An estimated 30-50 million people in Bangladesh consume groundwater with ar
senic contents far above accepted limits. A better understanding of arsenic
redox kinetics and simple water treatment procedures are urgently needed.
We have studied thermal and photochemical As(III) oxidation in the laborato
ry, on a time scale of hours, in water containing 500 mug/L As(III), 0.06-5
mg/L Fe(II,III), and 4-6 mM bicarbonate at pH 6.5-8.0. As(V) was measured
colorimetrically, and As(III) and As(tot) were measured by As(III)/As(tot)-
specific hydride-generation AAS. Dissolved oxygen and micromolar hydrogenpe
roxide did not oxidize As(III) on a time scale of hours. As(III) was partly
oxidized in the dark by addition of Fe(II) to aerated water, presumably by
reactive intermediates formed in the reduction of oxygen by Fe(ll). In sol
utions containing 0.06-5 mg/L Fe(II,III), over 90% of As(III) could be oxid
ized photochemically within 2-3 h by illumination with 90 W/m(2) UV-A light
. Citrate, by forming Fe(III) citrate complexes that are photolyzed With hi
gh quantum yields, strongly accelerated As(lll) oxidation. The photoproduct
of citrate (3-oxoglutaric acid) induced rapid flocculation and precipitati
on of Fe(III). in laboratory/tests, 80-90% of total arsenic was removed aft
er addition of 50 muM citrate or 100-200 muL (4-8 drops) of lemon juice/L,
illumination for 2-3 h, and precipitation. The same procedure was able to r
emove 45-78% of total arsenic in first field trials in Bangladesh.