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EC number: 915-009-3 | CAS number: -
- 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
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- Endpoint summary
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- 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
A 28-day repeated dose oral toxicity test (OECD 422) was performed for the substance. No adverse effects were observed in the study.
This result applies to all category members and no repeated dose toxicity of the test substance is thus expected.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- Adopted 29 July 2016
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Details on species / strain selection:
- This strain has been used for non-clinical safety studies, recommended by regulatory agencies.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source:
Taconic Biosciences, Inc., USA, through its representative Vivo Bio Tech Ltd., Telangana, INDIA, a vendor approved by the Test Facility Management.
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: 11-12 weeks
- Weight at study initiation: mal =: 302-372 g, female: = 204-249 g
- Fasting period before study: no
- Housing:
Animals were housed in Room No. AR-47 of the experimental animal facility of INTOX. Animals were housed maximum three per sex / cage in solid [Sized:42 cm (L) x 29 cm (W) x 19 cm (H)] bottom polypropylene cages with stainless steel grill tops, facilities for food and water bottle, and with bedding of clean and sterilized corn cob. The cages were suspended on stainless steel racks. Cages were suspended on movable stainless steel racks arranged in such a way that every cage would receive almost same amount of light. For this purpose, cages arranged on the first row were shifted to the last row, those on the second row were shifted to first row. Likewise all the cages were rotated. This kind of cage rotation was carried out every week throughout the treatment and observation period. Animals were housed in groups or singly, as below.
Pre-mating period: males and females were housed in groups of maximum two or three per cage per sex.
During mating (co-habitation): one male : one female, per cage.
Post-mating: females were housed individually once they were successfully mated. Males were housed in groups of maximum three per cage. During the post-natal (lactation) period the dam was housed individually.
- Diet (e.g. ad libitum): 'Altromin' brand extruded pelleted rat feed manufactured by M/s Altromin Spezialfutter GmbH & Co. KG, Germany, was provided ad libitum.
- Water (e.g. ad libitum): Potable water, passed through ‘Aquaguard’ water filter, and subjected to ultra violet irradiation, was provided ad libitum in sterilized glass bottles.
- Acclimation period:
The animals were acclimatised for a period of at least five days to the experimental room.
DETAILS OF FOOD AND WATER QUALITY:
The diet has been tested and certified to be free from undesired levels of environmental contaminants. Results of feed analysis were provided by the manufacturer for each batch of diet.
Water is analysed quarterly for potability and once in a year for various environmental contaminants.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-25°
- Humidity (%): 30-70%
- Air changes (per hr): 10-15/h
- Photoperiod (hrs dark / hrs light): 12 hours dark / 12 hours light
IN-LIFE DATES: From: 17 November 2017 To: 07 February 2018 - Route of administration:
- oral: gavage
- Details on route of administration:
- The oral route is an accidental route of exposure in humans.
- Vehicle:
- water
- Details on oral exposure:
- - PREPARATION OF DOSING SOLUTIONS:
The dosing formulations were prepared freshly each day before dosing. Analytical grade water was used as vehicle control item. Formulations for different doses were vary in concentrations to allow a constant dosage volume of 5 ml/kg body weight.
Required amount of test item was weighed on analytical balance, then analytical grade water was added gradually to achieve appropriate concentrations i.e. 50, 100 and 200 mg/ml to meet dosage level requirements.
- VEHICLE
Test item was completely soluble in analytical grade water, hence analytical grade water was chosen as a vehicle for the dosing formulation. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Test item formulations (for all concentrations) were subjected for verification of concentration twice (i.e. in first week after initiation of treatment and in last week at termination of treatment) during the study.
The following conditions were used:
Element-Matrix: Manganese (Mn)
Instrument type: Flame -AAS
Lamp current: 10 mA
Wavelength: 279.5 nm
Slit width: 0.2 nm
Flame Type: Air/Acetylene
Air Flow: 10 L/minute
Acetylene Flow: 2 L/minute
Diluent: Analytical grade water
Instrument mode: Absorbance
Calibration mode: Concentration
Measurement mode: Integrate
The analytical method was validated by determining the parameters viz., Linearity, Accuracy (% Recovery), Precision (Repeatability), Limit of detection (LOD) and Limit of quantification (LOQ) using Atomic Absorption Spectrometer.
