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Motor alterations associated with exposure to manganese in the environment in Mexico

Overexposure to manganese (Mn) causes neurotoxicity (a Parkinson-like syndrome) or psychiatric damage (“manganese madness”). Several studies have shown alterations to motor and neural behavior associated with exposure to Mn in the workplace. However, there are few studies on the effects of environme...

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Published in:The Science of the total environment 2006-09, Vol.368 (2), p.542-556
Main Authors: Rodríguez-Agudelo, Yaneth, Riojas-Rodríguez, Horacio, Ríos, Camilo, Rosas, Irma, Sabido Pedraza, Eva, Miranda, Javier, Siebe, Christina, Texcalac, José Luis, Santos-Burgoa, Carlos
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creator Rodríguez-Agudelo, Yaneth
Riojas-Rodríguez, Horacio
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Rosas, Irma
Sabido Pedraza, Eva
Miranda, Javier
Siebe, Christina
Texcalac, José Luis
Santos-Burgoa, Carlos
description Overexposure to manganese (Mn) causes neurotoxicity (a Parkinson-like syndrome) or psychiatric damage (“manganese madness”). Several studies have shown alterations to motor and neural behavior associated with exposure to Mn in the workplace. However, there are few studies on the effects of environmental exposure of whole populations. We studied the risk of motor alterations in people living in a mining district in Mexico. We studied 288 individual people (168 women and 120 men) from eight communities at various distances from manganese extraction or processing facilities in the district of Molango. We measured manganese concentrations in airborne particles, water, soil and crops and evaluated the possible routes of Mn exposure. We also took samples of people's blood and determined their concentrations of Mn and lead (Pb). We used “Esquema de Diagnóstico Neuropsicológico” Ardila and Ostrosky-Solís's neuropsychological battery to evaluate motor functions. Concentrations of Mn in drinking water and maize grain were less than detection limits at most sampling sites. Manganese extractable by DTPA in soils ranged between 6 and 280 mg kg − 1 and means were largest close to Mn extraction or processing facilities. Air Mn concentration ranged between 0.003 and 5.86 μg/m 3; the mean value was 0.42 μg/m 3 and median was 0.10 μg/m 3, the average value (geometric mean) resulted to be 0.13 μg/m 3. Mean blood manganese concentration was 10.16 μg/l, and geometric mean 9.44 μg/l, ranged between 5.0 and 31.0 μg/l. We found no association between concentrations of Mn in blood and motor tests. There was a statistically significant association between Mn concentrations in air and motor tests that assessed the coordination of two movements (OR 3.69; 95% CI 0.9, 15.13) and position changes in hand movements (OR 3.09; CI 95% 1.07, 8.92). An association with tests evaluating conflictive reactions (task that explores verbal regulations of movements) was also found (OR 2.30; CI 95% 1.00, 5.28). It seems from our results that people living close to the manganese mines and processing plants suffer from an incipient motor deficit, as a result of their inhaling manganese-rich dust.
doi_str_mv 10.1016/j.scitotenv.2006.03.025
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Several studies have shown alterations to motor and neural behavior associated with exposure to Mn in the workplace. However, there are few studies on the effects of environmental exposure of whole populations. We studied the risk of motor alterations in people living in a mining district in Mexico. We studied 288 individual people (168 women and 120 men) from eight communities at various distances from manganese extraction or processing facilities in the district of Molango. We measured manganese concentrations in airborne particles, water, soil and crops and evaluated the possible routes of Mn exposure. We also took samples of people's blood and determined their concentrations of Mn and lead (Pb). We used “Esquema de Diagnóstico Neuropsicológico” Ardila and Ostrosky-Solís's neuropsychological battery to evaluate motor functions. Concentrations of Mn in drinking water and maize grain were less than detection limits at most sampling sites. Manganese extractable by DTPA in soils ranged between 6 and 280 mg kg − 1 and means were largest close to Mn extraction or processing facilities. Air Mn concentration ranged between 0.003 and 5.86 μg/m 3; the mean value was 0.42 μg/m 3 and median was 0.10 μg/m 3, the average value (geometric mean) resulted to be 0.13 μg/m 3. Mean blood manganese concentration was 10.16 μg/l, and geometric mean 9.44 μg/l, ranged between 5.0 and 31.0 μg/l. We found no association between concentrations of Mn in blood and motor tests. There was a statistically significant association between Mn concentrations in air and motor tests that assessed the coordination of two movements (OR 3.69; 95% CI 0.9, 15.13) and position changes in hand movements (OR 3.09; CI 95% 1.07, 8.92). An association with tests evaluating conflictive reactions (task that explores verbal regulations of movements) was also found (OR 2.30; CI 95% 1.00, 5.28). 