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EC number: 233-828-8 | CAS number: 10377-66-9
- 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
Endpoint summary
Administrative data
Description of key information
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2010-04-07 to 2010-05-11.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted to GLP and to current guideline.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 420 (Acute Oral Toxicity - Fixed Dose Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.1 bis (Acute Oral Toxicity - Fixed Dose Procedure)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- fixed dose procedure
- Limit test:
- yes
- Species:
- rat
- Strain:
- Wistar
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Female Wistar (HsdRccHan:WIST) strain rats were supplied by Harlan Laboratories UK Limited, Bicester, Oxon, UK.
- Age at study initiation: Eight to twelve weeks.
- Weight at study initiation: 153 - 189 g. The bodyweight variation did not exceed ± 20% of the initial/mean bodyweight of any previously dosed animal(s).
- Fasting period before study: Overnight fast immediately before dosing and for approximately three to four hours after dosing.
- Housing: The animals were housed in groups of up to four in suspended solid floor polypropylene cages furnished with woodflakes.
- Diet : Free access to food (2014 Teklad Global Rodent diet supplied by Harlan Teklad, Blackthorn, Bicester, Oxon, UK) was allowed throughout the study.
- Water : Free access to mains drinking water was allowed throughout the study.
- Acclimation period: At least five days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): Temperature set to achieve limits of 19 to 25°C.
- Humidity (%): Relative humidity set to achieve limits of 30 to 70%.
- Air changes (per hr): At least fifteen changes per hour.
- Photoperiod (hrs dark / hrs light): Lighting was controlled by a time switch to give twelve hours continuous light (06:00 to 18:00) and twelve hours darkness. - Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on oral exposure:
- VEHICLE
- Concentration in vehicle: 280.4 mg/ml and 42.1 mg/ml
MAXIMUM DOSE VOLUME APPLIED: 10 ml/kg
DOSAGE PREPARATION (if unusual): For the purpose of the study the test material was freshly prepared, as required, as a solution in distilled water.
The test material was formulated within two hours of being applied to the test system. It is assumed that the formulation was stable for this duration.
- Rationale for the selection of the starting dose: Using available information on the toxicity of the test material, 2804 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight) was chosen as the starting dose. - Doses:
- Dose levels of 2804 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight) and 421 mg/kg (equivalent to 300 mg active ingredient/kg bodyweight).
- No. of animals per sex per dose:
- A single female was treated at a dose level of 2804 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight).
Five females were treated at a dose level of 421 mg/kg (equivalent to 300 mg active ingredient/kg bodyweight). - Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Clinical observations were made ½, 1, 2, and 4 hours after dosing and then daily for up to fourteen days. Morbidity and mortality checks were made twice daily. Individual bodyweights were recorded on Day 0 (the day of dosing) and on Days 7 and 14 or at death.
- Necropsy of survivors performed: yes. - Statistics:
- Using the mortality data obtained, an estimate of the acute oral median lethal dose (LD50) of the test material was made.
- Preliminary study:
- Dose Level - 2804 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight):
Individual clinical observations and mortality data are given in Table 1.
Mortality:
The animal was killed for humane reasons two hours after dosing, due to the approach of the moderate severity limit set by the UK Home Office.
Clinical Observations:
Signs of systemic toxicity noted were hunched posture, lethargy, tiptoe gait, abdominal discomfort and pilo erection.
Bodyweight:
The bodyweight on Day 0 and at death are given in Table 2.
Necropsy:
Necropsy findings are given in Table 3.
Abnormalities noted at necropsy of the animal treated at a dose level of 2804 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight) were patchy pallor of the liver, pale kidneys and severe haemorrhage of the gastric mucosa.
Based on the results at a dose level of 2804 mg/kg, a dose level of 421 mg/kg bodyweight was investigated. - Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- > 300 mg/kg bw
- Based on:
- test mat.
- Remarks:
- anhydrous equivalent
- Mortality:
- Dose Level - 421 mg/kg (equivalent to 300 mg active ingredient/kg bodyweight):
There were no deaths.
At 2804 mg/kg (equivalent to 2000 mg active ingredient/kg bodyweight, the single female rat tested had to be humanely killed.
Individual clinical observations and mortality data are given in Table 4. - Clinical signs:
- other: Dose Level - 421 mg/kg (equivalent to 300 mg active ingredient/kg bodyweight): No signs of systemic toxicity were noted during the observation period.
