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EC number: 240-369-7 | CAS number: 16260-27-8
- 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
No acute toxicity studies with zinc ditetradecanoate are available, thus the acute toxicity will be addressed with existing data on the dissociation products zinc and tetradecanoic acid. Signs of acute oral or acute dermal toxicity are not expected for zinc ditetradecanoate, since for the moiety zinc, has not shown signs of acute oral toxicity (LD50 > 2000mg/kg)
and acute dermal toxicity is considered to be low in view of the poor absorption by this route. The moiety tetradecanoate has not shown signs of acute oral or acute dermal toxicity in experimental testing (LD50 > 2000mg/kg).
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Used in EU risk assessment for zinc oxide, limited study details provided
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- GLP compliance:
- not specified
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- 5 per sex
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on oral exposure:
- single dose by oral gavage in water and observed for 14 days
- Doses:
- single dose of 5 gZnO/kg bw
- No. of animals per sex per dose:
- 5 per sex
- Control animals:
- not specified
- Details on study design:
- no further information
- Statistics:
- no data
- Preliminary study:
- no further information
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 5 000 mg/kg bw
- Mortality:
- no mortality
- Clinical signs:
- no adverse signs of toxicity
- Body weight:
- no adverse signs of toxicity
- Gross pathology:
- no adverse signs of toxicity
- Interpretation of results:
- practically nontoxic
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- LD50 > 5000 mg ZnO/kg bw was determined.
- Executive summary:
In an acute toxicity test Wistar rats (5/sex) were given a single dose of 5 g ZnO/kg bw (in water) by gavage and observed for 14 days. No mortality and signs of toxicity were observed. The LD50for rats is therefore >5 g ZnO/kg bw.
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study is well documented and meets general acceptable scientific principle.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 423 (Acute Oral toxicity - Acute Toxic Class Method)
- Deviations:
- no
- GLP compliance:
- not specified
- Remarks:
- the publication does not specify GLP compliance
- Test type:
- other: limit test
- Limit test:
- yes
- Species:
- mouse
- Strain:
- not specified
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- No data
- Route of administration:
- oral: gavage
- Vehicle:
- DMSO
- Details on oral exposure:
- - Rationale for the selection of the starting dose: Based on the result of another study (Yamaki & Yoshino 2009).
- Doses:
- 5,000 mg/kg bw for both ZnO nanoparticle and microparticle
- No. of animals per sex per dose:
- 5/sex/dose
- Control animals:
- yes
- Details on study design:
- Thirty mice were divided into three groups (five males and five females per group). Mice were fed with vehicle (control group), 5,000 mg/kg bw ZnO-nanoparticle suspension or 5,000 mg/kg bw ZnO-microparticles suspension. Dosed mice were conditioned for 14 d. The mortality and clinical behaviour were observed daily. Body weights were recorded twice weekly. At the end of the study (on Day 14), the mice were anaesthetised with isoflurane and blood (for serum biochemistry analysis) was collected from the orbital sinus, followed by gross necropsy. Tissue samples (for histopathologic examination) were taken and fixed in 10% neutral buffered formalin
- Statistics:
- All data were expressed as the mean ± SD from at least three independent experiments (N ‡ 3). The significance of the difference between the control and each experimental test condition was analysed by Student’s t-test. Statistically significant differences among groups were determined using one-way analysis of variance (ANOVA). A value of p < 0.05 was taken as statistically significant.
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 5 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- Not observed
- Clinical signs:
- Not observed
- Body weight:
- In comparison with vehicle control group, ZnO microparticles treated group showed a body weight reduction in both males (Days 5 and 10) and females (Days 5, 10, and 14); the body weight changes were unobvious in ZnO nanoparticle treated groups.
- Gross pathology:
- Decreased wet weights of the spleen, kidney, and liver were observed in ZnO microparticles treated females but not in ZnO nanoparticle treated males. However, no obvious gross pathological signs were found in the study.
- Other findings:
- All serum biochemistry measures were without any significant alternation except for marginal variations in certain parameters.
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- Based on the study details, the LD50 value of both the ZnO nanoparticles and ZnO microparticles can be established at >5,000 mg/kg bw in mice.
- Executive summary:
The study was conducted to examine the acute toxicity of both ZnO nanoparticles and ZnO microparticles in mice.
Thirty mice were divided into three groups (five males and five females per group). Mice were fed with vehicle (control group), 5,000 mg/kg bw ZnO-nanoparticle suspension or 5,000 mg/kg bw ZnO-microparticles suspension. Dosed mice were conditioned for 14 d.
