Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 208-863-7 | CAS number: 544-17-2
- 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:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- GLP guideline study. Justification of test substance: potassium diformate decomposes into one molecule of each formate and formic acid. Thus, potassium diformate gives two formate anions on a molar basis. Local effects of the formic acid formed can be neglected because these are not expected with neutral salts (sodium, potassium, ammonium, calcium formate). Read across can therefore be limited to systemic effects.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Deviations:
- yes
- Remarks:
- ; absorption of TS and reversibility of effects over a 4 week treatment-free period.
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Potassium formate(1:2)
- EC Number:
- 243-934-6
- EC Name:
- Potassium formate(1:2)
- Cas Number:
- 20642-05-1
- IUPAC Name:
- potassium formate(1:2)
- Reference substance name:
- potassium formate (1:2)
- IUPAC Name:
- potassium formate (1:2)
- Details on test material:
- - Name of test material (as cited in study report): Formi-LHS; Formi LHS-Super
- Molecular formula (if other than submission substance): C2H3O4 K
- Molecular weight (if other than submission substance): 130.14
- Substance type: double salt
- Physical state: white powder
- Analytical purity: not reported; information available at the sponsor
- Impurities (identity and concentrations):
- Storage condition of test material: in sealed container at room temperature (10-30°C) in the dark
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- other: Crl:CDBR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 6 weeks
- Weight at study initiation: males: 166 to 208 g; females; 136 to 173 g.
- Housing: groups of 5 rats per cage
- Diet: ad libitum
- Water: ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): routinely 19 to 25°C
- Humidity (%): 40 to 70%
- Air changes (per hr): minimum 15/hour
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- other: diet
- Details on oral exposure:
- - Dosing: test substance was mixed into the diet.
- Diet: ground SQC Rat and Mouse Maintenance Diet No. 1, free access to diet and to tap water.
- Stability of TS in diet: at least 2 weeks
- Replacement of diet: regularly within 2 weeks
- Dose levels:
- Main study: 0, 600, 1200, 3000 mg/kg bw/day.
- Recovery study: 0 and 3000 mg/kg bw/day.
- Absorption study: 3000 mg/kg bw/day. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The enzymatic method "Formic Acid" by Boehringen Mannheim was used
- Duration of treatment / exposure:
- 13 weeks
- Frequency of treatment:
- 7 days/week
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 600, 1200, 3000 mg/kg bw/day
Basis:
nominal in diet
- No. of animals per sex per dose:
- Main study: 10 per sex and dose group.
Recovery study: 10 per sex of the control and the high dose groups.
Absorption study: 10 per sex of the high dose group. - Control animals:
- yes, concurrent no treatment
- Details on study design:
- Post-exposure period: Satellite group: 4 weeks
- Positive control:
- Not required
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
Mortality, clinical signs: observed at least daily.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: weekly
BODY WEIGHT: Yes
- Time schedule for examinations: recorded before first treatment, at weekly intervals and before necropsy.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal group determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: before treatment and in week 12
- Dose groups that were examined: all main-study animals were examined before treatment and all control and high dose animals in week 12.
HAEMATOLOGY: Yes
- Time schedule for collection of blood: week 13 in main study, week 17 in recovery study
- How many animals: all animals
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: week 13 in main study, week 17 in recovery study
- How many animals: week 13 in main study, week 17 in recovery study
URINALYSIS: Yes
- Time schedule for collection of urine: week 13 in main study, week 17 in recovery study
- Metabolism cages used for collection of urine: yes
OTHER:
ABSORPTION
0.5 ml blood samples were taken on Day 1 of feeding and during weeks 13 and 17 by tail vein puncture. Plasma was separated and stored at below -10°C until analysis of formate using the Formic Acid method by Boehringer Mannheim.
GROSS PATHOLOGY
- All animals except those of the absorption study were subjected to terminal necropsy after sacrifice.
- Organ weights: adrenals, kidneys, liver, testes and epididymides were weighed before fixation.
HISTOPATHOLOGY
Histopathology: samples of the following tissues were fixed in 10% buffered formalin. Eyes were fixed in Davidson's fluid.
