On the basis of studies of the prevalence of skin cancer among users of As-
rich well water in Taiwan, WHO experts recommended in 1984 a maximum As con
centration of 50 mu g/litre in drinking water. Since that time, a plethora
of non-cancer as well as cancer effects has been observed in several other
populations sustaining a chronic exposure to various As concentrations in d
rinking water. This prompted a revision of the standard and a provisional g
uideline of 10 mu g/litre was recommended in 1993. While the uncertainty li
nked to the statistical inferences leading to the guideline are reduced by
the fact that they are directly estimated from human data and result from e
xtrapolations made relatively close to observed exposure levels, developed
guideline depends strongly on the choice of the dose-response model (linear
, quadratic, hockey-stick) and the accuracy of the exposure data. The poten
tial exposure to As sources other than drinking water, dietary habits and g
enetic characteristics of the populations may also make more difficult the
inference of a recommendation for As concentration in drinking water. Owing
to the huge cost of strongly reducing the current As in water standard, ma
ny efforts are presently made to clarify the quantitative aspects of As-ind
uced cancers, particularly at low dose levels. New data on the metabolism a
nd carcinogenic mechanism of As in humans along with the results of epidemi
ological studies presently under way in several countries will help to redu
ce the uncertainty in the risk assessment of As. (C) 2000 Elsevier Science
Ltd. All rights reserved.