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Diss Factsheets
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EC number: 248-370-4 | CAS number: 27253-29-8
- 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
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- Species:
- other: animal and human data
Additional information
- all available proprietary studies from the Metal carboxylates REACH Consortium (MCRC)
- detailed literature searches in online databases
- screening of human health review articles
- rigorous quality and reliability screening according to Klimisch criteria, where those criteria apply
Introductionto read-across matrix
A comprehensive data gap analysis was conducted for the entire substance portfolio of the Metal carboxylates REACH Consortium (MCRC), covering 10 metal carboxylates in total. This literature screening effort included:
During the literature search and data gap analysis it became obvious that the overall database on substance-specific human health hazard data for the metal carboxylates is too scant to cover all REACH endpoints. Therefore, the remaining data gaps had to be covered by either experimental testing or read-across from similar substances.
Selected endpoints for the human health hazard assessment are addressed by read-across, using a combination of data on the organic acid counterion and the metal (or one of its readily soluble salts). This way forward is acceptable, since metal carboxylates dissociate to the organic anion and the metal cation upon dissolution in aqueous media. No indications of complexation or masking of the metal ion through the organic acid were apparent during the water solubility tests (please refer to the water solubility data in section of the IUCLID and chapter of the CSR). Once the individual constituents of the metal carboxylate become bioavailable (i.e. in the acidic environment in the gastric passage or after phagocytosis by pulmonary macrophages), the “overall” toxicity of the dissociated metal carboxylate can be described by the toxicity of the “individual” constituents. Since synergistic effects are not expected for this group of metal carboxylates, the human health hazard assessment consists of an individual assessment of the metal cation and the organic anion.
The hazard information of the individual constituents was obtained from existing REACH registration dossiers via a license-to-use obtained by the lead registrant. These registration dossiers were submitted to ECHA in 2010 as full registration dossiers, and are thus considered to contain relevant and reliable information for all human health endpoints. All lead-registrant dossiers were checked for completeness and accepted by ECHA, i.e. a registration number was assigned.
Zinc neodecanoate is the zinc metal salt of neodecanoic acid, which readily dissociates to the corresponding divalent zinc cation and neodecanoic acid anions. The zinc cation and the neodecanoic acid anion are considered to represent the overall toxicity of the zinc neodecanoate in a manner proportionate to the free acid and the metal (represented by one of its readily soluble salts). Based on the above information, unrestricted read-across is considered feasible and justified.
Introduction to the neoacids hazard assessment
The carboxylic acids “neodecanoic acid” and “fatty acid C9 to C13 neo” are considered similar in their toxicological profile and are therefore grouped together. Both neoacids originate from the same production process in which a branched olefin is reacted with carbon monoxide and water at elevated temperature and pressure in th1e presence of an acid as catalytic component. The dossiers for neodecanoic acid and fatty acid C9 to C13 neo contain human health hazard information on both substances indicating that the toxicological profile is similar. This approach was also used and accepted in the US EPA HPV programme, even for a wider range of neo-acid substances (US EPA, April 2009: http://www.epa.gov/chemrtk/pubs/summaries/neoc528/c13335tc.htm).
Based on the above information “neodecanoic acid” and “fatty acid C9 to C13 neo” will be assessed for their hazardous properties, using the same dataset for both substances.
Although the term „constituent“ within the REACH context is defined as substance (also being part of a mixture), the term constituent within this hazard assessment is meant to describe either part of the metal carboxylate salt, i.e. anion or cation.
Repeated dose toxicity
No repeated dose toxicity study with zinc neodecanoate is available, thus the repeated dose toxicity will be addressed with existing data on the dissociation products zinc and neodecanoic acid as detailed in the table below.
