Abstract

AIM: Massive accumulations of aquatic sedimentary plant are the main source of CH4 and CO2 emissions in floodplain lakes. To examine this connection, this study measured CO2 and CH4 formation during anaerobic decomposition of aquatic macrophytes from a floodplain lake; METHODS: Methane formation was determined to the intrinsic characteristics of the debris, and the experimental (physical and chemical) conditions. Production of CH4 and CO2 were measured during anaerobic degradation of seven aquatic macrophytes: Cabomba furcata, Cyperus giganteus, Egeria najas, Eichhornia azurea, Ludwigia inclinata, Oxycaryum cubense, and Utricularia breviscapa, all of which inhabit the littoral zone of the lagoon studied; RESULTS: Overall, methanogenesis was more sensitive to temperature variation than gross anaerobic mineralization. Although the metabolic routes that generate CO2 were always predominant, as a competing process methanogenesis was favored by increasing temperature to the detriment of CO2 formation. Although several factors (such as pH, redox potential, salinity and nutrients availability) influenced yields of the final degradation products, temperature and detritus chemical composition were, in a first approach, the key factors in CH4 formation. In the oxbow lakes of the Mogi-Guaçu River Floodplain, especially Óleo Lagoon, on average, 10% of the total carbon can be regarded as the yield of CH4 formation derived from aquatic macrophyte decay, while the remaining carbon (90%) became CO2.

Highlights

  • Floodplain wetlands are among the most productive natural environments and are often characterized as having large inputs of detritus (Merritt andLawson, 1992; Neiff et al, 2006)

  • The pathway for CO2 formation in all experiments predominated over methanogenesis; in some cases, methane production was not recorded

  • Most debris produced in littoral regions is composed of aquatic macrophyte detritus, which contributes to sediment diagenesis and biogenic gas emissions

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Summary

Introduction

Floodplain wetlands are among the most productive natural environments and are often characterized as having large inputs of detritus (Merritt andLawson, 1992; Neiff et al, 2006). These systems are driven by hydrologic pulses, produced by oscillations in river water level and lateral overflow that determine floodplain conditions (Powell et al, 2008). Aquatic plant detritus accumulates heavily over sediments and may be the main source of CH4 and CO2 emissions in floodplain lakes. Methanogenesis can be limited by any single link in the chain of reactions that begins with detrital inputs (Megonigal et al, 2004)

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