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EC number: 234-919-5 | CAS number: 12040-43-6
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- November 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 106 (Adsorption - Desorption Using a Batch Equilibrium Method)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.18 (Adsorption / Desorption Using a Batch Equilibrium Method)
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- batch equilibrium method
- Media:
- soil
- Radiolabelling:
- no
- Test temperature:
- The test was performed at 22.5 ± 0.5 °C.
- Analytical monitoring:
- yes
- Details on sampling:
- In the preliminary test, one soil/solution ratio with the highest amount of soil was tested only: 1 : 1 (30 g soil and 30 mL test solution).
For equilibration, the air-dried soil samples (30 g each) were shaken with 27 mL of a 0.01 M CaCl2-solution for 2 days. After this time, 3 mL of filtrated test item stock solution (nominal concentration 50 g/L, see chapter 4.1.3) was added to 27 mL preparations to result in a test item solution with nominal concentration 5 g/L.To the blank samples 3 mL of a 0.01 M
CaCl2-solution was added. Six replicates of mixtures with the test item solution per soil were prepared (two replicates per sampling time: 0 h, 24 h and 48 h). Six blanks per soil and one replicate of CaCl2 solution (without test item) was prepared in order to determine the background signal. - Details on test conditions:
- The mixtures were shaken for 48 h at 22.5 °C. After 1 minute shaking two replicates with the test item and two blanks per soil were sampled as an initial value
(0 h). The initial concentration of silicon in the stock solution was determined with 8.30 mg/L Si. - Key result
- Type:
- log Koc
- Remarks on result:
- other: According the test results the determination of the adsorption of Silicic acid Aluminium Magnesium Sodium Salt on soils is not possible.
- Details on results (Batch equilibrium method):
- In the blank solutions on day 0, the concentration of silicon was higher than the silicon concentration in the test item solutions after subtraction of the blank value. Furthermore, the measured silicon concentration in the test solution with soil Lufa 2.2 has changed from 8.30 mg/L to 5.34 mg/L Si after one minute shaking of the solution with the soil. The concentration of silicon in Eurosoil 5 after one minute shaking lay in the similar range as the start value in the stock solution (8.48 mg/L Si).
During the test the measured silicon concentration in the blank solutions with soil Lufa 2.2 and Eurosoil 5 increased incessantly from 11.06 to 17.02 mg/L Si and from 8.50 to 21.08 mg/L Si, respectively, despite the 48 h equilibration phase before start of the test. After 48 h test duration, the concentration of silicon in Eurosoil 5 test item solution remained unchanged in comparison to the start vale (0 h). In contrast, the concentration of silicon in Lufa 2.2 test item solution was 59 % lower than the initial value, although the value in the blank solution increased incessantly. This is probably due to the precipitation of silicon in Lufa 2.2 test item solution during the test instead of adsorption, as different Si ions were probably present in the test mixture (obtained from the soil and from the test item). Furthermore, the properties of dissolved silicon are strongly dependent on the pH value. The measured pH values in Eurosoil 5 and in Lufa 2.2 test item solutions were 3.1 and 6.8, respectively. - Conclusions:
- The determination of the adsorption of Silicic acid Aluminium Magnesium Sodium Salt on soils is not possible.
- Executive summary:
Testing of the adsorption of Silicic acid, aluminium magnesium sodium salt on soils according OECD 106 failed, in a preliminary study to determine the concentration of silicon in the blank value in comparison to the test item solution the the concentration of silicon was higher than the silicon concentration in the test item solution after subtraction of the blank value.
Test solution (test item) and soil contain beside same cations (natrium, magnesium, aluminium) also silicon on both sides. Depending on parameters like reaction time, pH value etc. various equilibrium concentrations of silicon in soil and test solution occured including transfer of silicon from soil to test solution. Therefore an analytical determination of adsorption is technically not possible.
Reference
Table: Mean Concentrations on Day 0
Soil |
Sample |
Mean Value Si |
Amount Si – blank |
Mean Value Si |
RSD |
mg/L |
mg/L |
mg/L |
% |
||
Eurosoil 5 |
Blank 1 and 2 |
8.50 |
- |
- |
0.5 |
Flask 1 |
17.18 |
8.68 |
8.48 |
3.2 |
|
Flask 2 |
16.79 |
8.29 |
|||
Lufa 2.2 |
Blank 1 and 2 |
11.06 |
- |
- |
3.8 |
Flask 1 |
16.14 |
5.08 |
5.34 |
6.9 |
|
Flask 2 |
16.67 |
5.60 |
Table: Results
Soil |
Sample |
Mean Value Si on day 0 |
Mean Value Si after 24 h |
Mean Value Si after 48 h |
Difference after 48 h |
mg/L |
mg/L |
mg/L |
% |
||
Eurosoil 5 |
Blank |
8.50 |
15.71 |
21.08 |
+147.9 |
Test Solution* |
8.48 |
8.09 |
8.52 |
+0.5 |
|
Lufa 2.2 |
Blank |
11.06 |
14.59 |
17.02 |
+.53.9 |
Test Solution* |
5.34 |
2.87 |
2.18 |
-59.1 |
*the concentration of Si after subtraction of the blank value
Description of key information
Testing of the adsorption of Silicic acid, aluminium magnesium sodium salt on soils according OECD 106 failed:
Test solution (test item) and soil contain beside same cations (natrium, magnesium, aluminium) also silicon on both sides. Depending on parameters like reaction time, pH value etc. various equilibrium concentrations of silicon in soil and test solution occured including transfer of silicon from soil to test solution. Therefore an analytical determination of adsorption is technically not possible.
Key value for chemical safety assessment
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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