Laboratory experiments and field tests were conducted to determine the effe
ct of inorganic cations. on effluent from activated-sludge systems. Laborat
ory experiments showed that monovalent cations tend to, increase the concen
tration of solution biological polymers (biopolymers), whereas divalent cat
ions tend to retain the biopolymers in the floe. Biopolymers in solution af
fect effluent chemical oxygen demand (COD). Coagulation tests were performe
d on the effluent with ferric chloride. Ferric hydroxide can coagulate prot
ein through possible adsorptive interactions and may be responsible for som
e biopolymer retention in the floes. In the field study, it was found that
sodium ions in the influent wastewater caused an increase in proteins, and
polysaccharides in solution, thereby increasing the effluent COD concentrat
ion of the treated municipal wastewater. The attachment or release of these
microbially derived organic biopolymers and recalcitrant influent substrat
e may depend on the monovalent-to-divalent cation ratio and the concentrati
on of iron. Modeling of effluent organics in the activated-sludge process,
can be enhanced through incorporation of concepts that take into account th
e partitioning (between floe and solution) of microbial biopolymers and inf
luent recalcitrant substrate.