ALKALINITY GENERATION BY FE(III) REDUCTION VERSUS SULFATE REDUCTION IN WETLANDS CONSTRUCTED FOR ACID-MINE DRAINAGE TREATMENT

Authors
Citation
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
Citations number
42
Categorie Soggetti
Environmental Sciences","Water Resources
ISSN journal
00496979
Volume
69
Issue
3-4
Year of publication
1993
Pages
425 - 441
Database
ISI
SICI code
0049-6979(1993)69:3-4<425:AGBFRV>2.0.ZU;2-L
Abstract
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.