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EC number: 209-942-9 | CAS number: 598-62-9
- 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 5 January 2010 to 19 January 2010
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Study conducted in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results. The study report was conclusive, done to a valid guideline and the study was conducted under GLP conditions. Use of data on MnO to address data requirements of MnCO3 is considered to be justified on the basis that manganese is in the same oxidation state in both substances, the anions in both substances are not regarded as toxic, and both substances are expected to have similar dermal absorption due to their poor water solubility and inorganic nature. Furthermore, both substances exhibited no dermal or eye irritation and both substances were found to exert no toxicity when dosed at the maximum permissible level in acute oral toxicity studies (thereby confirming the similarity of the toxicological profile of both substances, related to exposure to Mn2+).
- Justification for type of information:
- The data on the read-across substance is considered representative.
Cross-reference
- Reason / purpose for cross-reference:
- other: Target record
Reference
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study conducted on read-across material
- Justification for type of information:
- The data on the read-across substance is considered representative.
- Reason / purpose for cross-reference:
- read-across source
- Parameter:
- SI
- Remarks on result:
- other: Not sensitising
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: Not sensitising
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- 1344-43-0
- Cas Number:
- 1344-43-0
- IUPAC Name:
- 1344-43-0
- Reference substance name:
- Manganese oxide
- EC Number:
- 215-695-8
- EC Name:
- Manganese oxide
- Cas Number:
- 1344-43-0
- Molecular formula:
- MnO
- IUPAC Name:
- Oxomanganese
- Reference substance name:
- Manganese oxide
- IUPAC Name:
- Manganese oxide
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
- Details on test material:
- - Name of test material : MnO (Erachem)
- Substance type: Green powder
- Physical state: solid
- Impurities (identity and concentrations): Fe - 96 ppm, Ins ac -15 ppm, H20 @ 105°c - 0.01%
- Composition of test material, percentage of components: Mn -77.8 %, MnO2 - 0.46%
- Purity test date: 29/09/08
- Lot/batch No.: 104833-06
- Storage condition of test material: room temperature in the dark
Constituent 1
Constituent 2
Constituent 3
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- other: CBA/Ca
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Harlan Laboratories UK Limited, Bicester. Oxon, UK
- Age at study initiation: 8 to 12 weeks
- Weight at study initiation: 15 to 23 g
- Housing: Individually housed in suspended solid-floor polypropylene cages furnished with softwood woodflakes
- Diet : Free access to 2014 Teklad Global Rodent diet (Harlan Teklad, Bicester, Oxon, UK)
- Water : Free access to mains tap water
- Acclimation period: 5 days minimum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 to 25 °C
- Humidity (%): 30 to 70 %
- Air changes (per hr): 15 changes per hour
- Photoperiod (hrs dark / hrs light): Twelve hour cycle (06:00 to 18:00 continuous light)
Study design: in vivo (LLNA)
- Vehicle:
- propylene glycol
- Concentration:
- 2.5, 5 and 10 % w/w
- No. of animals per dose:
- 4 animals per dose in the main test, with one animal in the preliminary test.
- Details on study design:
- RANGE FINDING TESTS:
- Irritation and toxicity : A preliminary screening test was performed using one mouse. The mouse was treated by daily application of 25 µL of the test substance at a concentration of 10 % w/w in propylene glycol to the dorsal surface of each ear for three consecutive days. The mouse was observed daily on days 1, 2 and 3 and once a day on days 4, 5 and 6. Signs of toxicity or excessive local irritation were recorded. The bodyweight of the mouse was recorded on day 1 (prior to dosing) and 6.
- Compound solubility: The vehicle was chosen based on its ability to produce the highest concentration that was suitable for dosing. The concentration for dosing was selected on the basis that the dose produces a solution or fine homogenous suspension that can be administered via a micropipette.
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Criteria used to consider a positive response: The test substance will be regarded as a sensitiser if at least one concentration of the test substance results in a threefold or greater increase in 3HTdR incorporation comapred to control values. Any test substance failing to produce a threefold or greater increase in 3HTdR incorporations will be classified as a non-sensitiser.
TREATMENT PREPARATION AND ADMINISTRATION: Groups of four mice were treated with the test substance at concentrations of 10%, 5% or 2.5 w/w in propylene glycol. The mice were treated daily by application of 25 µL of the appropriate concentration of the test substance to the dorsal surface of each ear for three consecutive days (1, 2, and 3). The test substance formulation was administered using an automatic micropipette and spread over the dorsal surface of the ear using the tip of the pipette. A further groups of four mice received the vehicle alone in the same manner.
Five days following the first topical application of the appropriate treatment all mice were injected via the teil vein with 250 µL of phosphate buffered saline (PBS) containing 3H-methyl thymidine (3HTdR: 80 µCi/mL, specific activity 2.0 Ci/mmol) giving a total of 20 µCi to each mouse.
Five hours following administration of 3HTdR all mice were killed by carbon dioxide asphyxiation. The draining auricular lymph nodes from the four mice were excised and pooled for each experimental group. For each group 1 mL of PBS was added to the pooled lymph nodes.
A single cell suspension of pooled lymph node cells was prepared by gentle mechanical disaggregation through a 200-mesh stainless steel gauze. The lymph node cells were rinsed through the gauze with 4 mL of PBS into a petri dish labelled with the project number and dose concentration. The lymph node cell suspension was transferred to a centrifuge tube. The petri dish was washed with an additional 5 mL of PBS to remove all remaining lymph node cells and these were added to the centrifuge tube. The pooled lymph node cells were pelleted at 1400 rpm (approximately 190 g) for ten minutes. The pellet was resuspended in 10 mL of PBS and re-pelleted. To precipitate out the radioactive material, the pellet was resuspended in 3 mL of 5 % Trichloroacetic acid (TCA).
