Bench-scale studies were conducted in model freshwater systems to inve
stigate how various parameters affected arsenic removal during coagula
tion with ferric chloride and arsenic adsorption onto preformed hydrou
s ferric oxide. Parameters included arsenic oxidation state and initia
l concentration, coagulant dosage or adsorbent concentration, pH, and
the presence of co-occurring inorganic solutes. Comparison of coagulat
ion and adsorption experiments and of experimental results with predic
tions based on surface complexation modeling demonstrated that adsorpt
ion is an important (though not the sole) mechanism governing arsenic
removal during coagulation. Under comparable conditions, better remova
l was observed with arsenic(V) [As(V)] than with arsenic(III) [As(III)
] in both coagulation and adsorption experiments. Below neutral pH val
ues, As(III) removal-adsorption was significantly decreased in the pre
sence of sulfate, whereas only a slight decrease in As(V) removal-adso
rption was observed. At high pH, removal-adsorption of As(V) was incre
ased in the presence of calcium. Removal of As(V) during coagulation w
ith ferric chloride is both more efficient and less sensitive than tha
t of As(III) to variations in source water composition.