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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
Epidemiological data
Administrative data
- Endpoint:
- epidemiological data
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- well-documented study, non-audited, no history on wives; parity not taken into account. Read-across from manganese sulphate to manganese nitrateis justified based on having both high water solubility and structural similarities. Specifically, both substances have anions containing multiple oxygens. In addition the percentage contribution of Mn2+ in both substances is comparable.
Data source
Reference
- Reference Type:
- publication
- Title:
- Fertility of male workers exposed to mercury vapor or to manganese dust: A questionnaire study
- Author:
- Lauwerys R, Roels H, Genet P, Toussaint G, Bouckaert A & de Cooman S
- Year:
- 1 985
- Bibliographic source:
- American Journal of Industrial Medicine, 7:171-176
Materials and methods
- Study type:
- cohort study (prospective)
- Endpoint addressed:
- toxicity to reproduction / fertility
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The fertility of male workers exposed to manganese dust was assessed with the use of questionnaire. A fertility questionnaire was applied to the total male work force of a manganese salts and oxides factory and two control plants with comparable workload characteristics.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Manganese dust (dioxide, carbonate, sulphate or manganese ore itself)
- IUPAC Name:
- Manganese dust (dioxide, carbonate, sulphate or manganese ore itself)
- Details on test material:
- Name of test material (as cited in study report): Manganese dusts (dioxide, carbonate, sulphate) including manganese ore
Other: The concentration of manganese was measured as total dust
Constituent 1
Method
- Type of population:
- occupational
- Ethical approval:
- not specified
- Details on study design:
- HYPOTHESIS TESTED : The possible interference of manganese on the reproductive system in male workers occupationally exposed.
METHOD OF DATA COLLECTION
- Type: Questionnaire and Clinical examinations.
- Details: The questionnaire contained questions on fertility along with questions on duration of employment, residence and smoking and drinking habits. Samples of blood and urine were collected for the determination of manganese.
SETTING: Occupational, the manganese exposed group were recruited from a factory producing manganese salts from concentrated ores
STUDY POPULATION
- Selection criteria: Only Belgian subjects were included, who had been married once. Subjects were excluded in they were widowed, divorced, separated or never married.
- Total number of subjects participating in study: 85 workers exposed to manganese, 81 control workers.
- Sex/age/race: All workers were male and Belgian
- Smoker/nonsmoker: Both were included in the study
COMPARISON POPULATION
- Type: Control or reference group
- Details: The control workers had never been occupationally exposed to manganese.
HEALTH EFFECTS STUDIED
- Disease(s): Fertility problems - Exposure assessment:
- not specified
- Details on exposure:
- TYPE OF EXPOSURE: Occupational
TYPE OF EXPOSURE MEASUREMENT: Personal sampling. Personal samplers were employed to measure total dust during the whole shift.
EXPOSURE LEVELS: Total dust levels over the entire shift ranged from 0.07 to 8.61 mg/m^3 (N = 80) with a median value of 0.97 µg/m^3 (overall arithmetic and geometric mean values, 1.33 and 0.94 mg/m^3 respectively).
EXPOSURE PERIOD: 7.9 ± 5.5 years average - Statistical methods:
- Results were analysed for statistical significance using a χ² test or the Student’s t-test.
Results and discussion
- Results:
- EXPOSURE
- Number of measurements: 80
- Average concentrations: 0.07 to 8.61 mg/m3
- Arithmetic mean: 1.33 mg/m3
- Geometric mean: 0.94 mg/m3
- Median: 0.97 µg/m3
FINDINGS
Please refer to section Remarks on results including tables and figures for full tabulated results.