Adrenals, aorta#, brain, cecum, colon, duodenum, eyes, femur with marrow and articular surface#, gross lesions, Harderian glands#*, head#, heart, ileum, jejunum, kidneys, lacrimal glands#*, larynx, liver, lungs, mammary (females)#, mandibular lymph nodes, mesenteric lymph nodes, muscle quadriceps#, esophagus, optic nerves#, ovaries, pancreas, pituitary, prostate#, rectum, salivary glands, sciatic nerves, seminal vesicles#, skin#, spinal cord (cervical, lumbar, thoracic)#, spleen, sternum with bone marrow, stomach, testes and epididymides, thymus, thyroids an parathyroids, tongue#, urinary bladder, uterus, nasal turbinates#*, nasopharynx#*, vagina#, Zymbal glands*#.
# = tissue retained in fixative but not examined. * = retained in situ with the head
All organs and tissues in the control and high dose group animals were histopathologically examined following hematoxylin and eosin staining. Additionally, kidneys, lungs and gross lesions from the intermediate groups were examined. Following observations in the stomachs of high dose animals, the stomachs of the low and intermediate dose group animals were also examined, together with the stomachs from the animals at the end of the recovery period. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes - Other examinations:
- Absorption and recovery within 4 weeks
- Statistics:
- Body weight gains, necropsy body weight, hematology and clinical chemistry variables were analyzed using ANOVA, separately for each sex. Dunnett's multiple test was used for comparison between control and treated group. A regression test was performed to determine whether there was a linear relationship between increasing dose and response. Organ weights were analyzed using ANCOVA and Dunnett's test.
All recovery study data were analyzed using ANCOVA.
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- effects observed, treatment-related
- Urinalysis findings:
- effects observed, treatment-related
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- not specified
- Details on results:
- CLINICAL SIGNS AND MORTALITY
There were no treatment-related clinical observations or mortalities. Of the 3 mortalities observed (2 controls, 1 high dose female), necropsy confirmed that all were associated with the orbital sinus blood sampling.
BODY WEIGHT AND WEIGHT GAIN
In males, there was a significant and dose-related reduction of body weight gain. The overall difference from the controls (Weeks 0-13) was statistically significant in all three groups (p<0.05, <0.01, and <0.001 in the low, intermediate, and high dose, resp.). In females, body weight gain was also reduced. Significance was gained only in the high dose group (p<0.01).
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study)
A slight dose-related reduction of food intake was noted in all male groups. In females, a reduction was seen only in the high dose group. No level of statistical significance was reached in any group. In the treatment-free recovery groups food intake was comparable to the control rats.
For details of resulting doses see "Remarks on results". The authors argued that reduced body weight gain and food intake were probabl relate to reduced palability of the test diets.
OPHTHALMOSCOPIC EXAMINATION
No treatment related effects noted.
HAEMATOLOGY
There were small but statistically significant differences from the controls (cf. table in "Remarks on results"). Fluctuations in white blood cell counts were noted for both sexes in all groups with no clear dose-relation or significant trends. Observed changes were not regarded to be of biological or toxicological relevance.
CLINICAL CHEMISTRY
There were small but statistically significant differences from the controls (cf. table in "Remarks on results"). Clotting times were unchanged. Observed changes were not regarded to be of biological or toxicological relevance.
URINALYSIS
Urinary parameters were similar to the controls in all groups except pH. There was a trend towards an increased urinary pH (pH 8 or 9) in the intermediate and high dose groups of both sexes at the end of the treatment period.
After the 4-wk treatment-free period the majority of the high dose rats had a urine pH of 6.0 or 7.0.
ORGAN WEIGHTS
At the end of the treatment period, group mean adjusted kidney, liver, testes and epididymides weights in males were similar to the controls, as were the mean weights of kidneys and liver in females. Reduced adrenal weights compared to controls were noted in males (not significant) and in females (p<0.05).
At the end of the treatment-free period, the mean liver weight of the high dose males was slightly higher (p<0.01) than in controls.
GROSS PATHOLOGY
No remarkable findings, except thickening of the stomach, usually involving the limiting ridge, at the end of the 13-week treatment period. The effect was more pronounced in males, probably due to the higher concentration of the TS in the diet (cf. table in "Remarks on results").