All the mice survived throughout the testing period without exhibiting any abnormalities related to the test substances. In comparison with the vehicle control group, ZnO-microparticles treated group showed a body weight reduction in both males (Days 5 and 10) and females (Days 5, 10, and 14); the body weight changes were not obvious in ZnO-nanoparticle treated groups. All serum biochemistry measures were without any significant alterations except for marginal variations in certain parameters.
Based on the study details, the LD50 value of both the ZnO nanoparticles and ZnO microparticles can be established at >5,000 mg/kg bw in mice.
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: According to the OECD guideline, but mice used
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- GLP compliance:
- not specified
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- mouse
- Strain:
- other: CD-ICR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Age: 8 weeks
Weight: 20-22 g - Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Doses:
- 1000, 2000, 3000, 4000, 5000 mg/kg
- No. of animals per sex per dose:
- 5
- Control animals:
- yes
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing:before begin of study, after 2 and 14 days
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight, histopathology, blood analysis - Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 5 000 mg/kg bw
- Remarks on result:
- other: 20 nm ZnO
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 - < 5 000 mg/kg bw
- Remarks on result:
- other: 120 nm ZnO
- Mortality:
- One female death occurred in the nano-scale 2000 mg group and one male death in the nano-scale 5000 mg group.
As for 120-nm ZnO treated mice, one and three female mice died in the sub-micro 2000 mg and 5000 mg group. - Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- According to the authors nano-scale as well as submicro-scale ZnO are both not classified according to the GHS with a LD50 of greater than 5 g/kg and 2g/mg < LD50 < 5 g/kg, respectively.
- Executive summary:
In this work, the acute oral toxicity of 20- and 120-nm ZnO powder at doses of 1-, 2-, 3-, 4-, 5-g/kg body weight was evaluated referred to the OECD guidelines for testing of chemicals. As the results, both 20- and 120-nm ZnO belong to non-toxic chemicals according to the Globally Harmonized Classification System (GHS) for the classification of chemicals.
Referenceopen allclose all
none
Combined with the results of zinc accumulation, pathological examination and the biological indicators assays, according to the authors the target organs for 20- and 120-nm ZnO acute oral administration are demonstrated as liver, heart, spleen, pancreas and bone.
The biochemical and pathological investigation shows that the toxic effects between the 20-nm and 120-nm ZnO particles are a little different. For example, the blood viscosity could be induced by low and median dose of 20-nm ZnO but high dose of fine ZnO after oral administration. The edema and degeneration of hepatocytes, and inflammation of pancreas could be observed in most of the 20-nm ZnO treated mice. The 120-nm ZnO treated mice were found having dose-effect pathological damage in gastric, liver, heart and spleen, however, the 20-nm ZnO treated mice presented lessened liver, spleen and pancreas damage with the increase of treated dose.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Endpoint:
- acute toxicity: dermal
- Data waiving:
- other justification
- Justification for data waiving:
- other:
Referenceopen allclose all
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
Additional information
Zinc ditetradecanoate
No acute toxicity studies with zinc ditetradecanoate are available, thus the acute toxicity will be addressed with existing data on the individual moieties zinc and tetradecanoate.
Signs of acute oral or acute dermal toxicity are not expected for zinc ditetradecanoate, since for the moiety zinc, has not shown signs of acute oral toxicity (LD50 > 2000mg/kg) and acute dermal toxicity is considered to be low in view of the poor absorption by this route. The moiety tetradecanoate has not shown signs of acute oral or acute dermal toxicity in experimental testing (LD50 > 2000mg/kg). Under the assumption that the moieties of zinc ditetradecanoate show their toxicological profile individually upon dissolution, the acute oral and dermal (systemic) toxicity of zinc ditetradecanoate can be calculated using the equation given in regulation (EC) 1272/2008, Annex I, Section 3.1.3.6.1.
A study for acute toxicity via inhalation was not conducted with zinc ditetradecanote, since inhalation of the substance zinc ditetradecanoate is considered negligible based on the outcome of the dustiness testing according to the modified Heubach method, as reported under section particle size distribution (granulometry). Further, in a supporting study with the analogous substance zinc dilaurate, no toxicity was seen in an acute inhalation toxicity test up to the limit concentration of 5mg/L. Thus, acute toxic effects are not likely to occur during manufacture and handling of that substance. For further information on the toxicity of the individual moieties, please refer to the relevant sections in the IUCLID and CSR.
The calculated oral and dermal LD50 for zinc ditetradecanoate is > 2000mg/kg, hence the substance is not to be classified according to regulation (EC) 1272/2008 for acute oral and dermal toxicity as well as for specific target organ toxicity, single exposure (STOT SE).
Zinc
Acute oral toxicity
- With LD50values consistently exceeding 2,000 mg/kg bw, zinc oxide (LD50ranges between 5,000 and 15,000mg/kg bw), shows very low level of acute oral toxicity.
