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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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
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EC number: - | 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
GHS
General Information
- Implementation:
- EU
- Type of classification:
- self-classification
- Remarks:
For the short-term toxicological endpoints (acute toxicity, skin-eye corrosion, sensitization, mutagenicity), the classification is based on test data. For all other endpoints (human health, environment), the classification is calculated with the MeClas tool (http://www.meclas.eu), i.e. based on classification of the individual constituents and using available data from elemental composition and available information on speciation.
General approach
An iUVCB substance is a complex substance. Its main characteristics are a known but variable elemental composition and the -in some cases- partly unknown speciation of the constituents.
The classification of the iUVCB is based on the hazard of its constituents and the classification rules for the hazard assessment of mixtures under the UN Globally Harmonised System (GHS) and its EU implementation (CLP). To derive the iUVCB classification, one therefore needs to have information on
- iUVCB variability (elemental concentration),the physical form (e.g. massive, powder),
- the physical form (e.g. massive, powder), the hazard profile for all the elemental constituents, and
- the hazard profile for all the elemental constituents,
- and the speciation of the constituents (and the uncertainty associated if partly unknown the speciation of the constituents (and the uncertainty associated if partly unknown)
The official ECHA guidance (e.g. from the European Chemicals Agency, ECHA for the CLP[1]) is used as basis for the assessment and includes metal-specific guidance.
The unknown constituents speciation and elemental variability are addressed following a precautionary and conservative approach. In practice:
The starting point is the iUVCB composition (as defined in IUCLID 1.2): the composition is provided listing variability (i.e. concentration range) including the available information on the chemical speciation of each constituent (i.e. specifying whether analytical tests could identify if the element is present as oxide, sulfide,…).
- When the speciation of the elemental constituent is known, it is used as such for the classification assessment of the iUVCB; when the speciation of the elemental constituent is unknown, the speciation with the worst-case classification is selected and assigned to the constituent for the iUVCB classification calculation.
- The typical iUVCB variability in elemental constituents (i.e. wide range concentration of the iUVCB constituents) is assessed by selecting a worst-case concentration, which is defined as the maximum of all company typical concentrations for each constituent.
Within one iUVCB substance, the variability in elemental composition can potentially lead to different hazard profiles. Therefore, there can be a practical need (for the purpose of SDS and labelling) to differentiate more hazardous from less hazardous individual streams within the iUVCB. Generic groups/grades/clusters within one iUVCB - each group with a common worst-case classification profile – can be developed and reported in IUCLID to increase general understanding of the variability of the hazard of the iUVCB and to allow registrants to easily derive a worst-case classification for possible new streams.
The MeClas tool (www.meclas.eu) has been developed to facilitate the classification of complex inorganic materials, considering the aspects raised above) is used. The tool allows the use of constituent specific information to derive iUVCB classification based on mixture rules (CLP).
MeClas
The classification of iUVCBs is assessed using the MeClas tool (Metal Classification tool,www.meclas.eu).
MeClas was developed to:
-
deal with the complexity of the hazard classification of complex iUVCBs
-
ensure consistent classification of complex iUVCBs throughout the industry
-
provide full recognition to metal specific aspects
-
provide a platform for relevant data centralisation between metal consortia (self-classifications and (eco)toxicity reference values) and between metal consortia and companies (read-across of speciation and bio-availability tests)
The tool allows the use of constituent specific information to derive iUVCB classification based on mixture rules (CLP).
MeClas is therefore facilitating the hazard identification for complex metal materials under CLP/ DSD/GHS throughout the metal industry.
MeClas is built on a limited number of simple and basic principles:
-
A tiered and inorganic specific approach, allowing refinement in accordance with the following (not necessarily sequential) steps/and available information:
-
Tier 0: elemental concentrations only (and worst-case speciation and worst-case 100% solubility)
-
Tier 1: speciation data and mineralogical evidence
-
Tier 2: correction based on release/solubility test data on the complex material
-
An up-to-date database including the official EU harmonised (Annex VI of the CLP and subsequent ATPs) and self-classifications, specific concentration limits, M-factors, (eco)toxicity reference values (ERVs) values,…
-
An open building block structure, enabling the inclusion of specific side modules if relevant (e.g. for ores and concentrates, for transport classification, additional reference lists (e.g. Japan), alloys, etc.). The core engine contains the UN-GHS, CLP (and DSD/DPD) hazard ID rulings, forming the base of the MeClas tool.