The effect subsided within the 4-week recovery period.
HISTOPATHOLOGY: NON-NEOPLASTIC
There was no other finding than a dose-related increase in the severity and incidence of squamous cell hyperplasia in the stomach. No squamous cell hyperplasia was noted in any of the male and female controls. The histopathological finding correlated with the thick stomach findings during necropsy.
The effect was largely reversible within the 4-week treatment-free period.
OTHER FINDINGS
Absorption study
Formate plasma levels following 3000 mg/kg bw/day were below the LOD (Level of Detection, i.e. 62.54 µg/ml) in all but few animals on Day 1. In Week 13, mean plasma levels were increased and slightly above the LOD in animals from both sexes in the early morning, consistent with the nocturnal feeding habit, but decreased within few hours to below the LOD.
In Week 17, formate levels were below the LOD at the end of the 4-week recovery period. Thus, there was no accumulation of formate detectable in plasma over time.
======================================================
Examination LOD Males Females
at (time) (µg/ml) (µg/ml) (µg/ml)
--------------------------------------------------------------------------------
62.54
Day 1
18:00 h < LOD < LOD
24:00 h max. 88.3
Day 2
06:00 h max. 114.4
15:00 h < LOD < LOD
Week 13 18:00 h < LOD < LOD
next day, 06:00 h mean: 158 mean: 96.6
next day, 15:00 h < LOD < LOD
End of 4-week recovery period < LOD < LOD
======================================================
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Remarks:
- systemic toxicity; calcium diformate
- Effect level:
- 3 000 other: mg/kg/day (calculated)
- Sex:
- male/female
- Basis for effect level:
- other: Read across from potassium diformate (1:2). No systemic toxicity or target organ
- Dose descriptor:
- NOAEL
- Remarks:
- systemic toxicity; potassium diformate
- Effect level:
- 3 000 mg/kg bw/day (actual dose received)
- Sex:
- male/female
- Basis for effect level:
- other: No systemic toxicity or target organ
- Dose descriptor:
- NOAEL
- Remarks:
- local irritation; potassium diformate
- Effect level:
- < 600 mg/kg bw/day (actual dose received)
- Sex:
- male/female
- Basis for effect level:
- other: Local irritation. Squamous cell hyperplasia in the forestomach of male and female rats seen at all tested dose levels.
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Consumption
of test substance:
The
consumption of test substance was close to the nominal dose levels.
Dose group |
Nominal dose (mg/kg/day |
Males |
Females |
Low |
600 |
591 |
589 |
Intermediate |
1200 |
1177 |
1178 |
High |
3000 |
2879 |
2951 |
Hematology:
At Week 13: There were small but statistically significant differences from the controls (cf. table). Clotting times were unchanged.
Fluctuations
in white blood cell counts were noted for both sexes in all groups
with no clear dose-relation or significant trends.
|
Males |
Females |
||||
|
Low |
Intermediate |
High |
Low |
Intermediate |
High |
RBC |
|
|
Incr* |
|
|
|
MCV |
|
|
Decr*** |
|
Decr* |
Decr*** |
MCH |
|
|
Decr** |
|
|
Decr* |
MCHC |
|
|
|
|
|
Incr** |
Platelet |
|
|
Incr*** |
|
|
|
WBC |
|
|
Incr** |
|
|
|
Levels
of statistical significance: *
= p<0.05; ** = p<0.01; ***
= p<0.001
RBC =
red blood cell count MCV =
mean cell volume
MCH =
mean cell hemoglobin MCHC
= mean cell hemoglobin concentration
WBC =
white blood cell count
Incr = increase Decr = decrease
At
Week 17: At
the end of the 4-week recovery significant changes were only noted in females
as
tabulated below.
|
Males |
Females |
||||
|
Low |
Intermediate |
High |
Low |
Intermediate |
High |
Hb |
|
|
|
|
|
Incr* |
RBC |
|
|
|
|
|
Incr* |
HK |
|
|
|
|
|
Incr* |
Hb =
hemoglobin HK
= hematocrit
Clinical
chemistry:
Isolated
fluctuations were noted among all groups without a clear trend.
