Litter decomposition processes were studied in a floodplain forest in South Carolina. Annual decomposition of mixed leaf species decreased from 85 % at the streambank to 58 % in the contiguous upland terrace forest. This decrease in weight loss was correlated with reduced flooding and an increase in more resistant litter substrates at the upland terrace. Species-specific studies indicated that sweet gum leaves decomposed more slowly than red maple, black gum and red ash. Sweet gum leaves had higher initial lignin and cellulose concentrations and larger C:N ratios than the other species. Nutrient release rates from litter varied across the floodplain. Magnesium and K leached quite rapidly within the floodplain, whereas Ca and N losses were more gradual. In contrast, Mg and K losses were less and Ca and N immobilization occurred in the more resistant litter on the unflooded upland terrace. The patterns of nutrient release were generally similar for the four floodplain species tested. Decomposition and recycling processes are different on the floodplain and upland terrace forest. Intrasystem nutrient cycling appears tight in the sandy, nutrientpoor upland terrace forest. Mechanisms such as litter burial during flooding and the timing of nutrient mineralization can limit nutrient export from the floodplain forest. INTRODUCTION Considerable ecological interest has been focused on the mechanisms of material exchange between terrestrial and aquatic habitats (Likens and Bormann, 1974). Alluvial stream-swamps in coastal plain areas represent excellent examples of the magnitude and complexity of potential import-export processes. These systems are characterized by low water velocity, extensive lateral flooding and long water-retention times. Allochthonous inputs from vegetation and fluvial transport often occur over a broad area of floodplain where materials are subject to high metabolic processing (Mulholland, 1981) and possible surface drainage losses during the annual hydroperiod. Recent evidence suggests that coastal plain swamps of the Southeastern U.S. may serve as nutrient traps, effectively removing material added through overland flow from the stream channel (Wharton, 1970; Brinson, 1977; Wharton et al., 1982). The role of overland flooding in the redistribution and long-term retention of radioisotopes in coastal plain streams has been clearly documented (Ragsdale and Shure, 1973). In contrast, Mulholland and Kuenzler (1979) and Mulholland (1981) have reported net fluvial exports of organic carbon from North Carolina swamp-draining watersheds. These studies emphasize the need for further examination of the mechanisms that promote the immobilization or loss of materials in alluvial systems and thus govern downstream export from the overall stream corridor. Organic litter is a major component of material exchange in alluvial habitats. Litter entering the stream-swamp corridor may be displaced downstream (Post and de la Cruz, 1977; Peterson and Rolfe, 1982) or be retained within the floodplain and undergo decomposition in situ. Floodplains in southeastern coastal plain systems retain coarse particulate organic matter effectively, although dissolved carbon losses may be high following metabolic processing and leaching from floodplain litter (Mulholland, 1981). Brinson (1977) indicated nutrient cycling may be tight in coastal plain alluvial swamps. Nutrients accumulate in decomposing litter during the nongrowing season when potential flooding losses would be greatest. The extent and timing of flooding can strongly influence decomposition and nutrient release in these alluvial habitats (Brinson, 1977; Brinson et al., 1981). 'Present address: Environmental Protection Division, Georgia Department of Natural Resources, 270 Washington St. SW, Atlanta 30034. 2Present address: Department of Biology, University of Alabama, University 35486.
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