For stability study, formulations at different doses were prepared in analytical grade water and analysed for determination of test item concentration after 4 hours. Data on test item concentrations after 4 hours at specified storage condition were compared with the data obtained before storage. On the basis of the calculated % deviation of test item concentration, stability of Manganese concentration in Reaction mixture of MnEDTA, MnDTPA and MnHEEDTA prepared in analytical grade water was determined. Based on the results of stability study, it is concluded that, Reaction mixture of MnEDTA, MnDTPA and MnHEEDTA is Stable in analytical grade water after specified storage conditions. - Duration of treatment / exposure:
- Males were dosed for a minimum of four weeks, up to and including the day before scheduled sacrifice (this included a minimum of two weeks prior to mating, during the mating period and, approximately, two weeks post mating).
Females were dosed throughout the study period. This included two weeks prior to mating (with the objective of covering at least two complete oestrous cycles), the variable time to conception, the duration of pregnancy and thirteen days after delivery, up to and including the day before scheduled sacrifice. - Frequency of treatment:
- Daily dosing
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Dose / conc.:
- 250 mg/kg bw/day (nominal)
- Dose / conc.:
- 500 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 10 males and 15 females
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale:
Repeated Dose 14 Days Oral Toxicity Study of Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA in Wistar Rat (Dose Range Finding Study) was performed in compliance with the Study Plan (No. P/17189/SOR-14-DRF/17). Groups of three male and three female Wistar rats were administered with test item, by oral gavage daily at the doses of 125, 250, 500 and 1000 mg/kg body weight for 14 days and were sacrificed on day 15 to evaluate its toxicity. Concurrent vehicle control group receiving analytical grade water at the dose of 5 ml/kg was also maintained. The test item did not induce any mortality and treatment related clinical abnormalities in rats treated at and up to the dose of 1000 mg/kg body weight. No mortality or abnormal clinical signs were observed in vehicle control group animals.
Body weight gain and food consumption was not affected at and up to the dose of 1000 mg/kg body weight. The values of absolute and relative organ weights of male and female rats treated with test item, at and up to the dose of 1000 mg/kg were found to be comparable with those of the control rats at termination. No gross pathological alterations were encountered in the rats sacrificed at termination of the study.
Based on these findings, the doses selected for the "Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test of Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA in Wistar Rat" are 250, 500 and 1000 mg/kg body weight.
- Rationale for animal assignment (if not random): random assignment
- Rationale for selecting satellite groups: not applicable
- Post-exposure recovery period in satellite groups: not applicable
- Section schedule rationale (if not random): not applicable - Positive control:
- no
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule:
All signs of ill health, together with any behavioural changes or reaction to treatment were observed (cage side observation) once a day for individual animals. Dated and signed records of appearance, change and disappearance of clinical signs were maintained on clinical history sheets.
Throughout the study, all animals were checked early on each working day and again in the afternoon to look for dead or moribund animals to allow necropsy examination to be carried out during the working hours of that day.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule:
Once before the first exposure (to allow for within-subject comparisons), and once a week thereafter, detailed clinical observations were made in all parental animals. The rats were subjected to detailed clinical examinations before initiation of the treatment (to allow for within-subject comparisons) and weekly thereafter during the treatment period.
These observations were made outside the home cage in a standard arena and preferably at the same time. Signs noted included, changes in skin, fur, eyes and mucous membranes, occurrence of secretions, excretions and autonomic activity such as lacrimation, piloerection, pupil size and unusual respiratory pattern. Changes in gait, posture and response to handling as well as the presence of clonic or tonic movements, stereotypies, difficult or prolonged parturition or bizarre behavior were also recorded.