Table: Summary of repeated dose toxicity data of the zinc neodecanoate and the individual constituents.
| (slightly soluble) zinc substances | Neodecanoic acid | Zinc neodecanoate |
Repeated dose | NOAEL(human data)= 0.83 mg Zn/kg bw/day* | NOAEL(rat;28d)= 300 mg/kg bw/day (read-across from fatty acid C9 -13 neo, CAS# 68938-07-8) | no data |
Repeated dose | NOAEC(guinea pig;5d)=2.7 mg ZnO/m³ | no data | no data |
Repeated dose | no data | NOAEL(rabbit; 10d)= 2,280 mg/kg bw/day | no data |
* Identified as most sensitive endpoint in the registration dossier for zinc, thus has been used for the DNEL derivation of this substance.
Zinc
From studies in which humans were supplemented with zinc (as zinc gluconate)it was concludedthat women are more sensitive to the effects of high zinc intake and that a dose of 50 mg Zn/day is the human NOAEL. This corresponds to a daily exposure of 0.83 mg Zn/kg bw. At the LOAEL of 150 mg Zn/day, clinical signs and indications for disturbance of copper homeostasis have been observed. Studies conducted on animals are not discussed here, since information on human experience are considered of higher relevance for risk assessment purposes and should take precedence over animal studies.For further information on the toxicity of zinc, please refer to the relevant sections in the IUCLID and CSR.
Neodecanoic acid
Five male and five female rats were exposed to 0; 10; 55; or 300 mg/kg bw/day fatty acids, C9-C13 neo by oral gavage for 28 consecutive days. There were no mortalities. Increased salivation was observed after dosing in rats receiving 300 mg/kg. No treatment related changes were observed in body weight, food consumption, haematology, or clinical chemistry. In males receiving 300 mg/kg, kidney weight increased and necropsy revealed an abnormal appearance of the kidney. A dose-related hyaline droplet was noted in males at all treatment levels. The findings in the kidney of the treated males are species and sex specific and not considered relevant to humans. The NOAEL in this study was 300 mg/kg
In a repeated-dose dermal study, neodecanoic acid was applied repeatedly (once daily for 10 applications with a rest period on days 5 and 6) to the skin of rabbits at doses of 0.5 or 2.5 ml/kg (400 or 2280 mg/kg bw/day). All animals survived the exposure. Wheezing was noted in one animal at the 0.5 ml dose level. Animals at the lower dose level generally showed an overall body weight gain while those at the high level showed terminal weight losses. The low level animals generally showed slight erythema and moderate atonia and desquamation following the first or fourth application and during the remainder of the study. At the high level, moderate erythema and moderate or marked atonia and desquamation were present in all animals. In addition, slight oedema was present following the fifth application and slight fissures or cracks were observed in several animals following the last seven applications. The exposed skin also became hypersensitive to the touch. There were no indications of systemic toxicity attributed to exposure.
Members of the neoacids category have a low order of toxicity under conditions of repeat exposure by oral and dermal routes. In addition, they display a consistent degree of subchronic toxicity by either oral or dermal route of exposure.
Zinc neodecanoate
Since no repeated dose toxicity study is available specifically for zinc neodecanoate, information on the individual constituents zinc and neodecanoic acid will be used for the hazard assessment and when applicable for the risk characterisation of zinc neodecanoate. For the purpose of hazard assessment of zinc neodecanoate, the point of departure for the most sensitive endpoint of each constituent will be used for the DNEL derivation. In case of zinc in zinc neodecanoate, the NOAEL of 0.83 mg/kg bw/day in repeated dose toxicity (human data) will be used.
In relevant and reliable repeated dose toxicity studies for both constituents of zinc neodecanoate, there were no toxicological findings reported that would justify a classification for specific target organ toxicity with repeated exposure. Hence, no classification for zinc neodecanoate as STOT, RE is required.
Justification for selection of repeated dose toxicity via oral route - systemic effects endpoint:
Information from read-across substances:
human data for zinc: NOAEL=0.83mg/kg bw/day
animal data for neodecanoic acid: NOAEL(rat)=300mg/kg bw/day
Justification for classification or non-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.
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