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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
Toxicity to soil macroorganisms except arthropods
Administrative data
- Endpoint:
- toxicity to soil macroorganisms except arthropods: long-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study conducted on read-across material
- Remarks:
- Conducted to a guideline with plenty of detail.The read-across from MnSO4 to Mn(NO3)2 is justified on the following basis: both substances are very soluble in water hence bioavailable and both will release Mn2+ ions. Therefore, from an ecotoxicity standpoint, the nitrate or sulphate anions are not considered to have any influence on the effective toxicity of Mn2+ or any toxicity in their own right, so the anions can be disregarded. Therefore any effect will be related to the Mn2+ cation, and the data from MnSO4 ecotoxicity tests is regarded as a suitable surrogate for read-across
- Justification for type of information:
- See the read-across report attached in Section 13.
Cross-reference
- Reason / purpose for cross-reference:
- other: Read-across target
Reference
- Endpoint:
- toxicity to soil macroorganisms except arthropods: long-term
- Type of information:
- read-across based on grouping of substances (category approach)
- 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:
- See the read-across report attached in Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 28 d
- Dose descriptor:
- LOEC
- Effect conc.:
- 267 mg/kg soil dw
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- other: Mn
- Basis for effect:
- reproduction
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 157 mg/kg soil dw
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- other: Mn
- Basis for effect:
- reproduction
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 002
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- ISO 11268-2 (Effects of Pollutants on Earthworms. 2. Determination of Effects on Reproduction)
- Deviations:
- yes
- Remarks:
- Natural soil was used instead of an artificial substrate
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Manganese sulphate monohydrate
- IUPAC Name:
- Manganese sulphate monohydrate
- Details on test material:
- - Name of test material (as cited in study report): Manganese sulphate monohydrate
- Lot/batch No.: Stock# 33341 Lot#I18129
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
Test substrate
- Details on preparation and application of test substrate:
- The soil was a natural soil containing 1.2% organic matter.
Test organisms
- Test organisms (species):
- Enchytraeus sp.
- Animal group:
- annelids
Study design
- Study type:
- laboratory study
- Substrate type:
- natural soil
- Limit test:
- no
- Total exposure duration:
- 28 d
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 28 d
- Dose descriptor:
- LOEC
- Effect conc.:
- 267 mg/kg soil dw
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- other: Mn
- Basis for effect:
- reproduction
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 157 mg/kg soil dw
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- other: Mn
- Basis for effect:
- reproduction
Any other information on results incl. tables
The natural background manganese concentration determined in the negative control treatment was 94 mg/kg. Total extractable manganese concentrations (in excess of background) in the experimental treatments ranged from 50 to 117% and averaged 94% of nominal. Exchangeable Mn fraction expressed as percent of total concentration increased with increasing soil Mn loads.
Table 1: Nominal and measured concentrations
Nominal (mg/kg) |
Measured (mg/kg) |
Corrected recovery (%) |
0 |
94 |
- |
10 |
99 |
50 |
18 |
110 |
89 |
31 |
119 |
80 |
54 |
157 |
117 |
94 |
191 |
103 |
164 |
267 |
105 |
287 |
386 |
102 |
503 |
644 |
109 |
Range finding test:
Range finding test for manganese was conducted using MnSO4·H20. Adult survival decreased by 10% at 500 mg/kg and by 95% at 1,000 mg/kg. Juvenile production decreased by 33% at 100 mg/kg. There were no surviving adults above 1,000 mg/kg or juveniles above the 100 mg/kg treatment concentrations.
Definitive test:
Test results complied with the validity criteria defined in the test guideline. Mean adult survival in negative controls ranged from 97.5 to 100%. The mean juvenile production in negative controls ranged from 735 to 1104 juveniles, and the coefficient of variation ranged from 6 to 18%.
Manganese did not affect (P = 0.721) adult E. crypticus survival up to 191 mg/kg concentration. Adult survival was reduced by 5% (P = 0.48) at 267 mg/kg. Juvenile numbers were significantly (P < 0.0001) higher in the 99 mg/kg treatment compared to negative control suggesting the hormetic effect of Mn on reproduction at this exposure level. The bounded No Observed Adverse Effect Concentration (NOAEC) for juvenile production was 157 mg/kg (P = 0.52). The bounded Lowest Observed Adverse Effect Concentration (LOAEC) for juvenile production was 191 mg/kg (P < 0.0001). No juveniles were produced in 644 mg/kg treatment. The hormetic effect at the 99 mg/kg concentration level suggested the use of the hormetic model to estimate ECp parameters for Mn data.
Applicant's summary and conclusion
- Conclusions:
- The NOEC was 157 mg Mn/kg. The read-across from MnSO4 to Mn(NO3)2 is justified on the following basis: both substances are very soluble in water hence bioavailable and both will release Mn2+ ions. Therefore, from an ecotoxicity standpoint, the nitrate or sulphate anions are not considered to have any influence on the effective toxicity of Mn2+ or any toxicity in their own right, so the anions can be disregarded. Therefore any effect will be related to the Mn2+ cation, and the data from MnSO4 ecotoxicity tests is regarded as a suitable surrogate for read-across
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