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Several studies have shown alterations to motor and neural behavior associated with exposure to Mn in the workplace. However, there are few studies on the effects of environmental exposure of whole populations. We studied the risk of motor alterations in people living in a mining district in Mexico. We studied 288 individual people (168 women and 120 men) from eight communities at various distances from manganese extraction or processing facilities in the district of Molango. We measured manganese concentrations in airborne particles, water, soil and crops and evaluated the possible routes of Mn exposure. We also took samples of people's blood and determined their concentrations of Mn and lead (Pb). We used “Esquema de Diagnóstico Neuropsicológico” Ardila and Ostrosky-Solís's neuropsychological battery to evaluate motor functions. Concentrations of Mn in drinking water and maize grain were less than detection limits at most sampling sites. Manganese extractable by DTPA in soils ranged between 6 and 280 mg kg − 1 and means were largest close to Mn extraction or processing facilities. Air Mn concentration ranged between 0.003 and 5.86 μg/m 3; the mean value was 0.42 μg/m 3 and median was 0.10 μg/m 3, the average value (geometric mean) resulted to be 0.13 μg/m 3. Mean blood manganese concentration was 10.16 μg/l, and geometric mean 9.44 μg/l, ranged between 5.0 and 31.0 μg/l. We found no association between concentrations of Mn in blood and motor tests. There was a statistically significant association between Mn concentrations in air and motor tests that assessed the coordination of two movements (OR 3.69; 95% CI 0.9, 15.13) and position changes in hand movements (OR 3.09; CI 95% 1.07, 8.92). An association with tests evaluating conflictive reactions (task that explores verbal regulations of movements) was also found (OR 2.30; CI 95% 1.00, 5.28). 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Several studies have shown alterations to motor and neural behavior associated with exposure to Mn in the workplace. However, there are few studies on the effects of environmental exposure of whole populations. We studied the risk of motor alterations in people living in a mining district in Mexico. We studied 288 individual people (168 women and 120 men) from eight communities at various distances from manganese extraction or processing facilities in the district of Molango. We measured manganese concentrations in airborne particles, water, soil and crops and evaluated the possible routes of Mn exposure. We also took samples of people's blood and determined their concentrations of Mn and lead (Pb). We used “Esquema de Diagnóstico Neuropsicológico” Ardila and Ostrosky-Solís's neuropsychological battery to evaluate motor functions. Concentrations of Mn in drinking water and maize grain were less than detection limits at most sampling sites. Manganese extractable by DTPA in soils ranged between 6 and 280 mg kg − 1 and means were largest close to Mn extraction or processing facilities. Air Mn concentration ranged between 0.003 and 5.86 μg/m 3; the mean value was 0.42 μg/m 3 and median was 0.10 μg/m 3, the average value (geometric mean) resulted to be 0.13 μg/m 3. Mean blood manganese concentration was 10.16 μg/l, and geometric mean 9.44 μg/l, ranged between 5.0 and 31.0 μg/l. We found no association between concentrations of Mn in blood and motor tests. There was a statistically significant association between Mn concentrations in air and motor tests that assessed the coordination of two movements (OR 3.69; 95% CI 0.9, 15.13) and position changes in hand movements (OR 3.09; CI 95% 1.07, 8.92). An association with tests evaluating conflictive reactions (task that explores verbal regulations of movements) was also found (OR 2.30; CI 95% 1.00, 5.28). It seems from our results that people living close to the manganese mines and processing plants suffer from an incipient motor deficit, as a result of their inhaling manganese-rich dust.</abstract><cop>Shannon</cop><pub>Elsevier B.V</pub><pmid>16793118</pmid><doi>10.1016/j.scitotenv.2006.03.025</doi><tpages>15</tpages></addata></record>
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subjects Adult
Air
Biological and medical sciences
Chemical and industrial products toxicology. Toxic occupational diseases
Environment exposure
Environmental Exposure - adverse effects
Environmental Exposure - analysis
Environmental Monitoring
Environmental Pollutants - analysis
Environmental Pollutants - blood
Environmental Pollutants - toxicity
Environmental pollutants toxicology
Female
Humans
Industrial Waste - analysis
Lead - blood
Male
Manganese
Manganese - analysis
Manganese - blood
Manganese - toxicity
Medical sciences
Metals and various inorganic compounds
Mexico
Middle Aged
Mining
Motor alterations
Motor Skills - drug effects
Neuropsychological Tests
Neurotoxicity
Poaceae - chemistry
Toxicology
Zea mays
Zea mays - chemistry
title Motor alterations associated with exposure to manganese in the environment in Mexico
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