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EC number: 252-669-5 | CAS number: 35674-68-1
- 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
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Sediment toxicity
Administrative data
Link to relevant study record(s)
Description of key information
Zinc bis[12-hydroxyoctadecanoate]:
Toxicity data are not available for zinc bis[12-hydroxyoctadecanoate]. Read-across to insoluble/ slightly soluble zinc substances is made.
ZINC:
Freshwater: chronic toxicity data are available for 7 species. Species mean NOECs used for PNEC derivation range from 201 to 1135 mg/kg dw. The species mean NOEC added range between 146 to 1101 mg/kg dw (after correction for background). In addition, two field studies are available for freshwater sediments. Lieber et al. 1996 have reported an overall NOECecosystem of 725 mg/kg d.w. added zinc. Burton et al. 2005 have observed minor effects on species richness and macroinvertebrate density at concentration of 119 mg/kg d.w. added zinc.
Marine water: chronic toxicity data are available for 2 marine species: the amphipod Melita plumulosa with a NOEC reproduction of 730 mg/kg dw and the mangrove Avicennia marina with a NOEC emergence of 250 mg/kg dw. After background correction the NOEC values then become 490 mg/kg dw and 207.1 mg/kg dw for M. plumulosa and A. marina, respectively. No field studies were found for marine sediments.
Key value for chemical safety assessment
Additional information
Zinc bis[12-hydroxyoctadecanoate]:
As sediment toxicity data are not available for zinc bis[12-hydroxyoctadecanoate],a read-across to insoluble/ slightly soluble zinc substances is made. It is assumed that upon dissolution or intake zinc bis[12-hydroxyoctadecanoate] is changed in part to ionic zinc and that only ionic zinc is determining biological activities.The ecotoxic potential of the fatty acid chain, i.e. 12-hydroxystearate, is assumed to be negligible. Fatty acids are generally not considered to represent a risk to the environment, which is reflected in their exclusion from REACH registration requirements (c.f. REACH Annex V (Regulation (EC) No 987/2008)). For a comprehensive overview of the toxicity of zinc, see the hazard assessment of "Zinc" within the framework of Regulation (EC) No 1907/2006 in Appendix 1 of the CSR and cited in excerpts below.
ZINC:
Freshwater: chronic toxicity data are available for 7 species. Species mean NOECs used for PNEC derivation range from 201 to 1135 mg/kg dw. The species mean NOEC added range between 146 to 1101 mg/kg dw (after correction for background). In addition, two field studies are available for freshwater sediments. Lieber et al. 1996 have reported an overall NOECecosystem of 725 mg/kg d.w. added zinc. Burton et al. 2005 have observed minor effects on species richness and macroinvertebrate density at concentration of 119 mg/kg d.w. added zinc.
Marine water: chronic toxicity data are available for 2 marine species: the amphipod Melita plumulosa with a NOEC reproduction of 730 mg/kg dw and the mangrove Avicennia marina with a NOEC emergence of 250 mg/kg dw. After background correction the NOEC values then become 490 mg/kg dw and 207.1 mg/kg dw for M. plumulosa and A. marina, respectively. No field studies were found for marine sediments.
Freshwater PNECadd, sediment
The assessment of the freshwaterPNECadd, sedimentfor zinc is based on the chronic benthic toxicity data that were presented in the EU RAR for zinc (2008), complemented with four new high quality studies (species). From the knowledge available at the time of closure, the RAR derived a PNEC using an application factor of 10 on the lowest available NOEC value (488 mg/kg d.w.). Because of the significant increase of information on chronic benthic toxicity, the PNEC from the RAR has been revised. Taking into account the weight of evidence provided by the elements discussed in the chemical safety report, it is considered that use of the HC5 from the SSD, using statistical extrapolation techniques, is justified for PNEC derivation, and that no additional assessment factor needs to be applied. Consequently, the PNEC is set at the level of the HC5 which is considered as protective for EU freshwater ecosystems:freshwaterPNECadd, sediment= 117.8 mg/kg d.w. (equivalent to 25.9 mg/kg w.w.).
Marine PNECadd, sediment
The assessment of the marine PNECadd, sedimentfor zinc identified two long-term chronic toxicity studies. However, an EqP (using partitioning coefficients and a robust aquatic toxicity database) approach provided a reliable derivation for the marine benthic compartment. The resulting value is considered protective for EU marine ecosystems: marine PNECadd, sedimentof 56.5 mg/kg d.w. (equivalent to 12.5 mg/kg w.w.).
[RAR zinc: European Communities, European Union Risk Assessment Report CAS: 7440-66-6 EINECS No: 231-175-3 ZINC METAL, EUR 24587 EN, available via Internet http://echa.europa.eu/documents/10162/d7248de0-eb5b-4a9b-83b9-042c4fd66998]
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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