Statistically significant findings are listed below.
At
week 13:
|
Males |
Females |
||||
|
Low |
Intermediate |
High |
Low |
Intermediate |
High |
AST |
|
|
Incrtrend |
|
|
|
AP |
|
|
Incrtrend |
|
|
|
Total bilirubin |
|
|
|
|
|
Decr* |
Total protein |
|
|
|
|
|
Decr* |
|
|
|
|
|
|
|
K |
|
|
Decr*** |
|
|
|
Ca |
|
|
|
|
|
Decr* |
|
|
|
|
|
|
|
Creatinine |
|
|
Decr*** |
Incr.* |
|
Decr* |
Urea |
|
|
|
Incr.* |
Incr.* |
|
Total cholesterol |
|
|
|
Incr.* |
Incr.* |
|
|
|
|
|
|
|
|
Globulin |
|
|
|
|
|
Decr* |
Albumin/globulin ratio |
|
|
|
|
|
Decr* |
Levels
of statistical significance: *
= p<0.05; **
= p<0.01; ***
= p<0.001
AST =
aspartate aminotransferase
AP =
alkaline phosphatase
Totbilirub =
total bilirubin
A/G ratio =
albumin/globulinratio
At
Week 17
At the end of the 4-week recovery significant changes were as tabulated below.
|
Males |
Females |
||||
|
Low |
Intermediate |
High |
Low |
Intermediate |
High |
AST |
|
|
Incr** |
|
|
|
AP |
|
|
Incr*** |
|
|
Incr** |
|
|
|
|
|
|
|
Glucose |
|
|
Decr** |
|
|
Decr** |
Urinalysis:
Urinary
parameters were similar to the controls in all groups except pH.
There
was a trend towards an increased urinary pH (pH 8 or 9) in the
intermediate and high dose groups of both sexes at the end of the
treatment period.
After the 4-wk treatment-free period the majority of the high dose rats
had a urine pH of 6.0 or 7.0.
Necropsy
Table:
local effects: incidences of thickening of the stomach
|
Males |
Females |
||||
|
Low |
Intermediate |
High |
Low |
Intermediate |
High |
Week 13 |
1/10 |
3/10 |
7/10 |
0/10 |
2/10 |
5/10 |
|
|
|
|
|
|
|
Week 17 |
0/10 |
0/10 |
2/10 |
0/10 |
0/10 |
0/10 |
Organ
weights
At
the end of the treatment period, group mean adjusted kidney, liver,
testes and epididymides weights in males were similar to the controls,
as were the mean weights of kidneys and liver in females. Reduced
adrenal weights compared to controls were noted in males (not
significant) and in females (p<0.05).
At the end of the treatment-free period, the mean liver weight of the high
dose
males was slightly higher (p<0.01) than in controls.
Histopathology
Table:
Incidence of squamous cell hyperplasia in the forestomach (local
effect)
|
Males |
Females |
||||
|
Low |
Intermediate |
High |
Low |
Intermediate |
High |
Week 13 |
|
|||||
n |
10 |
10 |
10 |
10 |
10 |
10 |
Grade 0 |
6 |
1 |
0 |
6 |
2 |
0 |
Grade 1 |
2 |
6 |
4 |
4 |
6 |
5 |
Grade 2 |
2 |
3 |
5 |
0 |
2 |
3 |
Grade 3 |
0 |
0 |
1 |
0 |
0 |
2 |
|
||||||
Week 17 |
|
|||||
n |
|
|
10 |
|
|
9 |
Grade 0 |
|
|
6 |
|
|
7 |
Grade 1 |
|
|
4 |
|
|
3 |
Grade 2 |
|
|
|
|
|
|
Grade 3 |
|
|
|
|
Applicant's summary and conclusion
- Conclusions:
- Local effects were seen in the stomach in both sexes in a dose-dependent manner at 1200 and at 3000 mg/kg bw/day. Clear systemic toxicity was not seen at any dose, including 3000 mg/kg bw/day, the highest dose tested. The NOAEL for systemic toxicity was therefore 3000 mg potassium diformate/kg bw/day in the rat, equivalent to 3000 mg calcium diformate/kg bw/day.
