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EC number: 208-914-3 | CAS number: 546-89-4
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics, other
- Type of information:
- other: Expert statement
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Expert statement
Data source
Reference
- Reference Type:
- other: Expert statement
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2017
Materials and methods
- Objective of study:
- toxicokinetics
Results and discussion
Applicant's summary and conclusion
- Conclusions:
- The substance completely dissociates in water forming lithium cation and the corresponding acetate anion. Lithium ions are distributed throughout the body and are mainly excreted (80 - 90 %) unchanged via the kidneys. The acetate ion is a metabolite that is normally occurring in different human synthesis mechanisms. Via the citric acid cycle, acetate is rapidly metabolised to carbon dioxide, which will be eliminated from the body, predominantly via the exhaled air and in smaller quantities also via urine and faeces. Due to the fast excretion of both ions, bioaccumulation is not to be assumed.
- Executive summary:
Dermal absorption
The stratum corneum provides its greatest barrier function against hydrophilic compounds, whereas the viable epidermis is most resistant to highly lipophilic compounds. Based on the hydrophilic character of lithium acetate and the barrier function of the stratum corneum against salts, dermal absorption is expected to be very poor. It is supported by an acute dermal toxicity study with lithium acetate dihydrate that revealed a LD50 value >2000 mg/kg bw without any local or systemic effects. The assumption that absorption is negligible is further confirmed by the negative results of an EPISKIN assay (OECD 439) with lithium acetate anhydrous and a Corrositex assay with lithium acetate dihydrate, respectively. Further, no sensitization was observed in a sensitization studies with the read-across substances lithium chloride and lithium carbonate. Additionally, acetic acid is an important industrial chemical that is also used in food industry as acidity regulator (E260). Further a harmonised classification and labelling is listed in Annex VI of Regulation (EU) No 1272/2008 that does not include skin sensitising properties. Based in the results of the read across substances it is concluded, that lithium acetate is not skin sensitizing.
Resorption after oral uptake:
Upon oral uptake, lithium acetate will reach the stomach in form of lithium ions and acetate ions. Lithium- and acetate ions will be readily and almost completely absorbed from the gastrointestinal tract due to their low molecular weight (< 500 g/mol). Additionally, the low log Pow of both ions favors them for absorption by passive diffusion and therefore they can cross lipophilic membranes. They are also small and water soluble enough to be carried through the epithelial barrier by the bulk passage of water. In a study with lithium acetate an LD0 of 1500 mg/kg bw was determined. Based on this result the substance in classified as cat. 4 H302.
Resorption after inhalation:
The vapour pressure of lithium acetate is negligible (Modified Gain method: 2.59E-006 Pa at 25 °C) and therefore exposure to vapour is toxicologically not relevant. If lithium ions reach the lung resorption after inhalation is assumed to be low due to the very low log Pow. Thus, upon inhalation, the bioavailability of lithium acetate is expected to be low.
Distribution, Metabolism and Excretion
Lithium:
Lithium does not bind to protein and as a small cation it is quickly distributed throughout the body water both intra- and extracellularly, replacing cations (as K+, Na+) in the body cells. Lithium ion effects in the cell level are presumed to be related to interferences with processes that involve these ions such as renal tubular transport and ion channels involved in neurotransmission. Lithium has a large volume of distribution of 0.6-0.9 L/kg (for a 70 kg human a 42 L of volume of distribution). Because of its large volume of distribution, lithium shifts into the intracellular compartment of cells. With long-term use, the intracellular concentration of lithium increases, which thereby results in increased total body lithium load. The intracellular concentration is not reflected by the plasma level, which measures only the extracellular fluid concentration. Organ distribution is not uniform: Lithium is rapidly taken up by the kidney (there is obviously a clear interaction between lithium and sodium excretion/retention altering the electrolyte balance in humans). Penetration is slower into the liver, bone and muscle. Its passage across the blood-brain barrier is slow and equilibration of the CSF lithium level reaches only approximately half the plasma concentration.
The primary route of excretion is through the kidneys. Lithium is filtered by the glumeruli and 80 % of the filtered lithium is reabsorbed in the tubules, probably by the same mechanism of sodium reabsorption. Lithium is excreted primarily in urine with less than1 % being eliminated with the feces.
The renal clearance of lithium is proportional to its plasma concentration. The excretion of lithium ions is considered to be fast. About 50 % of a single dose of lithium is excreted in 24 hours and about 90 % in 48 hours. However, trace amounts can still be found 1 to 2 weeks after the ingestion of a single lithium dose. A single oral dose of lithium ion is excreted almost unchanged through the kidneys. A low salt intake resulting in low tubular concentration of sodium will increase lithium reabsorption and might result in retention and intoxication. Renal lithium clearance is under ordinary circumstances, remarkably constant in the same individual but decreases with age and also when sodium intake is lowered.
Due to the fast excretion bioaccumulation is not to be assumed. Lithium is not metabolised to any appreciable extent in the human body. In conclusion, Lithium in human body is quickly distributed and unchanged excreted. Bioaccumulation can be excluded.
Acetate ion/Acetic acid:
The acetate ion (the anion of acetic acid) is a normally occurring metabolite in catabolism or in anabolic synthesis (e.g. in formation of glycogen, cholesterol synthesis, degradation of fatty acids, and acetylation of amines). The estimated plasma level of the acetate ion in the human body is about 50-60 µmol/L (3.0-3.6 mg/L) and 116 µmol/L (7 mg/L) in cerebrospinal fluid. Daily turnover of the acetate ion in humans is estimated to be about 7.5 µmol/kg/min (45 g/day; SCOL, 2012). Via the citric acid cycle, acetate is rapidly metabolised to carbon dioxide, which will be eliminated from the body, predominantly via the exhaled air and in smaller quantities also via urine and faeces. Acetic acid can also be used as a building block e.g. in the biosynthesis of fatty acids (Efsa, 2011)
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