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EC number: 203-674-6 | CAS number: 109-46-6
- 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
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Specific details on test material used for the study:
- None.
- Key result
- Water solubility:
- 212 mg/L
- Conc. based on:
- act. ingr.
- Loading of aqueous phase:
- 4 g/L
- Incubation duration:
- 72 h
- Temp.:
- 20 °C
- pH:
- 5
- Details on results:
- Test item concentrations determined in samples are presented in Table 1. The test item concentrations in filtered, centrifuged and centrifuged then filtered samples are not significantly different, but samples centrifuged then filtered did not contain any undissolved particles. These samples were thus considered for calculation. Results are presented in table1. As specified in the OECD 105 guideline, the saturation equilibrium was reached: the concentrations measured in at least the two last vessels did not differ by more than 15%, all three samples were thus considered for the final calculation. The temperature in the test systems was monitored during the test, it was remained between 19.9°C and 20.0°C throughout the experiment (mean 19.9°C).
- Conclusions:
- Water solubility of 1,3-dibutyl-2-thiourea is 212 mg/L.
- Executive summary:
The solubility of 1,3 -dibutyl-2 -thiourea was determined according to the OECD 105 guideline, shake-flask method. Three replicate samples of test item (around 1 g) dissolved in ultrapure water were prepared into glass flasks (250 mL of capacity, theoretical concentration of 4 g/L). Samples were diluted with ultrapure and shaken during 5 min, then test vessels were capped and placed in an oven operating at ca 30°C under continuous stirring (with a magnetic stir bar). Three additional glass flasks containing only ultrapure water were also placed within the same conditions (control samples). After ca 24 hours at 30°C, 1 test item sample and 1 control sample were transferred in an oven operating at ca 20°C (agitation was stopped). After 24h, and due to the presence of undissolved test item, an aliquot of the supernatants was filtered through 0.8 and 0.8 µm filters, 1 aliquot was centrifuged (2000 g / 12 minutes) and 1 aliquot was centrifuged then filtered: clear solutions of all samples were analysed according to the available analytical procedure. This protocol was applied to dispose of undissolved particles. The other samples after 48 and 72 days were only centrifuged then filtered. The pH of test item samples were assessed after a cooling period (pH strips); the temperature in the oven was monitored during the whole test. 1,3-dibutylthiourea was analysed with UPLC/MS. Variation on a set of repeated measurements was 0.62% (repeatability). LOQ was 9 µg/L and LOD was 3 µg/L.
The test item concentrations in filtered, centrifuged and centrifuged then filtered samples were not significantly different, but samples centrifuged then filtered did not contain any undissolved particles. These samples were thus considered for calculation. As specified in the OECD 105 guideline, the saturation equilibrium was reached: the concentrations measured in at least the two last vessels did not differ by more than 15%, all three samples were thus considered for the final calculation. The temperature in the test systems was monitored during the test, it was remained between 19.9°C and 20.0°C throughout the experiment (mean 19.9°C). pH was between 4.5 and 5.5
Water solubility of 1,3-dibutyl-2-thiourea is 212 mg/L.
Reference
Table1Definitive test: test item determinations
Time point (hours) |
Control concentration |
Test item concentration (g/L) |
Difference from previous time point (%)* |
Overall Mean Measured Test Item (g/L) |
24 |
<DL |
Filtered sample : 0.216 |
NA |
0.212 |
Centrifuged sample: 0.221 |
||||
Centrifuged & filtered sample: 0.214 |
||||
48 |
<DL |
Centrifuged & filtered sample: 0.217 |
1.4% |
|
72 |
<DL |
Centrifuged & filtered sample: 0.206 |
-5.1% |
*only the centrifuged & filtered sample was considered
NA Not Applicable
< DL (0.0028 mg/L): concentration lower than the Detection Limit of the analytical method
< QL (0.0093 mg/L): concentration lower than the Quantification Limit of the analytical method
Description of key information
The solubility of 1,3-dibutyl-2-thiourea was determined according to the OECD 105 guideline, shake-flask method. Three replicate samples of test item (around 1 g) dissolved in ultrapure water were prepared into glass flasks (250 mL of capacity, theoretical concentration of 4 g/L). Samples were diluted with ultrapure and shaken during 5 min, then test vessels were capped and placed in an oven operating at ca 30°C under continuous stirring (with a magnetic stir bar). Three additional glass flasks containing only ultrapure water were also placed within the same conditions (control samples). After ca 24 hours at 30°C, 1 test item sample and 1 control sample were transferred in an oven operating at ca 20°C (agitation was stopped). After 24h, and due to the presence of undissolved test item, an aliquot of the supernatants was filtered through 0.8 and 0.8 µm filters, 1 aliquot was centrifuged (2000 g / 12 minutes) and 1 aliquot was centrifuged then filtered: clear solutions of all samples were analysed according to the available analytical procedure. This protocol was applied to dispose of undissolved particles. The other samples after 48 and 72 days were only centrifuged then filtered. The pH of test item samples were assessed after a cooling period (pH strips); the temperature in the oven was monitored during the whole test. 1,3-dibutylthiourea was analysed with UPLC/MS. Variation on a set of repeated measurements was 0.62% (repeatability). LOQ was 9 µg/L and LOD was 3 µg/L.
The test item concentrations in filtered, centrifuged and centrifuged then filtered samples were not significantly different, but samples centrifuged then filtered did not contain any undissolved particles. These samples were thus considered for calculation. As specified in the OECD 105 guideline, the saturation equilibrium was reached: the concentrations measured in at least the two last vessels did not differ by more than 15%, all three samples were thus considered for the final calculation. The temperature in the test systems was monitored during the test, it was remained between 19.9°C and 20.0°C throughout the experiment (mean 19.9°C). pH was between 4.5 and 5.5
Water solubility of 1,3-dibutyl-2-thiourea is 212 mg/L.
Key value for chemical safety assessment
- Water solubility:
- 212 mg/L
- at the temperature of:
- 20 °C
Additional information
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