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EC number: 221-656-6 | CAS number: 3179-31-5
- 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
Water solubility
Administrative data
- Endpoint:
- water solubility
- 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:
- 2 019
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
Test material
- Reference substance name:
- 1,2,4-triazole-3-thiol
- EC Number:
- 221-656-6
- EC Name:
- 1,2,4-triazole-3-thiol
- Cas Number:
- 3179-31-5
- Molecular formula:
- C2H3N3S
- IUPAC Name:
- 4H-1,2,4-triazole-3-thiol
- Test material form:
- solid: crystalline
Constituent 1
Results and discussion
Water solubility
- Key result
- Water solubility:
- 89.76 g/L
- Conc. based on:
- test mat.
- Loading of aqueous phase:
- 500 g/L
- Incubation duration:
- >= 24 - <= 72 h
- Temp.:
- 20 °C
- pH:
- 5
Any other information on results incl. tables
The measurements of the day 1-3 were included in the calculation of the mean.
Table8.3‑a Measurements used for Calculation of Solubility
Day |
Flask |
Concentration [g/L] |
Total Mean [g/L] |
Total Standard Deviation [g/L] (RSD* [%]) |
1 |
1 A |
89.51 |
89.76 |
1.44 (1.6) |
2 |
1 B |
89.14 |
||
3 |
1 C |
88.11 |
||
3 |
2 |
89.18 |
||
3 |
3 |
89.25 |
||
3 |
4 |
89.18 |
||
3 |
5 |
92.73 |
||
3 |
6 |
91.01 |
*RSD = relative standard deviation
Mean at the plateau is 89.76 g/L. A standard deviation of 1.44 g/L was calculated, giving a relative standard deviation of 1.6 %.
Temperature was measured with 20.1 - 20.5 °C.
Applicant's summary and conclusion
- Conclusions:
- The solubility of 3-Mercapto-1,2,4-triazole in water was determined from the measured concentrations in the filtrated test solutions with 89.76 g/L.
All replicates showed good correspondence. Standard deviation of the samples, which were used for the calculation of water solubility, was 1.44 g/L, corresponding to a relative standard deviation of 1.6 %.
Equilibration was considered to be reached after 1 day, as no further increase in solubility was noticed after 1 day. Therefore, all flasks were taken into account for the final calculation of the solubility.
All replicates showed very good correspondence. Standard deviation of the test item concentration in all measured flasks was very low.
No observations arousing doubts concerning the accuracy of the results and the validity of the study were made. - Executive summary:
The solubility of the test item3-Mercapto-1,2,4-triazolein water was determined by measurement of the test item concentration in the filtrated test solutions using HPLC.
In the pre-tests no complete dissolution was achieved for test item / water-mixtures with nominal concentration 10 g/L. Therefore, flasks with nominal concentrations 50 g/L and
10 g/L were treated 30 minutes in ultrasonic bath and shaken at room temperature for one day. Then, the test item concentration was measured after membrane filtration (0.45 µm, PTFE) to test for concentration dependency Undissolved particles were observed in both flasks. Dependency of solubility on amount of the test item (nominal load) was assumed. According to the guideline, the flask method was used for the determination of the solubility of the test item in water.In the main test,six different loading rates of the test item were chosen to study the effect of the loading rate on the measured water solubility: 100, 200, 400, 500, 600, and 800 g/L (nominal). Three flasks 1A - C with the same loading rate (500 g/L) were used during equilibration. Seven vessels (flasks blank, 1C (for the sampling point 72 h) and 2 – 6) were set onto the shaking apparatus immediately. After 24 ± 2 hours, flask 1B (for the sampling point 48 h) and after 48 ± 2 hours, flask 1A (for the sampling point 24 h) were set on the shaker and all flasks were shaken for further 24 ± 2 hours at room temperature (20.0 ± 0.5 °C). Then, flasks 1A - 1C were taken from the shaker, samples were taken, membrane filtered and analysed via HPLC.
No rising tendency in concentration of the solutions was found on day 3. No differences above 15% in the concentration of the solutions could be determined between the sampling dates 2 and 3, supporting the hypothesis, that the maximum concentration of the test item had been reached. Therefore, the flasks 2 - 6 were sampled, filtrated and analysed.
No Tyndall effect (i.e. a laser beam was not scattered when transmitted through the liquid) could be observed indicatingthat no colloidal dispersed particles or micells are present.
Dependency of solubility on amount of the test item (nominal load) was not perceived in the main study. A low relative standard deviation of 1.6 % was obtained for the measured concentrations in all flasks.
At the plateau, the concentration of3-Mercapto-1,2,4-triazolein water had reached
89.76 ± 1.44 g/L at 20.1 – 20.5 °C
= 89.76 ± 1.44 kg/m3(SI units)
(mean value ± standard deviation of eight individual vessels)
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