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EC number: 209-170-2 | CAS number: 557-34-6
- 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
Acute toxicity: oral: Weight of evidence: The estimated LD50 for Zinc Acetate anhydrous was 663.83-2460 mg/kg bw in rats, and it was 239.95 mg/kg bw in mice. Mice were more sensitive than rats. Test method similar to OECD guideline 423.
Acute toxicity: inhalation: Weight of evidence: The estimated LC50 for Zinc Acetate was between 6.49 and 58.04 mg/L. Read-across approach from experimental data on analogues Calcium Acetate and Zinc Stearate.
Acute toxicity: other routes: Supporting information: The LD50 for adult mice was 42 mg/kg bw, and for juvenile mice was 97.8-99.6 mg/kg bw. The LD50 of zinc acetate anhydrous was 90.29 (56.02 -229.91) mg/kg bw in male mice, and 135.44 (74.41 -244.13) mg/kg bw in male rats. Mice were more sensitive than rats.
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: A scientifically defensible approach was used to conduct the study performed similar to OECD 423 guideline. No data on GLP.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 423 (Acute Oral toxicity - Acute Toxic Class Method)
- Deviations:
- not specified
- Remarks:
- (No data on control animals)
- GLP compliance:
- not specified
- Test type:
- acute toxic class method
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: The animals were supplied by Panlab (Barcelona, Spain).
- Weight at study initiation: 230-280 g
- Diet (e.g. ad libitum): The animals had free access to a standard pellet diet (Panlab, Barcelona, Spain).
- Water (e.g. ad libitum): Ad libitum.
- Acclimation period: Rats were allowed to acclimatize for a period of 7 days after shipping before experimental use. - Route of administration:
- oral: gavage
- Vehicle:
- physiological saline
- Details on oral exposure:
- Solutions of zinc were prepared and administered in 0 .9% saline.
Solution concentrations were adjusted so that a 300-g rat received 1 mL.
All solutions were given at pH between 6.0 and 7.0. Sodium bicarbonate was used to adjust the pH when necessary. - Doses:
- No data.
- No. of animals per sex per dose:
- Ten male animals in each group were used.
- Control animals:
- not specified
- Details on study design:
- - Duration of observation period following administration: 14 days
- Statistics:
- The LD50 values were then calculated according to the Litchfield and Wilcoxon method.
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 663.83 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- 488.26 - 902.94
- Remarks on result:
- other: (Estimated results for Zinc Acetate anhydrous)
- Mortality:
- The majority of deaths were observed within the first 24 hr. No deaths occurred after 3 days.
- Clinical signs:
- other: The physical and clinical signs appeared within the first 48 hr. These signs included miosis, conjunctivitis, decreased food and water consumption and hemorrhages and hematomas in the tall. These changes decreased with time which would suggest a quick eli
- Interpretation of results:
- Toxicity Category IV
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The LD50 of zinc acetate anhydrous was 663.83 (488.26-902.94) mg/kg bw in male rats.
- Executive summary:
Zinc acetate dihydrate was administered po by gavage to male rats. Ten animals in each group were used. The LD50 values were then calculated according to the Litchfield and Wilcoxon method. Animals were observed for 14 days.
The LD50 of zinc acetate anhydrous was 663.83 (488.26-902.94) mg/kg bw in male rats.
The majority of deaths occurred during the first 48 hr. The clinical and physical signs appearing after intoxication included miosis, conjunctivitis, decreased food and water consumption and hemorrhages and hematomas in the tall. These changes decreased with time which would suggest a quick elimination of zinc.
Reference
The LD50 of zinc acetate anhydrous was 663.83 (488.26-902.94) mg/kg bw in male rats.
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 663.83 mg/kg bw
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The analogue Calcium Acetate which shares the same functional group with Zinc Acetate, also has comparable values for the relevant molecular properties for the acute inhalation toxicity endpoint.
- Reason / purpose for cross-reference:
- reference to other study
- Principles of method if other than guideline:
- Read-across approach from Letter of Access experimental data (study with a test method similar to OECD 403) on the analogue Calcium Acetate.
- GLP compliance:
- no
- Test type:
- other: read-across from an standard acute method with an analogue
- Sex:
- female
- Dose descriptor:
- LC50
- Effect level:
- > 6.49 mg/L air
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Other findings:
- Based on the experimental results obtained with the analogue Calcium Acetate (LC 50 for female rats > 5.6 mg/L air) and the molecular weights, the read-across approach is applied and the LC50 for substance Zinc Acetate is calculated to be higher than 6.49 mg/L air under test conditions.