After 18 hours incubation at approximately 4 °C, the precipitates were recovered by centrifugation at 2100 rpm (approximately 450 g) for 10 minutes, resuspended in 1 mL of TCA and transferred to 10 mL of scintillation fluid (Optiphase Trisafe). 3HTdR incorporation was measured by β-scintillation counting. The Poly Q vials containing the samples and scintillation fluid were placed in the sample changer of the scintillator and left for approximately twenty minutes to reduce the risk of luminescence. After 20 minutes the vials were shaken vigorously. The number of radioactive disintigrations per minute was then measure using the Beckman LS6500 scintillation system. - Positive control substance(s):
- other: Phenylacetaldehyde (90%)
- Statistics:
- The stimulation Index was calculated by dividing the mean radioactive incorporation for each treatment group by the mean radioactive incorporation of the vehicle control.
Results and discussion
- Positive control results:
- The Stimulation Index for phenylacetaldehyde (90%) was considered to be a positive sensitiser under the conditions of the test (see table 1).
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Value:
- 1.21
- Test group / Remarks:
- 2.5 % (w/w) in propylene glycol
- Remarks on result:
- other: Negative
- Parameter:
- SI
- Value:
- 1.31
- Test group / Remarks:
- 5 % (w/w) in propylene glycol
- Remarks on result:
- other: Negative
- Parameter:
- SI
- Value:
- 1.03
- Test group / Remarks:
- 10 % (w/w) in propylene glycol
- Remarks on result:
- other: Negative
- Parameter:
- other: DPM (Disintegrations Per Minute)
- Value:
- 3 734.44
- Test group / Remarks:
- Vehicle
- Remarks on result:
- other: Negative
- Parameter:
- other: DPM (Disintegrations Per Minute)
- Value:
- 4 535.63
- Test group / Remarks:
- 2.5 % (w/w) in propylene glycol
- Remarks on result:
- other: Negative
- Parameter:
- other: DPM (Disintegrations Per Minute)
- Value:
- 4 876.24
- Test group / Remarks:
- 5 % (w/w) in propylene glycol
- Remarks on result:
- other: Negative
- Parameter:
- other: DPM (Disintegrations Per Minute)
- Value:
- 3 853.15
- Test group / Remarks:
- 10 % (w/w) in propylene glycol
- Remarks on result:
- other: Negative
Any other information on results incl. tables
Table 2. The stimulation index expressed as the mean radioactive incorporation for each treatment group divided by the mean radioactive incorporation of the vehicle control group are as follows:
Concentration (% w/w) in propylene glycol |
Stimulation Index |
Result |
2.5 |
1.21 |
Negative |
5 |
1.31 |
Negative |
10 |
1.03 |
Negative |
Table 3. Clinical observations, Bodyweight and Mortality Data – Preliminary Screening Test
Concentration (% w/w) propylene glycol |
Animal Number |
Bodyweight (g) |
Day |
|||||||||
1 |
2 |
3 |
4 |
5 |
6 |
|||||||
Day 1 |
Day 6 |
Pre-Dose |
Pre-Dose |
Pre-Dose |
Pre-Dose |
Pre-Dose |
Pre-Dose |
|||||
10 |
S-1 |
20 |
20 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 = No signs of systemic toxicity
Table 4. Disintegrations per minute, Disintegrations per Minute/Node and Stimulation Index
Concentration (% w/w) in propylene glycol |
dpm |
Dpm/Nodea |
Stimulation Indexb |
Result |
Vehicle |
3734.44 |
466.81 |
na |
na |
2.5 |
4535.63 |
566.95 |
1.21 |
Negative |
5 |
4876.24 |
609.53 |
1.31 |
Negative |
10 |
3853.15 |
481.64 |
1.03 |
Negative |
dpm = Disintegrations per minute
a = Disintegrations per minute/node obtained by dividing the disintegrations per minute value by 8 (total) number of lymph nodes)
b = Stimulation Index of 3.0 or greater indicates a positive result
na = Not applicable
Table 5. Individual Bodyweights and Bodyweight changes
Concentration (% w/w) in propylene glycol |
Animal Number |
Bodyweight (g) |
Bodyweight Change (g) |
|
Day 1 |
Day 6 |
|||
Vehicle |
1-1 |
21 |
20 |
-1 |
1-2 |
20 |
19 |
1 |
|
1-3 |
23 |
21 |
-2 |
|
1-4 |
19 |
21 |
2 |
|
2.5 |
2-1 |
21 |
20 |
-1 |
2-2 |
18 |
17 |
-1 |
|
2-3 |
20 |
19 |
-1 |
|
2-4 |
22 |
21 |
-1 |
|
5 |
3-1 |
18 |
19 |
1 |
3-2 |
19 |
20 |
1 |
|
3-3 |
19 |
18 |
-1 |
|
3-4 |
20 |
20 |
0 |
|
10 |
4-1 |
20 |
20 |
0 |
4-2 |
20 |
20 |
0 |
|
4-3 |
22 |
21 |
-1 |
|
4-4 |
20 |
18 |
-2 |
Applicant's summary and conclusion
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The test substance was considerd to be a non-sensitiser under the conditions of the test.
- Executive summary:
The skin sensitisation potential of the test substance was investigated in a study which was conducted under GLP conditions and in accordance with the standardised guidelines OECD 429 and EU Method B.42.
Under the conditions of the study the test substance was concluded to be a non sensitiser.
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