BODY WEIGHT: Yes
- Time schedule for examinations:
Males and females were weighed on the first day of dosing, weekly thereafter, and at termination. During pregnancy, females were weighed on days 0, 7, 14 and 20 and then within 24 hours of parturition (day 1 post-partum), and at day 4 and day 13 post-partum.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
During pre-mating, food consumption was measured weekly (on days 0, 7 and 14). During pregnancy it was measured on gestation day 0, 7, 14 and 20 and in lactation on days 4 and 13. Food consumption during mating period was not measured.
Food consumption was computed as the amount of food consumed in grams per animal per day.
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood:
After completion of premating period (day 14 from start of treatment) haematological examination was made in five males and five females randomly selected from each group.
- Anaesthetic used for blood collection: Yes (light CO2 anaesthesia)
- Animals fasted: Yes
- How many animals: five males and five females randomly selected from each group
- Parameters checked in table 1 were examined.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood:
At termination (day 29 for males and day 14 of lactation for females)
- Animals fasted: Yes
- How many animals: five males and five females randomly selected from each group.
- Parameters checked in table 2 were examined.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: Yes
- Time schedule for examinations:
In males, these functional observations were made towards the end of their dosing period, shortly before scheduled sacrifice but before blood sampling for haematology or clinical chemistry.
In females these functional tests were made during the last week of lactation (e.g., LD 6-13), shortly before scheduled sacrifice.
- Dose groups that were examined: each group
- Battery of functions tested: sensory activity / grip strength / motor activity
IMMUNOLOGY: Yes
Based on the haematology
- Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
The testes, epididymides, prostate, seminal vesicles with coagulating glands as a whole, levator ani plus bulbocavernosus muscle complex, Cowper’s glands and glans penis of all male adult animals were weighed at termination of treatment (on day 29). Uterus with cervix and ovaries from all adult females were weighed at termination on lactation day 14.
From all adult males and females, thyroid glands were preserved and weighed post fixation. At lactation day 13 the thyroid glands from 1 male and 1 female pup per litter were preserved and weighed post fixation.
Trimming was done very carefully and only after fixation to avoid tissue damage.
In addition, from five adult males and females, randomly selected from each group, the liver, kidneys, adrenals, thymus, spleen, brain and heart were trimmed of any adherent tissue, as appropriate and their weights were taken as soon as possible after dissection to avoid drying.
HISTOPATHOLOGY: Yes (see table 3)
From five adult males and females, randomly selected from each group, the following tissues were fixed in 10% neutral buffered formalin, were embedded in paraffin wax, sectioned at 5 μm thickness and stained with haematoxylin and eosin, for microscopic examination.
Microscopic examination was carried out on tissues as listed below:
On all listed organs and tissues of selected five males and five females of groups G1 (control) and G4 (high dose), sacrificed at termination.
In absence of any microscopic alteration in the thyroid glands of adult male and female rats and in absence of any alterations in the values of total T4, microscopic evaluation of thyroid glands from the pups was not carried out. - Statistics:
- Statistical analysis was performed using IBM SPSS Statistical Software (version 23). For statistical analysis, the litter was used as the basic sampling unit. Following statistical methods were used to analyse the various parameters:
One-way ANOVA followed by Dunnett's test (parametric): Premating Body weight and body weight gain, Premating Food Consumption, Gestational and lactational body weights and body weight gain, Gestational and lactational food consumption, Organ weight (Absolute and relative)
The results of these statistical analysis were assessed at 5% level of significance (p = 0.05) and designated as significantly higher (S+) / lower (S-) than control values. - Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- no effects observed
- Description (incidence and severity):
- Based on the results of haematology especially Total and Differential Leucocyte Counts and general blood picture along with results of organ weights and histopathology of thymus and spleen, there was no evidence of immunological effects.
