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EC number: 212-769-1 | CAS number: 868-14-4
- 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
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well documented report equivalent or similar to OECD guidelines
Data source
Reference
- Reference Type:
- publication
- Title:
- Renal and bone uptake of tartaric acid in rats: comparison of L(+) and DL-forms
- Author:
- Down WH, Sacharin RM, Chasseaud LF, Kirkpatrick D & Franklin ER
- Year:
- 1 977
- Bibliographic source:
- Toxicology. 8: 333-346
Materials and methods
- Objective of study:
- distribution
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Principles of method if other than guideline:
- The toxicokinetics of monosodium L(+)-tartrate was studied on CFY rats in this study, and DL-tartrate was also studied as a comparison.
1. DL-[1,4-14C] tartaric acid was obtained and then was resolved into L(+)-[14C] isomer.
2. Either form of monosodium [14C] tartrate was dissolved in water and administered to animals for 7days by oral intubation.
3. One animal in each group was sacrificed immediately before the seventh day's dose, and the remainders in each group were sacrificed at intervals during the following 12 days
4. The radioactivity of samples of blood, bone and kidney and the whole-body autoradiography was measured.
5. Samples of kidney were fixed and stained with haematoxylin and eosin for histological examination. - GLP compliance:
- no
Test material
- Reference substance name:
- Sodium hydrogen tartrate
- EC Number:
- 208-400-9
- EC Name:
- Sodium hydrogen tartrate
- Cas Number:
- 526-94-3
- Molecular formula:
- C4H6O6.Na
- IUPAC Name:
- sodium hydrogen tartrate
- Details on test material:
- - Name of test material (as cited in study report): Monosodium L(+)-tartrate
- Molecular formula (if other than submission substance): C4H5NaO6
- Molecular weight (if other than submission substance): 172.07
- Radiochemical purity (if radiolabelling): 99%
- Locations of the label (if radiolabelling): 1,4
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 14C labeled
Test animals
- Species:
- rat
- Strain:
- other: CFY ratsm, a strain of SD origin
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Anglia Laboratory Animals, Huntingdon, Great Britain
- Weight at study initiation: 160-180 g in the first experiment, 180-200g in the further experiment.
- Individual metabolism cages: No
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- not specified
- Duration and frequency of treatment / exposure:
- once per day for 7 days
Doses / concentrations
- Remarks:
- Doses / Concentrations:
2.73 g/kg/day in the first experiment, 2.57 g/kg/day in the further experiment. All the values here are the actual ingested
- No. of animals per sex per dose / concentration:
- in the first experiment, 10 M in each dose group.
in the further experiment, 8 M in each dose group, and 1 rat receiving DL-tartrate died on the fifth day of dosing - Control animals:
- no
- Details on study design:
- - Dose selection rationale: the dose level corresponded to an intermediate dietary level used in long-term toxicity studies of monnosodium L(+)-tartaric acid.
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled : blood, plasma, kidney, bone
- Time and frequency of sampling:one animal in each group was sacrificed immediately before the seventh day's dose, and the remainder in each group were sacrificed at intervals during the following 12 days. in the further experiment, all rats sacrificed at 6 h after the seventh day's dose. - Statistics:
- not mentioned
Results and discussion
Main ADME resultsopen allclose all
- Type:
- distribution
- Results:
- the initial decline of L(+)-tartrate plasma concentration of radioactivity was rapid
- Type:
- distribution
- Results:
- L(+)-tartrate was not retained in the kidneys and bone after dosing
Toxicokinetic / pharmacokinetic studies
- Details on distribution in tissues:
- At 3 h after the last dose of L(+)-tartrate, the radioactivity was mainly present in the gastrointestinal tract, liver, kidneys and bone. Radioactivity in the kidney was mainly evenly distributed in the cortex. Aggregates of radioactive particles in the large intestine indicate unabsorbed tartrate. At 24 h after the last dose of L(+)-tartrate, only localization of radioactivity in bone was detected and persisted for at least 192 h after the last dose.
At 3 h after the last dose of DL-tartrate, the radioactivity was mainly present in the gastrointestinal tract, liver, kidneys and bone. Aggregates of radioactive particles were present in kidney cortex and medulla. the aggregates in kidney could be detected for at least 192 h after the last dose. Radioactivity was associated with bone throughout the time-course studied.
Concentrations of radioactivity associated with bone after the last dose of L(+)-tartrate were maximal at 1 h (787 μg/g) and declined slowly. For DL-tartrate, it was maximal at 12 h (1203 μg/g) and declined rapidly. During 96 h after the last dose, concentrations of radioactivity in the bones of rats dosed with DL-tartrate was twice those in the bones of rats dosed with L(+)-tartrate.
The retention of radioactivity in the kidneys of rats dosed with L(+)-tartrate was much less than in those of rats dosed with DL-tartrate. Furthermore, radioactivity in the kidney of rats dose L(+)-tartrate was mainly water soluble whereas that of rats dose with DL-tartrate was probably present as the more insoluble calcium salt.
Toxicokinetic parametersopen allclose all
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 1st: 3 h in plasma after the last dose
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 2nd: 53 h in plasma after the last dose
Metabolite characterisation studies
- Metabolites identified:
- no
Any other information on results incl. tables
The retention of radioactivity in the kidneys of rats dosed with L(+)-tartrate was much less than in those of rats dosed with DL-tartrate. And furthermore, L(+)-tartrate in kidneys was mainly in soluble manner, whereas DL-tartrate was present as more insoluble calcium salt.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): bioaccumulation potential cannot be judged based on study results
At 3 h after the last dose of L(+)-tartrate, the radioactivity was mainly present in the gastrointestinal tract, liver, kidneys and bone. L(+)-[14C] tartrate was not retained in the kidneys (1287±118 ppm at 6 h, n = 8) when administered to rats for 7 days at a dose level of 2.73 g/kg/day, and the initial decline of plasma concentrations of radioactivity was more rapid (t0.5 approx.3 h). For this reason, monosodium L (+)-tartrate was non-toxic at 2.73 g/kg/ day whereas monosodium DL-tartrate was toxic at this dosage. - Executive summary:
This study reported were carried out to compare the distribution of radioactivity in the bones and kidneys of rats administered relatively high repeated oral doses of monosodium L(+)-[14C]tartrate or DL-[14C]tartrate. At 3 h after the last dose of L(+)-tartrate, the radioactivity was mainly present in the gastrointestinal tract, liver, kidneys and bone. L(+)-[14C] tartrate was not retained in the kidneys (1287±118 ppm at 6 h, n = 8) when administered to rats for 7 days at a dose level of 2.73 g/kg/day, and the initial decline of plasma concentrations of radioactivity was more rapid (t0.5approx.3 h). For this reason, monosodium L (+)-tartrate was non-toxic at 2.73 g/kg/ day whereas monosodium DL-tartrate was toxic at this dosage.
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