Ma. Vile et Rk. Wieder, ALKALINITY GENERATION BY FE(III) REDUCTION VERSUS SULFATE REDUCTION IN WETLANDS CONSTRUCTED FOR ACID-MINE DRAINAGE TREATMENT, Water, air and soil pollution, 69(3-4), 1993, pp. 425-441
Despite the widespread use of wetlands for acid mine drainage (AMD) tr
eatment, alkalinity generating mechanisms in wetlands and their abioti
c and biotic controls are poorly understood. While both dissimilatory
sulfate reduction and Fe(III) reduction are alkalinity-generating mech
anisms, only the former has been considered as important in wetlands c
onstructed for AMD treatment. This study was conducted to determine th
e ''tent to which Fe(III) reduction occurs and the extent to which sul
fate reduction versus Fe(III) reduction contributes to alkalinity gene
ration in 5 wetlands constructed with different organic substrates (Sp
hagnum peat with limestone and fertilizer, Sphagnum peat, sawdust, str
aw/manure, mushroom compost) that had been exposed to the same quality
and quantity of AMD for 18-22 months. These substrates had Fe oxyhydr
oxide concentrations of 250-810 mumol Fe g-1 dry substrate. Flasks con
taining 100 g of wet substrate along with either 150 mL of wetland wat
er or 130 mL of wetland water and 20 mL of 37% formalin were incubated
at 4-degrees-C in January and 25-degrees-C in May. On days 0, 2, 4, 8
, 12 and 16, the slurry mixtures were analyzed for concentrations of H
+, Fe2+ and SO42-. The bulk of the evidence indicates that for all exc
ept the mushroom compost wetland, especially at 25-degrees-C, biologic
ally-mediated Fe(II) reduction occurred and generated alkalinity. Howe
ver, in none of the wetlands, regardless of incubation temperature, wa
s there evidence to support net biological sulfate reduction or its at
tendant alkalinity generation. Sulfate reduction and concurrent Fe(III
) oxyhydroxide accumulation may be important in the initial stages of
wetland treatment of AMD, both contributing to effective Fe retention.
However, as Fe(III) oxyhydroxides accumulate over time, Fe(III) reduc
tion could lead not only to decreased Fe retention, but also to the po
tential net release of Fe from the wetland.