The Mt. Diwata study on the Philippines 1999 - assessing mercury intoxication of the population by small scale gold mining

Citation
G. Drasch et al., The Mt. Diwata study on the Philippines 1999 - assessing mercury intoxication of the population by small scale gold mining, SCI TOTAL E, 267(1-3), 2001, pp. 151-168
Citations number
25
Categorie Soggetti
Environment/Ecology
Journal title
SCIENCE OF THE TOTAL ENVIRONMENT
ISSN journal
00489697 → ACNP
Volume
267
Issue
1-3
Year of publication
2001
Pages
151 - 168
Database
ISI
SICI code
0048-9697(20010221)267:1-3<151:TMDSOT>2.0.ZU;2-X
Abstract
The region of Diwalwal, dominated by Mt. Diwata, is a gold rush area on Min danao (Philippines) where approximately 15 000 people live. The fertile pla in of Monkayo is situated downstream, where people grow crops such as rice and bananas; locally caught fish is eaten frequently. The ore is dug in sma ll-scale mines and ground to a powder by ball-mills while still in Diwalwal . The gold is then extracted by adding liquid mercury (Hg), forming gold-am algam. To separate the gold from the Hg, in most cases the amalgam is simpl y heated in the open by blow-torches. A high external Hg burden of the loca l population must be assumed. To evaluate the internal Hg burden of the pop ulation and the extent of possible negative health effects, 323 volunteers from Mt. Diwalwal, Monkayo and a control group from Davao were examined by a questionnaire, neurological examination and neuro-psychological testing. Blood, urine and hair samples were taken from each participant and analyzed for total Hg. A statistical evaluation was possible for 102 workers (occup ationally Hg burdened ball-millers and amalgamsmelters), 63 other inhabitan ts from Mt. Diwata ('only' exposed from the environment), 100 persons, livi ng downstream in Monkayo, and 42 inhabitants of Davao (serving as controls) . The large volume of data was reduced to yes/no decisions. Alcohol as a po ssible bias factor was excluded (level of alcohol consumption and type, see Section 4.4). Each factor with a statistically significant difference of a t least one exposed group to the control group was included in a medical sc ore (0-21 points). In each of the exposed groups this score was significant ly worse than in the control group (median control, 3; downstream, 9; Mt. D iwata, non-occupational exposed, 6; Hg workers, 10). In comparison to the s urprisingly high Hg concentration in blood (median, 9.0 mug/l; max, 31.3) a nd in hair (2.65 mug/g; max, 34.7) of the control group, only the workers s how elevated levels: Hg-blood median 11.4, max 107.6; Hg-hair median 3.62, max 37.8. The Hg urine concentrations of the occupational exposed and non-e xposed population on Mt.Diwata was significantly higher than in the control group: control median 1.7 mug/l, max 7.6; non-occupational burdened median 4.1, max 76.4; and workers median 11.0, max 294.2. The participants, livin g downstream on the plain of Monkayo show no statistically significant diff erence in Hg-blood, Hg-urine or Hg-hair in comparison with the control grou p. The German Human-Biological-Monitoring value II (HBM II) was exceeded in 19.5% (control), 26.0% (downstream), 19.4% (Mt. Diwata, non-occupational) and 55.4% (workers) of the cases, the German occupational threshold limit i n 19.6% of the workers. Only some of the clinical data, characteristic for Hg intoxication (e.g. tremor, loss of memory, bluish discoloration of the g ingiva, etc.), correlate with Hg in blood or urine, but not with Hg in hair . The medical score sum correlates only with Hg in urine. The poor correlat ion between the Hg concentration in the biomonitors to classic clinical sig ns of chronic Hg intoxication may be explained by several factors: HE in bl ood, urine and hair do not adequately monitor the Hg burden of the target t issues, especially the brain. Inter-individual differences in the sensitive ness to Hg are extremely large. In this area a mixed burden of Hg species m ust be assumed (Hg vapor, inorganic Kg, methyl-Kg). Chronic Hg burden may h ave established damage months or even years before the actual determination of the Hg concentrations in the bio-monitors under quite different burden was performed (Drasch G. Mercury. In: Seller HG, Sigel A, Sigel H, editors. Handbook on metals in clinical and analytical chemistry. New York: Marcel Dekker, 1994:479-494). Therefore, 'Hg intoxication', that should be treated, was not diagnosed by the Hg concentration in the bio-mon itors alone, but by a balanced combination of these Hg values and the medic al score sum. In principle, this means the higher the Hg concentration in t he bio-monitors, the lower the number of characteristic adverse effects are required for a positive diagnosis. By this method, 0% of the controls, 35% downstream, 27% from Mt. Diwata, non-occupational exposed and 71.6% of the workers were classified as Hg intoxicated. A reduction of the external Hg burden on Mt. Diwata is urgently recommended. An attempt to treat the intox icated participants with the chelating agent dimercaptopropanesulfonic acid (DMPS) is planned. (C) 2001 Elsevier Science B.V. All rights reserved.