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Cortes-Maramba, Nelia; Reyes, J.P.; Panganiban, L.C.P.; Francisco-Rivera, Ana Trinidad; Suplido, M.L.; Akagi, Hirokatsu
Co-ordinated research project on health impacts of mercury cycling in contaminated environments studied by nuclear techniques. Report on the second research co-ordination meeting2002
Co-ordinated research project on health impacts of mercury cycling in contaminated environments studied by nuclear techniques. Report on the second research co-ordination meeting2002
AbstractAbstract
[en] Mercury pollution in most parts of the regions in the world are caused by release into the environment of metallic mercury used in the recovery of gold by an amalgamation technique with subsequent mercury emission into the atmosphere by blowtorching operations. Significant small-scale gold mining operations in other countries such as Tanzania, Philippines, Indonesia, China and Vietnam have been reported with roughly 10 million people estimated to be involved in these activities Artisanal gold mining activities using mercury has proliferated in various parts of the country since the early 1980's. In Southern Philippines, it is estimated that a small-scale gold processor utilizes one kilogram of mercury every week or an average of fifty-two kgs/1yr. Production is estimated at 30 kilograms of gold per day. It has been estimated that 140 tons of mercury flux has been dumped directly into the river systems from small-scale gold mining operations in one of the gold rush areas in the country. In the 1980's, gold rush activities intensified in Northeastern Mindanao providing livelihood opportunities to about 80,000-120,000 people at the height of mining activities in the area. In gold mining areas it should be noted that transformation in the natural environment of inorganic mercury to methylmercury occurs which can easily bio-accumulate in fish and other organisms through the aquatic food chains. Therefore, there are two main exposure pathways of mercury contamination that can affect the human population in gold mining areas. First, gold miners and workers are exposed to inorganic mercury due to direct inhalation of mercury during gold recovery processes and second, people living along the river systems and depending on riverine products for food sources can be exposed to methylmercury mainly through fish consumption. Presently, environmental and health monitoring conducted by several government agencies in the recent past were limited to the determination of total mercury only. Previous studies undertaken focused mainly on the exposure of adults and workers to mercury during mining/processing operations. Fifty-three (53) research subjects were selected by stratified random sampling in a mining community in Sibutad, Zamboanga del Norte, Philippines. There were 40 (75.47%) adults aged from 26 to 50 years and 13 children aged 6 months to 11 years. Environmental monitoring results showed that ambient air monitoring of three sampling station exceeded the standards for mercury in ambient air. Water quality monitoring of a drinking water source showed a slightly higher level than that obtained from a nearby river. Mercury levels in marine/aquatic samples ranged from 4.03-62.97 ng/g for total mercury and 3.75-35.98 ng/g in 9 species. These levels were below the recommended USFDA standard of 500 ng/g. The proportion of methylmercury ranged from 22.98%-89.78%. Hair samples in 51 respondents showed total mercury and methylmercury levels which ranged from 0.95-68.68 ng/g and 0.73-5.81 ng/g. The proportion of methylmercury in hair ranged from 2.66-99.98%. 10 had elevated total mercury levels and 23 with elevated methylmercury levels. Blood samples from 50 respondents showed total mercury and methylmercury levels ranged from 2.74-29.47 ug/L and 1. 63-23.11 ug/L. A total of 23 blood samples from the 50 tested showed total mercury values will be followed up for possible detoxification while 10 had elevated methylmercury levels. (author)
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International Atomic Energy Agency, Section of Nutritional and Health-Related Environmental Studies, Vienna (Austria); 168 p; 2002; p. 75-90; 2. research co-ordination meeting on health impacts of mercury cycling in contaminated environments studied by nuclear techniques; Minamata (Japan); 22-26 Oct 2001; 14 refs, 2 figs, 6 tabs
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Report
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Conference
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ADULTS, AGE GROUPS, AGED ADULTS, ANIMALS, AQUATIC ORGANISMS, BIOLOGICAL MATERIALS, BODY, BODY FLUIDS, ELEMENTS, ENVIRONMENTAL QUALITY, HUMAN POPULATIONS, HYDROGEN COMPOUNDS, MAMMALS, MAN, MATERIALS, METALS, MINORITY GROUPS, ORGANIC COMPOUNDS, ORGANIC MERCURY COMPOUNDS, ORGANS, OXYGEN COMPOUNDS, POLLUTION, POPULATIONS, PRIMATES, SKIN, SURFACE WATERS, TRANSITION ELEMENTS, VERTEBRATES, WATER
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