Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 231-130-8 | CAS number: 7440-21-3
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
The low solubility of silicon may be the reason that the number of studies can be found regarding the aquatic toxicity of Si/silica is limited. No studies on acute or chronic aquatic effect of elemental silicon have been located. More often it is the impurities of commercial substances which may raise some concern over Si-based industrial products rather than the Si-element itself. For sparingly soluble substances such as metals and metalloids, environmental hazard assessments can be performed using data on particle dissolution and metal release by using the OECD T/Dp (transformation/dissolution) protocol (OECD 2001). The principle of the T/D protocol is to determine the concentration of metal elements that are released from sparingly water soluble substances. These data are then compared with data that are already available for each of the elements to determine if the concentration released is above the concentration expected to cause an effect in the environment. Information on the different elements and their potential effects to the environment is discussed in the following section.
Information regarding solubility of silicon:
Silicon powder dissolves relatively sparingly in distilled water, but dissolves to much higher extent in natural waters (e.g. in brackish and sea water). Technically aquatic reliable and valid tests for silicon (applying dissolved material) can be carried out.
The solubility of silicon for particles sized less than 0.05 mm of Si HG, Si LG and PCS after 168 hours of exposure at 100 mg/l load were tested and results, as dissolved %, are as follows:
Silicon HG 12 % ± 0.7 % (at pH 7.2)
Silicon LG 3.2 % ± 0.2 % (at pH 7.2)
Silicon PCS 32 % ± 1 % (at pH 7.2)
Normally, the dissolved fraction in ecotoxicity tests refers to the fraction that passes through a filter of 0.45 μm. It should be noted, however, that this definition may not necessarily refer to the metals/elements in solution. In the range of 0.01- 0.45 μm colloid inert particles remain suspended.
Soluble amorphous silica or sparingly soluble forms of silica have been studied on aquatic species, fish, daphnia and algae in few studies. These results can be used partly as a read across/Weight of Evidence approach (WoE) material in support of the silicon hazard assessment.
Performing ecotoxicity tests on sparingly water soluble substances, and in particular metals and metalloids, can be problematic. Therefore, the Transformation/Dissolution (T/D) protocol is recommended as a first tier for assessing testing requirements (OECD 2001). The T/D protocol has been performed on Silicon (low grade) for a period of 7 and 28 days representing potential acute and chronic effects respectively. The T/D protocol is a relevant approach particularly for sparingly water soluble metals. The 7 day test is only representative of acute toxicity, and for substances which are produced/imported at high tonnage, chronic data may be required which can be obtained from the full 28 day transformation/ dissolution protocol.
The T/D test protocols were performed (7 and 28 days) according to the methods presented in section 4.1.1.1 (Lillicrap et al, 2011). In addition, the results from the T/Dp tests are also presented in section 4.1.1.1 and are summarised below in Table A10.:
Table A10. 7 day transformation/dissolution data.
Identification |
conc (mg/L) |
pH |
Cu(μg/L) |
Pb (μg/L) |
Si (mg/L) |
Zn (μg/L) |
DWC (7day) |
- |
6 |
3.69 |
0.034 |
<0.02 |
1.28 |
- |
8.5 |
1.13 |
0.02 |
0.26 |
1.18 |
|
Si low grade (7 day) |
1 |
6 |
2.26 |
0.029 |
<0.02 |
1.18 |
1 |
8.5 |
0.67 |
0.01 |
0.27 |
1.07 |
|
10 |
6 |
3.92 |
0.027 |
<0.02 |
1.81 |
|
10 |
8.5 |
0.78 |
0.006 |
0.26 |
1.44 |
|
100 |
6 |
3.03 |
0.030 |
<0.02 |
2.16 |
|
100 |
8.5 |
0.69 |
0.008 |
0.24 |
0.95 |
|
DWC (28 day) |
5.5 |
2.37 |
0.0310 |
<0.02 |
1.72 |
|
8.5 |
0.88 |
<0.005 |
0.26 |
1.40 |
||
Si low grade (28 day) |
5.5 |
6.89 |
0.028 |
<0.02 |
1.59 |
|
8.5 |
0.76 |
<0.005 |
0.28 |
0.81 |
Comparing the data from the 7 and 28 day T/Dp tests with the limits recommended in the EU Risk Assessment Reports (RAR) as shown in Lillicrap et al. (2010), the data indicate that the impurities present in the silicon (low grade) should not cause an effect to aquatic organisms and hence these substances should require no further testing and silicon does not require environmental hazard classification.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.