- Confidentiality assurance for proprietary information: confidentiality of proprietary data is assured by having the ERVs for such substances hidden from normal users of the tool in a dedicated layer of MeClas.
Self-classification of the iUVCB substance was performedusing the MeClas toolbased on the following outline:
i. Characterisation
The material is accurately described from its elemental composition (typical concentrations and concentration ranges across production sites –IUCLID Section 1.2), and the specific speciation data (mineralogical information, hazard) obtained from representative samples. This information is estimated sufficient to initiate the classification process.
ii. Classification by the Mixture Approach
The iUVCB is treated as a complex metal containing substance with a number of discrete constituents (i.e. chemical element with discrete speciation). The hazard classifications of each compound are then factored into a combined classification of the iUVCB as a whole. For health endpoints, iUVCB classifications are based on the combined hazards of the compounds (i.e. chemical element with discrete speciation) whereby additivity or key cut off levels, specified in look-up tables are used, depending on the endpoint and amount of information available for the constituting compounds. These concepts and rules are incorporated in the MeClas tool.
iii. Bridging
(Eco)-toxicological data are not available for the specific iUVCBs being evaluated. Considering the knowledge and variability in composition, read-across and bridging are done by using a "representative" mineralogical/speciation analysis" combined with the "worst case" elemental concentration (across companies) as a basis for the classification of the iUVCB substance (chemical and mineralogical surrogates with similar origin/production process and physical/chemical properties).
iv. Optional correction for bioavailability (Tier 2 in MeClas)
MeClas fulfills the OECD principles for validation of (Q)SARs model
- Well defined end points
- Unambiguous algorithmfrom EU CLP Guidance: summation/additivity formula, to determine classification and, back-calculation (via Acute Toxicity Estimate formula, etc) to derive the corresponding toxicity of the substance
- Clear applicability domain: applicable to classify complex metal containing materials in a Tiered approach (see EU CLP Guidance pg 499 Annex IV.5.5, and for conceptual outline ICMM Fact Sheet “Ores & Concentrates –An industry approach to EU hazard classification”, November 2009). Input information at tier 1: elemental composition and representative mineralogical information
- Mechanistic interpretation
- Mechanistic interpretation - metal speciation:
The tool translates the elemental composition into a mineralogical composition relevant for classification (i.e. mineralogical distribution pattern for each element/constituent of the iUVCB substance).
In the Tier 1, the classification is derived (by means of the summation formula) without taking into account any bioavailability correction. In the Tier 2, the classification is derived (e.g. for environment by means of the additivity formula) taking into account bioavailability correction.
- Mechanistic interpretation - metal-ion additivity for environment:
(1) The additivity assumption for the toxicity of mixtures of metals was evaluated by C. Nys, TVan Regenmortel, CR Janssen, K Oorts, E Smolders & KAC De Schamphelaere, (2018). A framework for ecological risk assessment of metal mixtures in aquatic systems. (Environ. Toxicol. Chem. 37, 623–642).The additivity mode was judged conservative for the prediction of the toxicity of metal mixture at low effect concentrations in a meta-analysis of chronic metal mixture toxicity to freshwater organisms.
(2) A. Stockdale, E Tipping, S Lofts & SJ Ormod, combined metal speciation to the additive toxicity approach and predicted the combined metal toxicity in a range of UK river systems impacted by metals: in "Modeling multiple metal toxic effects in the field - evaluation of the Toxicity Binding Model (TBM) ", ICA Report November 2009.
[1]ECHA, July 2017. Guidance on the Application of the CLP Criteria. Guidance to Regulation (EC) No 1272/2008 on classification, labelling and packaging (CLP) of substances and mixtures.