Acute dermal toxicity
- There are no available data on which to evaluate acute dermal toxicity for ZnO micromaterial. However, acute dermal toxicity can be considered to be low in view of the poor absorption by this route.
Tetradecanoate
Acute oral toxicity
According to the HERA document on fatty acid salts (2002) “the available data for fatty acids provide a clear picture of low acute toxicity for this class of chemicals. All oral LD50values were greater than 2,000 mg/kg, with little mortality being observed even at the highest doses tested in the studies (IUCLID, 2000c, 2000e, 2000f, 2000g; Clayton & Clayton, 1982; CIR, 1987)” (HERA, 2002).
“In a study conducted according to the FHSA, groups of five male albino rats were administered myristic acid at doses up to 10,000 mg/kg bw. There were no deaths. There were no clinical signs at 464, 1000, 2150 mg/kg bw. Transient slight diarrhea and excessive salivation was observed at 4640 mg/kg bw. The majority of animals in the 10,000 mg/kg group showed slight depression, mucoid diarrhea, unkempt fur stained with diarrhea, and serum and blood discharge from the nose and eyes the first three days of dosing. There were no findings at gross necropsy. The LD50was > 10,000 mg/kg bw” (OECD SIDS, 2014).
“International-BioResearch (1974, as referred to by CIR, 1987) determined the acute oral toxicity in groups of five male albino rats. Animals were administered by gavage lauric-, myristic-, palmitic- or stearic acid with increasing doses of up to 10,000 mg/kg bw and oleic acid up to 20,000 mg/kg bw. It was observed that for all these fatty acids the LD50value was above the maximum level tested” (EFSA ANS Panel, 2017).
Based on these results, the EFSA ANS Panel concluded that myristic acid has a low acute oral toxicity.
In conclusion, the conduct of any further toxicity studies with acute oral exposure in animals would not contribute any new information and is therefore not considered to be required.
Acute dermal toxicity
A registration dossier shall contain information on the human health hazard assessment (regulation 1907/2006, Art.10). However, it is considered that the information requirements for zinc ditetradecanoate (synonym: zinc dimyristate) as laid down in annex VII to IX can be fulfilled by adaptation of the standard testing regime according to Annex XI, points 1.2. and 1.3. as presented in the following:
According to Regulation (EC) No 1907/2006 Annex V substances obtained from natural sources and not modified such as vegetable fats and oils as well as fatty acids from C6 to C24 and their potassium, sodium, calcium and magnesium salts are excluded from the obligation to register.
The substance subjected to registration is a common saturated C14- fatty acid, which is present in bovine milk, breast milk as well as palm kernel oil, coconut oil and butterfat. Based on this, the following endpoint is covered by publicly available data on fatty acids with the same or similar structure.
“As with the acute oral data, the available acute dermal toxicity data for the fatty acids (and their salts) provide a clear picture of low acute toxicity for this group of chemicals. All dermal LD50values were greater than >2,000 mg/kg (BIBRA, 1996; IUCLID, 2000e; Clayton & Clayton, 1982; CIR, 1982, 1987)” (HERA, 2002).
“In a subchronic study, no adverse effects were produced from topical application of myristic acid (C14) to rabbit skin. One-half ml of a 30% preparation of myristic acid in ether and propylene glycol (solvents at a 1:1 ratio in concentration) was massaged into the depilated skin of the flanks of 5 rabbits daily for 30 days. The opposite flank of the rabbits was depilated and treated with solvent only. No significant macroscopic changes were observed. Microscopic lesions included thinning of collagen fibres in the superficial layer of the dermis after 10 days and a loose dermal infiltrate of lymphomononuclear cells and histocytes after 20 and 30 days (CIR, 1987)” (HERA, 2002).
No dermal toxicity was reported for similar substances such as sodium stearate. “In a dermal study in which concentrations of sodium stearate (C18) ranged between 10-25% in a 20% bath soap detergent form, the LD50was >3000 mg/kg (highest dose tested) (CIR, 1982). In a dermal study in guinea pigs, application of commercial grade oleic acid (3,000 mg/kg) produced no deaths and no signs of toxicity. The number of applications was not stated (CIR, 1987)” (HERA, 2002).
Justification for classification or non-classification
The calculated oral and dermal LD50 for zinc ditetradecanoate is > 2000mg/kg, hence the substance is not to be classified according to regulation (EC) 1272/2008 for acute oral and dermal toxicity as well as for specific target organ toxicity, single exposure (STOT SE).
Zinc ditetradecanoate is not classified for acute inhalative toxicity because of lacking data.
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.