The matching between the exposed and controls in regard to age of the subject and their wives, age of wife at marriage, age difference between husband and wide, duration of employment in the factory, smoking habits, alcohol consumption, educational level and professional activity of spouse. Very few differences between the groups reached statistical significance. Manganese levels in the urine fluctuated much more than levels in the blood. The median values in the control and exposed groups were 0.16 and 1.17 µg/g creatinine respectively. During the period of exposure to the metal, the number of observed children in the age groups 16-25 and 26-35 was significantly lower than the expected number. The sex ratio was not found to be significantly different. The was no indication that other factors might account for the marked observed fertility difference between the control and the manganese-exposed group. No difference between the wife’s occupations were detected. The proportion of wives performing clerical or manual work was not significantly different. The only statistically significant difference between the group characteristics that might have an influence on fertility (i,e, educational levels of the wives) would tend to decrease the fertility of the control group in comparison to that of the exposed group. - Confounding factors:
- Past exposure to manganese may have been lower than the levels of the study as there was a higher volume of production during the study compared to past years. The only statistically significant difference between the group characteristics that might have an influence on fertility (i.e. educational levels of wives) would tend to decrease the fertility of the control group by comparison to that of the manganese group. This may have masked the effect of manganese on fertility.
- Strengths and weaknesses:
- No extensive monitoring data were available to assess past exposure to manganese. However the same production process had been used for at least 15 years.
Any other information on results incl. tables
Table 1: Characteristics of Control and Manganese-Exposed Male Workers
Control |
Exposed |
P |
|||
Number of subjects |
81 |
|
85 |
|
|
Age (years) |
39.5 ± 10.9a |
(21-58) |
37.4 ± 9.3 |
(21-59) |
NSc |
Age of wife (years) |
38.0 ± 1.6 |
(17-61) |
35.9 ± 9.4 |
(19-58) |
NSc |
Age of wife at marriage (years) |
22.4 ± 3.5 |
(16-34) |
21.4 ± 3.6 |
(17-33) |
NSc |
Duration of employment in the factory (years) |
13.4 ± 10.8 |
(1-40) |
8.1 ± 5.6 |
(1-19) |
<0.001c |
Years of exposure to manganese |
- |
- |
7.9 ± 5.5 |
(1-19) |
|
Percent smokers |
73 |
|
86 |
|
NSd |
Alcohol consumption |
|||||
Yes (% of subjects) |
73 |
|
79 |
|
NSd |
Glasses of beer/week |
18.2 ± 13.9 |
|
22.4 ± 20 |
|
NSc |
Educational level |
|||||
Primary and junior high school (%) |
57 |
|
72 |
|
NSd |
Senior high school and university (%) |
43 |
|
28 |
|
|
Educational level of wife |
|||||
Primary and junior high school (%) |
54 |
|
75 |
|
<0.02d |
Senior high school and university (%) |
46 |
|
26 |
|
|
Wife with a job (%) |
37 |
|
35 |
|
NSd |
Percent desiring a child |
27 |
|
25 |
|
NSd |
Mn-B (µg/100 mL) |
0.57 ± 0.26 |
(0.04-1.31) |
1.29 ± 0.53 |
(0.10-3.30) |
|
Mn-U (µg/g creatinine) |
0.27 ± 0.31 (0.16)b |
(0.1-2.00) |
4.37 ± 15.65 (1.17)b |
(0.09-140.6) |
|
aMean ± SD (range) bMedian cStudent’s t-test dx2 test NS: Statistically not significant. |
Table 2: Fertility of Male Workers Exposed to Manganese Dusts
Age groups |
Exposure |
Number of years of fertility |
Number of children |
P |
|
Observed |
Expected |
||||
16-25 |
Before |
205 |
64 |
64.3 |
NS |
During |
123 |
17 |
38.6 |
<0.05 |
|
26-35 |
Before |
277 |
37 |
28.4 |
NS |
During |
257 |
16 |
1.5 |
<0.05 |
|
36-45 |
Before |
85 |
2 |
3.5 |
NS |
During |
195 |
6 |
|
NS |
|
NS: Statistically not significant (critical ratio) |
Applicant's summary and conclusion
- Conclusions:
- Due to the presence of more than one manganese substance, including possible exposure to manganese ore, it is not possible to make a conclusion about the effect of any particular substance on fertility, or whether the effect may be due to exposure to the ore rather than a single substance. Read-across from manganese sulphate to manganese nitrateis justified based on having both high water solubility and structural similarities. Specifically, both substances have anions containing multiple oxygens. In addition the percentage contribution of Mn2+ in both substances is comparable.
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