- Organ weight findings including organ / body weight ratios:
- effects observed, non-treatment-related
- Description (incidence and severity):
- A few instances of statistically significant (p<0.05) changes when compared to that of control organ weights were noticed and were considered incidental as they were within historical control ranges. They were;
G4M - Mean absolute weight of adrenals 0.056 ± 0.001; Historical data range 0.032 to 0.077 g
G4M - Mean relative weight of adrenals 0.016 ± 0.001; Historical data range 0.011 to 0.024 g
G2M - Mean absolute weight of epididymides 1.50 ± 0.09; It is considered incidental as there was no dose dependency. - Gross pathological findings:
- no effects observed
- Neuropathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Some incidental and spontaneous lesions observed in animals from the control and high dose group (1000 mg/kg) comprised of cortical vacuolation in adrenals; sub-mucosal lymphocytic infiltration in rectum; dilated glands and cystic glands in stomach and ultimobranchial cyst in thyroid. All these changes were of minimal severity and are commonly observed in rats of this age and were not considered to be treatment related.
- Other effects:
- not examined
- Dose descriptor:
- NOAEL
- Effect level:
- >= 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- behaviour (functional findings)
- body weight and weight gain
- clinical biochemistry
- clinical signs
- food consumption and compound intake
- gross pathology
- haematology
- histopathology: neoplastic
- histopathology: non-neoplastic
- immunology
- mortality
- neuropathology
- organ weights and organ / body weight ratios
- Critical effects observed:
- no
- Conclusions:
- Groups of ten male and fifteen female Wistar rats were administered with the test item Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA daily by oral gavage at the doses of 250, 500 and 1000 mg/kg of body weight to evaluate its systemic toxicity and effects on reproduction and development. Males were dosed for a period of four weeks and females were dosed for 50 to 60 days (this included two weeks prior to mating, the variable time to conception, the duration of pregnancy and thirteen days after delivery). The findings of this study were as follows:
* no treatment related deaths; no neurotoxic potential;
* no clinical abnormalities;
* no effect on average body weight and body weight gain during premating, mating, gestation and lactation period in females and no effect on average body weight and body weight gain during premating and mating period in males.
* no effect on the average daily food intake in treated rats;
* no effects on the haematological parameters;
* no effects on the blood chemistry parameters; no effects on total T4 levels;
* no alterations in the absolute and relative organ weights;
* no remarkable gross pathological alterations in tissues/organs;
* no histopathological alterations, suggestive of systemic toxicity, at 1000 mg/kg dose level;
* no effects on organ weight data, gross and histopathological alterations in reproductive organs;
* no effects on reproductive performance, gestation, parturition, lactation and litter data.
Based on the findings of this study, it is concluded that, the No-Observed-Adverse-Effect-Level (NOAEL) of Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA in Wistar rats, following oral administration for a period of four weeks for males and 50 to 60 days for females for systemic toxicity and for reproductive and developmental toxicity was found to be equal to or greater than 1000 mg/kg body weight. - Executive summary:
‘Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening test of Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA in Wistar rat’ was performed in compliance with the Organization for Economic Co-operation and Development (OECD) Guidelines for Testing of Chemicals (No. 422, Section 4: Health Effects) “Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test”, adopted by the council on 29 July 2016 and in accordance with the mutually agreed Study Plan (No. P/17190/CRRDT/17).
Groups of ten male and fifteen female Wistar rats were administered with the test item Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA daily by oral gavage at the doses of 250, 500 and 1000 mg/kg of body weight. A concurrent control group of ten males and fifteen females receiving the vehicle, i.e. analytical grade water at 5 ml/kg was also maintained. Males were dosed for a period of four weeks, up to and including the day before scheduled sacrifice. Females were dosed (50 to 60 days) throughout the study. This included two weeks prior to mating, the variable time to conception, the duration of pregnancy and thirteen days after delivery, up to and including the day before scheduled sacrifice.
