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
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.