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Diss Factsheets
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EC number: 915-093-1 | CAS number: -
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- GLP guideline study. Reliability assigned by a secondary source (OECD SIDS Initial Assessment Report). Only secondary source reviewed, as primary study was not available.
- Justification for type of information:
- 1. HYPOTHESIS FOR THE CATEGORY APPROACH: The hypothesis is that properties are likely to be similar or follow a similar pattern because of the presence of a common metal ion, in this case tungstate.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES):
Source: Tungsten Carbide
Target: Fused tungsten carbide
3. CATEGORY APPROACH JUSTIFICATION: See Annex 3 in CSR
4. DATA MATRIX: See Annex 3 in CSR - Reason / purpose for cross-reference:
- read-across: supporting information
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Strain: STRAUSS
- Source: Federal Health Office, Berlin Germany
- Age at study initiation (mean and range, SD): 2-24 hours.
- Feeding during test: None - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- N/A
- Test temperature:
- 21 +/- 1 ⁰C
- pH:
- 7.5 - 7.9
- Dissolved oxygen:
- 9 mg/L
-The oxygen saturation was >= 60 % (21 ⁰C) at the end of testing. - Nominal and measured concentrations:
- 32, 58, 100, 180, 320, 580, 1000 mg/L.
- Details on test conditions:
- TEST SYSTEM:
-Keeping water: M4 medium according to Elendt/Federal Health Office (BGA), Berlin Germany (1992).
-Photoperiod: 10 hours light.
-Illumination: diffuse light, illumination strength 1.5 – 5 umol*m-2*s-1.
-Test vessel: glass beakers, volume 50 mL, 20 mL test medium, not ventilated.
-Number of daphnia per beaker: 5 daphnids.
-Number of replicate: 4 plus 1 control.
-Test parameter: immobilization. - Key result
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 580 mg/L
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 1 000 mg/L
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Details on results:
- The test substance was not soluble in dilution water in a concentration of 1000 mg/l. The test substance was deposited on the ground.
The recovery rates of the active ingredient at the end of the test were > 80 %. For that reason effect level concentrations are given as nominal concentrations.
The percentage of immobility was determined in all concentration groups and controls after 24 and 48 h. Effects = 10 % are not regarded as significant for the EC0 values. EC0 values were determined directly from the test results. The highest concentrations that did not result in 0 % incapability of swimming during the test period were:
- 24h-EC0 = 1000 mg/L
- 48h-EC0 = 580 mg/L
None of the test concentrations resulted in 100 % incapability of swimming during the test period:
- 24h-EC100 = >1000 mg/L
- 48h-EC100 = >1000 mg/L
From the test results a 48h-EC50 of >1000 mg/L was derived.
None of the control daphnids were incapable of swimming at the end of the test or swam on the surface - Reported statistics and error estimates:
- no data
- Validity criteria fulfilled:
- yes
- Conclusions:
- 48 hour EC50 >1000 mg/L
- Executive summary:
No aquatic invertebrate short-term toxicity data of sufficient quality are available for fused tungsten carbide (target substance). However, aquatic invertebrate short-term toxicity data are available for tungsten carbide (source substance), which will be used for read-across. Due to similar water solubility and lower toxicity for the target substance compared to the source substance, the resulting read-across from the source substance to the target substance is appropriate. In addition, read-across is appropriate because the classification and labelling is similar for the source substance than the target substance, the PBT/vPvB profile is the same, and the dose descriptors are, or are expected to be, lower for the source substance. For more details, refer to the read-across category approach included in the Category section of this IUCLID submission and/or as an Annex in the CSR.
Reference
Description of key information
Fused tungsten carbide was not tested for short-term toxicity to aquatic invertebrates and read-across to tungsten carbide was used for this endpoint. The test substance was not soluble in dilution water in a concentration of 1000 mg/l. The percentage of immobility was determined in all concentration groups and controls after 24 and 48 h. Effects are not regarded as significant for the EC0 values. EC0 values were determined directly from the test results. From the test results a 48h-EC50 of >1000 mg/L was derived. None of the control daphnids were incapable of swimming at the end of the test or swam on the surface.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 1 000 mg/L
Additional information
No aquatic invertebrate short-term toxicity data of sufficient quality are available for fused tungsten carbide (target substance). However, aquatic invertebrate short-term toxicity data are available for tungsten carbide (source substance), which will be used for read-across. Due to similar water solubility and lower toxicity for the target substance compared to the source substance, the resulting read-across from the source substance to the target substance is appropriate. In addition, read-across is appropriate because the classification and labelling is similar for the source substance than the target substance, the PBT/vPvB profile is the same, and the dose descriptors are, or are expected to be, lower for the source substance. For more details, refer to the read-across category approach included in the Category section of this IUCLID submission and/or as an Annex in the CSR
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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