+kacid×[H+]
Temperature (°C( | *kH(hr-1(mol/l)-1 | KOH(hr-1(mol/l)-1 | kN(hr-1) |
25 | -282 | 3001.463 | 0.087 |
40 | -212 | 5071.421 | 0.010 |
70 | -284 | 14538.71 | 0.132 |
*the negative kH actual indicates that there is no acid catalyzed hydrolysis.
And dependency of temperature according to an Arrhenius equation:
khydrolysis= khydrolysis,0×exp(-A/T), T being the absolute temperature.
pH | khydrolysis,0 (hr-1) | A (K) |
4 | 1.3732 | 1255.6 |
7 | 0.6248 | 920.77 |
9 | 4.1035 | 1882.7 |
Hydrolysis products
Based on the molecular structure of OBSH and available hydrolysis data from previous tests (see 5.1.2 – hydrolysis), it is expected that hydrazine and 4,4’-oxybis(benzenesulfonic acid) are the main hydrolysis products. This is in agreement with the assessments stated in the recent CLH report for harmonized classification of OBSH.
After the 5 days study at an initial concentration of OBSH of 300 mg/L, the below degree of degradation of OBSH and theoretical concentration of the two hydrolysis products can be calculated (25°C) using the measured rate constants:
pH | - | 4 | 7 | 9 |
OBSH | Mg/L | 0.25 | 0.0080 | 0.00023 |
Hydrazine | Mg/L | 83.7 | 83.8 | 83.8 |
4,4’-oxybis(benzenesulfonic acid) | Mg/L | 276 | 277 | 277 |
No standard form for 4,4’-oxybis(benzenesulfonic acid) can be purchased, so it was not possible to analyse for the substance.
Evaluation of hydrazine was performed using Hydrazine monohydrate as standard. Hydrazine monohydrate was dissolved in the buffer solutions (pH 4, 7, 9) and then analyzed using HPLC. A quite poor sensitivity was found for this substance with a LOD of 32.044 mg/L and a LOQ of 97.104 mg/L. The hydrazine is not expected to dissipate to a very high degree during the study (it will in natural surface waters), so would be expected that at detection but not a quantification of the hydrazine would be expected. Even so, there has been analytical problems in a proper identification of hydrazine in the samples after hydrolysis.
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