The analogue Calcium Acetate, which shares the same functional group with Zinc Acetate, also has comparable values for the relevant molecular properties. These properties are:
- a low log Pow value which is - 1.38 for Calcium Acetate and -1.28 for Zinc Acetate,
- a similar water solubility which is 1.0 g/mL at 25 ºC for Calcium Acetate and 434.78 g/L for Zinc Acetate at 25 ºC, and
- molecular weights which are 158.166 for Calcium Acetate and 183.497 for Zinc Acetate. - Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The LC50 for substance Zinc Acetate is calculated to be higher than 6.49 mg/L air under test conditions.
- Executive summary:
Based on the experimental results (reported under the endpoint record 07.02.02_01 CaAc) obtained with the analogue Calcium Acetate (LC 50 for female rats > 5.6 mg/L air) and the molecular weights, the read-across approach is applied and the LC50 for substance Zinc Acetate is calculated to be higher than 6.49 mg/L air under test conditions.
Reference
The LC50 for substance Zinc Acetate is calculated to be higher than 6.49 mg/L air under test conditions.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LC50
- Value:
- 6 490 mg/m³ air
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
ACUTE TOXICITY: ORAL:
Weight of evidence: Experimental results with Zinc Acetate dihydrate. Test method similar to OECD guideline 423.
The Acute Oral Toxicity test of Zinc acetate dihydrate was performed in Carworth-Wistar male rats. Single oral dose toxicity is estimated by the gastric intubation of groups of five non-fasted rats (concentration of solution intubated: 0.200 g test substance /mL water). The estimated LD50 for Zinc Acetate was 2.06 (1.34 -3.16) g/kg bw (2.46 g/kg bw for Zinc acetate dihydrate) in male rats.
Zinc acetate dihydrate was administered po by gavage to male mice and rats. Ten animals of each kind in each group were used. The LD50 values were then calculated according to the Litchfield and Wilcoxon method. Animals were observed for 14 days.
The LD50 of zinc acetate anhydrous was 239.95 (118.72 -486.58) mg/kg bw in male mice, and it was 663.83 (488.26-902.94) mg/kg bw in male rats. Mice were more sensitive than rats.
The majority of deaths occurred during the first 48 hr. The clinical and physical signs appearing after intoxication included miosis, conjunctivitis, decreased food and water consumption and hemorrhages and hematomas in the tall. These changes decreased with time which would suggest a quick elimination of zinc.
ACUTE TOXICITY: INHALATION:
Weight of evidence: Read-across approach from experimental results obtained with Calcium Acetate and Zinc Stearate.
Calcium acetate LC50value for 4 hours exposition at rat (male and female) is higher than 5.6 mg/L.
Based on these experimental results and the molecular weights, the read-across approach is applied and the LC50 for substance Zinc Acetate is calculated to be higher than 6.49 mg/L air under test conditions.
In a study with albino rats, Zinc stearate was determined to be nontoxic by inhalation. The (1 h) LC50 was > 200 mg/L.
The read-across approach is applied and the LC50 for substance Zinc Acetate is calculated to be higher than 58.04 mg/L air under test conditions.
ACUTE TOXICITY: OTHER ROUTES:
Supporting information: Experimental data on Zinc Acetate and Zinc Acetate dihydrate.
The sex and age related responses to Zinc Acetate were investigated in mice. Male and female juvenile and adult ICR-mice were administered single intraperitoneal injections of test substance. The median lethal dose (LD50) was calculated 1, 3, 5, 7, and 14 days following administration. Nearly all deaths occurred by day seven, with few deaths occurring between 7 and 14 days. The LD50 for juveniles was two and one half times higher than for adults. The mortality ratios on days one and three were higher for adult females than adult males, but by day seven, the LD50 values for males and females were not significantly different in either adults or juveniles.
The LD50 for adult mice was 42 mg/kg bw, and for juvenile mice was 97.8-99.6 mg/kg bw.
Zinc acetate dihydrate was administered ip to male mice and rats. Ten animals of each kind in each group were used. The LD50 values were then calculated according to the Litchfield and Wilcoxon method. Animals were observed for 14 days.
The LD50 of zinc acetate anhydrous was 90.29 (56.02 -229.91) mg/kg bw in male mice, and 135.44 (74.41 -244.13) mg/kg bw in male rats. Mice were more sensitive than rats.
The majority of deaths occurred during the first 48 hr. The clinical and physical signs appearing after intoxication included miosis, conjunctivitis, decreased food and water consumption and hemorrhages and hematomas in the tall. These changes decreased with time which would suggest a quick elimination of zinc.
Justification for classification or non-classification
Based on the available data, the substance is classified as acute oral toxicity category 4 according to CLP Regulation (EC) no. 1272/2008.
LD50>2000mg/kg/bw and <300mg/kg/bw: acute oral toxicity category 4.Inhalation: LC50>5 mg/L: non-classification
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