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EC number: 208-901-2 | CAS number: 546-46-3
- 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
ZINC
(13 wk) NOAEL 234 mg ZnSO4.7H2O/kg bw rats (approximately 53.5 mg Zn2+/kg bw or 155 mg trizinc dicitrate/kg (bw)*) (Maita et al., 1981; rel 2)
(13 wk) NOAEL = 469 mg ZnSO4.7H2O/kg bw rats (approximately 104 mg Zn2+/kg bw or 302 mg trizinc dicitrate/kg (bw)*). (Maita et al., 1981, rel. 2).
CITRIC ACID
(5 d) NOAEL 4000 mg/kg, rats (Bachtold1976; rel 2)
(10 d) NOAEL (mortality) values of 1000 and 4000 mg/kg, mice and rats respectively (Bachtold 1978, rel. 2)
For DNEL derivation human data (listed under IUCLID chapter 7.10.3) are used with a 10 week NOAEL of approx. 50 mg Zn2 +/person/d based on a depressed copper uptake and an altered lipid profile in humans.
This section contains substantially new data.
Key value for chemical safety assessment
Additional information
Although most of the available test data for citric acid does not match current testing standards (due to short testing duration, or insufficient information, etc), it does indicate low acute toxicity following repeat dose exposure.For example, a reliable five day study in rats gave NAOEL value of 4000 mg/kg (Bachtold, 1976; rel 2); a 10 day study in mice and rats gave NOAEL (mortality) values of 1000 mg/kg and 4000 mg/kg respectively (Bachtold, 1978;rel 2).
The effect of trizinc dicitrate is not expected to differ significantly from the effects of the zinc ions and citric acid separately once absorbedtherefore the assessment of this substance will be based on both citric acid and zinc respectively. Since the toxicological effects of citric acid are negligible, the effects of trizinc dicitrate are derived from zinc.
Results from a 13 week reliable screening repeat dose/reproduction feeding study in rats with zinc sulphate reported aNOAEL of 234 mg ZnSO4.7H2O/kg bw (approximately 53.5 mg Zn2+/kg bw or 155 mg trizinc dicitrate/kg (bw)*), and in mice a NOAEL of 469 mg ZnSO4.7H2O/kg bw. (Which approximates to 104 mg Zn2+/kg bw or 302 mg trizinc dicitrate/kg (bw)*). (Maita et al, 1981).
Another study in rats with zinc monoglycerolate reported a NOAEL = 31.52 mg zinc monoglycerolate/kg bw. This correlates to a NOAEL ~ 13.26 mg Zn2+/kg bw or 38.45 mg trizinc dicitrate/kg (bw)*).(Edwards and Buckley, 1995, Zinc chloride RAR 2008).
For DNEL derivation human data (listed under IUCLID chapter 7.10.3) are used with a 10 week NOAEL of approx. 50 mg Zn2 +/person/d based on a depressed copper uptake and an altered lipid profile in humans, which is in line with existing evaluation like EFSA, EU and MAK commission.
This information is considered as substantial new information compared to the study results from animal studies.
Other zinc RAR have been reviewed and the data contained is identical to that which has been detailed here.
*Conversion factor = (MW trizinc dicitrate / (MW Zinc x 3) = 547 / (65x3) = 2.9)
Justification for classification or non-classification
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