Related composition
- Related composition:
- pNMC oxide (typical,generic)
- pNMC oxide (typical,generic)
- composition NiMnCo Oxide
- composition NiMnCo Oxide
Classificationopen allclose all
Explosives
- Reason for no classification:
- data conclusive but not sufficient for classification
Flammable gases and chemically unstable gases
- Reason for no classification:
- data conclusive but not sufficient for classification
Aerosols
- Reason for no classification:
- data conclusive but not sufficient for classification
Oxidising gases
- Reason for no classification:
- hazard class not applicable
Gases under pressure
- Reason for no classification:
- hazard class not applicable
Flammable liquids
- Reason for no classification:
- hazard class not applicable
Flammable solids
- Reason for no classification:
- data conclusive but not sufficient for classification
Self-reactive substances and mixtures
- Reason for no classification:
- data conclusive but not sufficient for classification
Pyrophoric liquids
- Reason for no classification:
- hazard class not applicable
Pyrophoric solids
- Reason for no classification:
- data conclusive but not sufficient for classification
Self-heating substances and mixtures
- Reason for no classification:
- data conclusive but not sufficient for classification
Substances and mixtures which in contact with water emit flammable gases
- Reason for no classification:
- data conclusive but not sufficient for classification
Oxidising liquids
- Reason for no classification:
- hazard class not applicable
Oxidising solids
- Reason for no classification:
- data conclusive but not sufficient for classification
Organic peroxides
- Reason for no classification:
- hazard class not applicable
Corrosive to metals
- Reason for no classification:
- data conclusive but not sufficient for classification
Desensitized explosives
- Reason for no classification:
- hazard class not applicable
Acute toxicity - oral
- Reason for no classification:
- data conclusive but not sufficient for classification
Acute toxicity - dermal
- Reason for no classification:
- hazard class not assessed
Acute toxicity - inhalation
- Reason for no classification:
- data conclusive but not sufficient for classification
Skin corrosion / irritation
- Reason for no classification:
- data conclusive but not sufficient for classification
Serious eye damage / eye irritation
- Reason for no classification:
- data conclusive but not sufficient for classification
Respiratory sensitisation
- Reason for no classification:
- hazard class not assessed
Skin sensitisation
- Reason for no classification:
- data conclusive but not sufficient for classification
Aspiration hazard
- Reason for no classification:
- hazard class not applicable
Reproductive toxicity
- Hazard category:
- Repr. 1B
- Hazard statement:
- H360: May damage fertility or the unborn child <state specific effect if known > <state route of exposure if it is conclusively proven that no other routes of exposure cause the hazard>.
Effects on or via lactation
- Reason for no classification:
- data lacking
Germ cell mutagenicity
- Reason for no classification:
- data conclusive but not sufficient for classification
Carcinogenicity
- Hazard category:
- Carc. 1A
- Hazard statement:
- H350: May cause cancer <state route of exposure if it is conclusively proven that no other routes of exposure cause the hazard>.
1. Specific target organ toxicity - single (STOT-SE)
- Reason for no classification:
- data conclusive but not sufficient for classification
1. Specific target organ toxicity - repeated (STOT-RE)
- Hazard category:
- STOT Rep. Exp. 1
- Hazard statement:
- H372: Causes damage to organs <or state all organs affected, if known> through prolonged or repeated exposure <state route of exposure if it is conclusively proven that no other routes of exposure cause the hazard>.
- Affected organs:
- lungs
Hazardous to the aquatic environment (acute / short-term)
- Reason for no classification:
- data conclusive but not sufficient for classification
Hazardous to the aquatic environment (long-term)
- Hazard category:
- Aquatic Chronic 2
- Hazard statement:
- H411: Toxic to aquatic life with long lasting effects.
Hazardous to the ozone layer
- Reason for no classification:
- data lacking
Labelling
- Signal word:
- Danger
Hazard pictogram
- GHS08: health hazard
- GHS09: environment
Hazard statements
- H350i: May cause cancer by inhalation.
- H360Fd: May damage fertility. Suspected of damaging the unborn child.
- H372: Causes damage to organs <or state all organs affected, if known> through prolonged or repeated exposure <state route of exposure if it is conclusively proven that no other routes of exposure cause the hazard>.
- H411: Toxic to aquatic life with long lasting effects.
Precautionary statements
- P201: Obtain special instructions before use.
- P260: Do not breathe dust/fume/gas/mist/vapours/spray.
- P280: Wear protective gloves/protective clothing/eye protection/face protection/hearing protection/...
- P308+P313: IF exposed or concerned: Get medical advice/attention.
- P314: Get medical advice/attention if you feel unwell.
- P405: Store locked up.
- P501: Dispose of contents/container to ...
Notes
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.