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EC number: 203-740-4 | CAS number: 110-15-6
- 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study published in a peer-reviewed journal, Read across
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 990
- Report date:
- 1990
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Deviations:
- not specified
- Remarks:
- . Study details are missing, but obviously performed in accordance with guideline.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- Monosodium succinate
- IUPAC Name:
- Monosodium succinate
- Reference substance name:
- Sodium hydrogen succinate
- EC Number:
- 220-871-2
- EC Name:
- Sodium hydrogen succinate
- Cas Number:
- 2922-54-5
- IUPAC Name:
- sodium hydrogen succinate
- Details on test material:
- - Name of test material (as cited in study report): Monosodium succinate
- Analytical purity: 100.2 % (99.7-100.7 %)
- Producer: Mitsubishi Kasei Food Co. (Tokyo, Japan)
- Provider: Japan Food Additives Association (Tokyo, Japan)
- Stability under test conditions: The stability of a 2 % aqueous solution of the test substance was ascertained for at least one week at room temperature.
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Japan, Inc. (Kanagawa, Japan)
- Status: SPF
- Age at study initiation: 6 weeks
- Weight at study initiation: between 100 and 200 g, not reported (only growth curves available)
- Fasting period before study: none reported
- Diet: basal diet (CRF-1), Oriental Yeast Inc., Tokyo, Japan), ad lib.
- Water: distilled water (test substance dissolved in distilled water as drinking water)
- Acclimation period: one week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): not reported
- Humidity (%): not reported
- Air changes (per hr): not reported
- Photoperiod (hrs dark / hrs light): not reported
Administration / exposure
- Route of administration:
- oral: drinking water
- Vehicle:
- water
- Remarks:
- distilled water
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
- Test substance dissolved in distilled water (vehicle), used as drinking water
VEHICLE
- Concentration in vehicle: 0, 0.3, 0.6, 1.25, 2.5, 5 and 10 %
- Justification for choice of vehicle: not reported - Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 13 weeks
- Frequency of treatment:
- daily / continuously (access to test substance solutions in drinking water ad lib.)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 0.3, 0.6, 1.25, 2.5, 5, 10 %
Basis:
nominal in water
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Dose selection rationale: to find appropriate doses for a subsequent long-term toxicity/carcinogenicity study
- Positive control:
- Not appropriate
Examinations
- Observations and examinations performed and frequency:
- ANIMAL OBSERVATIONS: Yes
- Cage side/detailed clinical: not stated
- Time schedule: once daily
BODY WEIGHT: Yes
- Time schedule for examinations: every other week
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes
- Time schedule for examinations: not reported
OPHTHALMOSCOPIC EXAMINATION: No data
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at necropsy
- Animals fasted: No data
- How many animals: survivors
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: at necropsy
- Animals fasted: No data
- How many animals: survivors
URINALYSIS: No data
NEUROBEHAVIOURAL EXAMINATION: No data
OTHER: - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes - Statistics:
- None reported
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- 100 % mortality at 10 % test substance
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- 100 % mortality at 10 % test substance
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- suppression of body-weight gain at >= 2.5 % test substance
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- effects observed, treatment-related
- Description (incidence and severity):
- small at 10 %, larger than in other groups at 5 %
- Ophthalmological findings:
- not specified
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- emaciation in rats that died during the study
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 12 500 mg/L drinking water
- Based on:
- dissolved
- Sex:
- male/female
- Basis for effect level:
- other: clinical signs; mortality; body weight; haematology; clinical chemistry; gross pathology; histopathology
- Dose descriptor:
- LOAEL
- Effect level:
- 25 000 mg/L drinking water
- Based on:
- dissolved
- Sex:
- male/female
- Basis for effect level:
- other: body weight gain (suppressed)
- Dose descriptor:
- NOAEL
- Effect level:
- 860 other: mg succinic acid / kg bw /day
- Based on:
- other: This NOEL (mg/kg bw/d) for succinic acid was calculated from the NOEL (mg/mL/d) for Na-succinate, the average body weight, the average water consumption, both taken from Figures 1 and 2 of the publication, and also from the different molecular masses.
- Sex:
- male
- Dose descriptor:
- NOAEL
- Effect level:
- 990 other: mg succinic acid / kg bw /day
- Based on:
- other: This NOEL (mg/kg bw/d) for succinic acid was calculated from the NOEL (mg/mL/d) for Na-succinate, the average body weight, the average water consumption, both taken from Figures 1 and 2 of the publication, and also from the different molecular masses.
- Sex:
- female
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- On the basis of body-weight depression, the maximum tolerated dose of monosodium succinate was determined to be about 2-2.5 % when it was given in the drinking water. The NOAEL is 12.5 mg/mL drinking water/day.
The derived NOAEL for succinic acid, assuming that monosodium succinate and succinic acid dissociate completely in low concentrations, was calculated to 860 mg/kg/d for male rats and 990 mg/kg/d for female rats. - Executive summary:
Monosodium succinate was dissolved in distilled water which was given as drinking water to groups of 10 male and 10 female rats each for a period of 13 weeks. Substance concentrations in water were 0, 0.3, 0.6, 1.25, 2.5, 5 or 10 %. The rats were observed daily for clinical signs. Body weights were determined weekly. At the end of the study period, haematological and biochemical examinations were carried out and the survivors were killed for gross and microscopic examination.
Severe suppression of body weights occurred in rats in the highest dose group, and all of these rats died during the first 4 weeks of the experiment. All of the other animals survived until the end of the study. Suppression of body weight was found in groups given >= 2.5 % of test substance in the drinking water, and this suppression was >10 % in the groups given 5 or 10 % in comparison with the controls. The volume of drinking water consumed was very small in the highest dose group. No specific and dose-related changes were observed in any parameters in the haematological and biochemical investigations.
Rats that died during the study were severely emaciated. However, in the histopathological examination no toxic lesions caused by monosodium succinate was found in any organs of these rats, although atrophy of the organs was observed. In the other groups also, there were no specific lesions.
On the basis of body-weight depression, the maximum tolerated dose of monosodium succinate was determined to be about 2 -2.5 % when it was given in the drinking water.
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