The rats were examined daily for signs of toxicity, morbidity and mortality. They were subjected to detailed clinical examination before initiation of the study and weekly thereafter during the treatment period and at termination. Animals were additionally examined (five males and five females per group) for assessment of sensory reactivity, assessment of grip strength and motor activity. In males, these functional tests were made towards the end of their dosing period and in females during the last week of lactation (i.e. Lactation day 6-13). Males and females were weighed on the first day of dosing, weekly thereafter and at termination. During pregnancy, females were weighed on days 0, 7, 14, 20 and then within 24 hours of parturition (day 1 post-partum), at day 4 and day 13 post-partum. During pre- mating, food consumption was measured weekly (on days 0, 7 and 14). During pregnancy it was measured on gestation day 0, 7, 14 and 20 and during lactation on days 4 and 13. Vaginal smears of all females were monitored daily during pretreatment, premating treatment period and during mating period until evidence of mating. After parturition, each litter was examined for number and sex of pups, still births, live births, runts and the presence of gross abnormalities. Litters were weighed within 24 hours of parturition (day 0 or 1 post-partum) and on day 4 and day 13 post- partum. The anogenital distance of each pup was measured daily on the postnatal day (PND) 0 to PND 4. Pup body weight was recorded daily on PND 0 to PND 4 and at termination on day 13. The number of nipples / areolae in male pups were counted on PND 12. Total T4 assessments were carried out on few pups on day 4 and day 13 after birth.
Laboratory investigations were performed on male and female rats at baseline, at completion of premating period and at termination. All animals sacrificed terminally (males on day 29 and females at lactation day 14) were subjected to a detailed necropsy and weights of testes, epididymides, prostate, seminal vesicles with coagulating glands as a whole, levator ani plus bulbocavernous muscle complex, Cowper’s glands, glans penis of all adult males, the ovaries and uterus with cervix of all adult females were recorded.
In addition weights of liver, kidneys, adrenals, thymus, spleen, brain and heart from five adult males and females, randomly selected from each group were taken.
Thyroid gland from all adult male and female rats, from one male and one female pups of day 13 from each litter were also weighed. Histopathological evaluation was performed on all tissues in five male and five female rats from the control and high dose groups.
There was no incidence of any treatment related mortality amongst the rats treated with the Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA at any of the dose levels in both males and females. Treatment with Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA for males (28 days) and for females (50 to 60 days involving pregnancy and lactation period) did not induce any adverse clinical signs at any dose levels. No abortion/premature deliveries were observed during the study period.
The functional observations (neurological examinations) did not reveal any remarkable and treatment related incidence of neurological abnormalities. Also no findings, indicative of a neurotoxic potential of the test item, were encountered during these examinations.
Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA at and up to the dose of 1000 mg/kg dose group did not have any remarkable and adverse effects on the weight gain by the treated male and female rats in this study. The values of mean body weights and mean body weight gain for rats treated with test item at and up to 1000 mg/kg did not differ significantly (p>0.05) from those of the concurrent control group rats during premating, gestation period and the post-natal lactation period.
The test item did not have any adverse effect on the average daily food consumption by the male and female rats treated at any of the dose levels. The haematological and clinical chemistry parameters of male and female rats treated with the test item were found to be comparable to those of baseline values and also comparable to the control animals. The values of absolute and relative organ weights of male and female rats treated with test item were found to be comparable with those of the control group rats at the end of treatment period.
No treatment related gross pathological changes were noted. Histopathological examination was performed on tissues of the control and high dose group animals, where the changes in the high dose group were incidental or comparable to the control group or unrelated to treatment.
No evidence of immunological effect was observed.
The reproductive organ weight data, gross and histopathological examination of reproductive organs did not reveal any treatment related changes. Data regarding development and reproduction indicated no difference between the animals treated with the test item and the vehicle control.
Based on the findings of this study, it is concluded that, the No-Observed-Adverse-Effect-Level (NOAEL) of Reaction Mixture of MnEDTA, MnDTPA and MnHEEDTA in Wistar rats, following oral administration for a period of four weeks for males and 50 to 60 days for females for systemic toxicity and for reproductive and developmental toxicity was found to be equal to or greater than 1000 mg/kg body weight.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Justification for classification or non-classification
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