- Executive summary:
The repeated dose of potassium diformate(1:2) was examined in a subchronic rat study according to the OECD guideline 408 and under GLP conditions. The guideline requirements were exceeded in that an absorption study and a recovery study were also included.
A read across from potassium diformate is justified because potassium diformate decomposes in aqueous solution into one molecule of each formate and formic acid, and the potassium ion. Thus, potassium diformate gives two formate anions on a molar basis. Local effects of the formic acid formed can be neglected because these are not expected with neutral salts (sodium, potassium, ammonium, calcium formate). Read across can therefore be limited to systemic effects.
In the 13-week oral fed study potassium diformate (1:2) was administered in the diet at dose levels of 0, 600, 1200, and 3000 mg/kg bw/day to 10 rats/sex/dose. The doses were selected based on the results of a 7 day range finding study. Additional animals were used in satellite studies, i.e. a 4-week recovery study (0 and 3000 mg/kg bw/day, 10 rats/sex/dose), and in an absorption study (3000 mg/kg bw/day, 10 rats/sex/dose).
In the absorption study, formate blood levels were below the level of detection (LOD; 62.54 µg/mL) in most instances. Slightly increased levels in the range 66 to 158 µg/mL were occasionally seen in some animals few hours after the nocturnal food uptake, but these declined to below the detection limit within few hours. Blood levels were also below the LOD at the end of the 4-week recovery period.
These findings indicate that formate is rapidly metabolised in the rat, and that there was no accumulation over the 13-week treatment period.
Main study: no mortality or clinical signs of toxicity were seen. Male body weight gain was significantly decreased in all treated groups, whereas in females body weight reduction gained a level of significance only in the high dose group animals. A slightly reduced food consumption was seen in groups with reduced body weights. Test substance consumption was close to the nominal doses, i.e. 0, 590, 1180, and 2880 (males) and 2950 (females) mg/kg bw/day, respectively. Reduced body weight gain and food consumption resulted possibly from a reduced palability of the diet, and from the local irritation.
There were no effects in ophthalmology. No clear effects were seen in hematology and clinical chemistry. Some parameters gained a level of statistical significance, but this was of no biological or toxicological relevance. Organ weights of male and female rats were similar to those of the controls.
Pathology revealed no remarkable finding except from local irritation, evidenced by the observation of a thickening of the limiting ridge in the stomach in all male groups and in the female high dose group at the end of the 13-week period. Histopathology revealed a dose-related increase in the incidence and severity of squamous cell hyperplasia in the forestomach of male and female rats. This effect was largely reversible in the 4-week recovery group.
Overall, there was no overt systemic toxicity or target organ in this study. A dose-related body weight decrease was seen in all treated males and in the high dose female group, possibly as a result of the reduced palability of the diet. The small but statistically significant changes in hematology and clinical chemistry parameters in the high dose animals were not of toxicological significance, due to the small changes and the lack of target organ toxicity.
A specific target organ was the stomach, based on local irritation in the forestomach which caused a dose-related thickening of the stomach at all dose levels, and was confirmed to be squamous cell hyperplasia. This was considered to be a response to minor irritation by the test substance, rather than a toxic effect (Covance, 1998).
Conclusion:
Overall, dietary administration of potassium diformate (1:2) to rats at 600, 1200, and 3000 mg/kg bw and day for 13 weeks did not produce any overt systemic toxicity. Minor local irritation had occurred in the forestomach of both sexes, with effects being seen in the males at all dose levels. Recovery was not complete in all animals after the 4-week treatment-free period.
The authors did not derive NOAEL values, but they may be considered as follows:
Local irritation: NOAEL below 600 mg/kg bw/day, based on the irritation of the forestomach and the squamous cell hyperplasia seen at 600 mg/kg bw and day in both sexes.
Systemic toxicity: NOAEL(rat, 90 day study) 3000 mg Formi LHS/kg bw/day, as no adverse effect was seen at the highest dose tested. Taking stoichiometry and formula weights into consideration, this is equivalent to 3000 mg calcium diformate/kg bw/day.
This subchronic toxicity study in the rat is acceptable and satisfies the guideline requirement for a subchronic oral study (OECD 408).
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.