- Gross pathology:
- Dose Level - 421 mg/kg (equivalent to 300 mg active ingredient/kg bodyweight):
Individual necropsy findings are given in Table 6.
No abnormalities were noted at necropsy. - Interpretation of results:
- Category 4 based on GHS criteria
- Conclusions:
- The acute oral median lethal dose (LD50) of the test material in the female Wistar strain rat is greater than 300 mg/kg bodyweight (Globally Harmonised Classification System - Category 4). The effects seen in the single animal tested at the highest dose are most likely due to the severe local action of the test substance, rather than a true systemic effect.
Reference
Table 1 Individual Clinical Observations and Mortality Data -2804 mg/kg
Dose Level mg/kg |
Animal Number and Sex |
Effects Noted After Dosing |
Effects Noted During Period After Dosing |
||||||||||||||||
½ |
1 |
2 |
4 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
||
2804+ |
1-0 Female |
HLWt |
HLWtAd |
HLPWtX* |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
+ = Equivalent to 2000 mg active ingredient/kg bodyweight)
H= Hunched posture
L = Lethargy
Wt = Tiptoe gait
Ad = Abdominal discomfort
P = Pilo‑erection
X* = Animal was killed for humane reasons due to the approach of the moderate severity limit set by the UK Home Office
Table 2 Individual Bodyweights and Bodyweight Changes -2804 mg/kg
Dose Level mg/kg |
Animal Number and Sex |
Bodyweight (g) at Day |
Bodyweight (g) |
Bodyweight Gain (g) |
|||
0 |
7 |
14 |
1 |
2 |
|||
2804+ |
1-0 Female |
153 |
- |
- |
151 |
- |
- |
+ = Equivalent to 2000 mg active ingredient/kg bodyweight)
- = animal dead
Table 3 Necropsy Findings - 2804 mg/kg
Dose Level |
Animal Number |
Time of Death |
Macroscopic Observations |
2804+ |
1-0 Female |
Humanely Killed Day 0 |
Liver: patchy pallor Kidneys: pale Gastric mucosa: severe haemorrhage |
+ = Equivalent to 2000 mg active ingredient/kg bodyweight)
Table 4 Individual Clinical Observations and Mortality Data - 421mg/kg*
Dose Level mg/kg |
Animal Number and Sex |
Effects Noted After Dosing |
Effects Noted During Period After Dosing |
||||||||||||||||
½ |
1 |
2 |
4 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
||
421* |
2-0 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3-0 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-1 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-2 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-3 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
* = Equivalent to 300 mg active ingredient/kg bodyweight)
0= No signs of systemic toxicity
Table 5 Individual Bodyweights and Bodyweight Changes - 421mg/kg*
Dose Level mg/kg |
Animal Number |
Bodyweight (g) at Day |
Bodyweight Gain (g) During Week |
|||
0 |
7 |
14 |
1 |
2 |
||
421* |
2-0 Female |
171 |
184 |
193 |
10 |
9 |
3-0 Female |
156 |
160 |
168 |
4 |
8 |
|
3-1 Female |
184 |
189 |
200 |
5 |
11 |
|
3-2 Female |
162 |
167 |
177 |
5 |
10 |
|
3-3 Female |
189 |
193 |
209 |
4 |
16 |
* = Equivalent to 300 mg active ingredient/kg bodyweight)
Table 6 Individual Necropsy Findings- 421mg/kg*
Dose Level |
Animal Number |
Time of Death |
Macroscopic Observations |
421* |
2-0 Female |
Killed Day 14 |
No abnormalities detected |
3-0 Female |
Killed Day 14 |
No abnormalities detected |
|
3-1 Female |
Killed Day 14 |
No abnormalities detected |
|
3-2 Female |
Killed Day 14 |
No abnormalities detected |
|
3-3 Female |
Killed Day 14 |
No abnormalities detected |
* = Equivalent to 300 mg active ingredient/kg bodyweight)
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Justification for classification or non-classification
Manganese dinitrate is classified as acutely toxic by the oral route. However, it is considered that the classification is based on local effects rather than systemic effects, due to the corrosive nature of the substance.
Manganese dinitrate is not classified as acutely toxic by either the inhalation or dermal routes and testing is not appropriate due to the corrosive nature of the substance.
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