70 research outputs found

    Wetland and Hydric Soils

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    Soil and the inherent biogeochemical processes in wetlands contrast starkly with those in upland forests and rangelands. The differences stem from extended periods of anoxia, or the lack of oxygen in the soil, that characterize wetland soils; in contrast, upland soils are nearly always oxic. As a result, wetland soil biogeochemistry is characterized by anaerobic processes, and wetland vegetation exhibits specific adaptations to grow under these conditions. However, many wetlands may also have periods during the year where the soils are unsaturated and aerated. This fluctuation between aerated and nonaerated soil conditions, along with the specialized vegetation, gives rise to a wide variety of highly valued ecosystem services

    Forested Wetlands of the Southern United States: A Bibliography

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    The term forested wetland covers a variety of forest types including mangroves, cypress/tupelo swamps, bottomland hardwoods, pocosins and Carolina bays, flatwoods, and mountain fens. These forests are dominated by woody species that have morphological features, physiological adaptations, and/or reproductive strategies enabling them to achieve maturity and reproduce in an environment where the soils within the rooting zone may be inundated or saturated for various periods during the growing season. Although alluvial floodplains occur along most streams of the United States, they are most extensive in the Atlantic Coastal Plain, Gulf Coastal Plain, and Mississippi Alluvial Plain. Only about half of the original floodplain forests remained by the 1930s, and conversion to agriculture continued at an accelerated pace during the 1960s and 1970s.The purpose of this bibliography is to provide a detailed listing of references for students and researchers of the varied studies conducted in these forest types

    Short-term nutrient and sediment fluxes following dam removal

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    Sediment and nutrient fluxes resulting from dam removal were investigated with a combination of field and laboratory studies. Impoundment-specific controls (i.e., regional, structural, biological and hydrogeomorphic) on loadings of dissolved organic carbon (DOC), inorganic and organic nitrogen and total suspended solids (TSS) were investigated. In particular, impoundment source areas (channel as well as floodplain wetlands) were compared to determine which represents a greater source of TSS, DOC and TDN to downstream environments. To determine if nutrient-rich sediments released from former impoundments continue to contribute C, N and P to the water column during downstream routing, a series of controlled laboratory experiments were performed. Sediment suspensions - at concentrations similar to those seen during dam removals - were exposed to simulated solar radiation, while DOC, total dissolved nitrogen (TDN), dissolved inorganic nitrogen (DIN) and soluble reactive phosphorus (SRP) and CO2 concentrations were measured before and after exposure. Additionally, the ability of successional plant community to sequester or otherwise immobilize interstitial N and P pools within formerly impounded sediment accumulations exposed by dam removal was investigated. Finally, based on the experience and knowledge gained from this dissertation, a conceptual model of upstream and downstream disturbances resulting from dam removal was constructed. It is hoped that this dissertation will serve the shared interests among basic river researchers, river restoration practitioners, policy makers and aquatic resources regulators

    Element Transport in A River-lake Continuum across Forest-dominated Landscapes: A Case Study in Central Louisiana

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    Studying the biogeochemical connectivity between rivers and lakes can help us understand their ecological and environmental impacts within a drainage basin, which is especially true for forest watersheds that play a vital role in provisioning freshwater services to ecosystems and downstream communities. This dissertation research consists of three interconnected studies with the overarching goal of discerning the connectivity of elements in a river-lake continuum across forest-dominated landscapes. These studies utilized water samples and in situ measurements collected from the Little River-Catahoula Lake continuum in the subtropical Louisiana, USA at monthly intervals during 2015-2016 and 1978-2008 historical water quality, hydrological and meteorological data downloaded from public-access databases to determine whether the forestry best management practices (BMPs) were effective in reducing levels and loads of sediment and nutrients from forest-dominated river headwaters and investigate the transport of dissolved carbon and metals from a river upstream to the outlet of its downstream receiving lake. Results show that forestry BMPs were effective in reducing sediment runoff from the intensively managed forested headwaters but less effective in controlling stream nitrogen concentrations and loading. Phosphorus loading at the basin outlet was significantly increased, which was probably caused by a drastic increase in the application of phosphorus fertilizer after extensive BMPs implementations. The dissolved organic carbon (DOC) pool in the studied watershed was dominantly terrestrially derived, while autochthonous DOC production derived from aquatic phytoplankton during the warm productive period was also important. In contrast, dissolved inorganic carbon (DIC) in the studied river-lake continuum was mainly from carbon-13 isotope (13C) depleted sources such as soil respired CO2 and in situ organic matter, and the combined effect of metabolism and carbon dioxide outgassing controlled the DIC dynamics in the in-network lake. For all metals analyzed in this study, the river functioned as a sink for Al, Ca, Fe, K, Mg, Na, B, Ba, Mn, Sr and Ti due to sedimentation and biological immobilization, while the lake acted as a source for Al, Mg, K and Ti due to their enrichments in the lakebed, a greater weathering intensity at the lake and backwater effects

    Comparison of water quality in coastal plain streams of North Carolina

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    Forest and Rangeland Soils of the United States Under Changing Conditions

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    This open access book synthesizes leading-edge science and management information about forest and rangeland soils of the United States. It offers ways to better understand changing conditions and their impacts on soils, and explores directions that positively affect the future of forest and rangeland soil health. This book outlines soil processes and identifies the research needed to manage forest and rangeland soils in the United States. Chapters give an overview of the state of forest and rangeland soils research in the Nation, including multi-decadal programs (chapter 1), then summarizes various human-caused and natural impacts and their effects on soil carbon, hydrology, biogeochemistry, and biological diversity (chapters 2–5). Other chapters look at the effects of changing conditions on forest soils in wetland and urban settings (chapters 6–7). Impacts include: climate change, severe wildfires, invasive species, pests and diseases, pollution, and land use change. Chapter 8 considers approaches to maintaining or regaining forest and rangeland soil health in the face of these varied impacts. Mapping, monitoring, and data sharing are discussed in chapter 9 as ways to leverage scientific and human resources to address soil health at scales from the landscape to the individual parcel (monitoring networks, data sharing Web sites, and educational soils-centered programs are tabulated in appendix B). Chapter 10 highlights opportunities for deepening our understanding of soils and for sustaining long-term ecosystem health and appendix C summarizes research needs. Nine regional summaries (appendix A) offer a more detailed look at forest and rangeland soils in the United States and its Affiliates

    Savannah River Ecology Laboratory 2005 Annual Technical Progress Report

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    Large River Food Webs: Influence of Nutrients, Turbidity, and Flow, and Implications for Management

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    Humans impact rivers in many ways that modify ecological processes yielding ecosystem services. In order to mitigate anthropogenic impacts, scientists are challenged to understand interactions among physicochemical factors affecting large river food webs. An understanding of socioeconomic factors also is critical for ecosystem management. In this dissertation, I explore spatiotemporal patterns in floodplain river food webs and political barriers to management of environmental flows, an important factor influencing river ecology. In Chapter II, I reviewed the scientific literature to test conceptual models of river food webs and predictions of environmental factors that might produce variation in basal production sources supporting consumer biomass. My review indicates that algae are the predominant production source for large rivers worldwide, but consumers assimilate C3 plants in rivers 1) with high sediment loads and low transparency during high flow pulses, 2) with high dissolved organic matter concentrations, and 3) following periods of high discharge or leaf litter fall that increase the amount of terrestrial material in the particulate organic matter pool. In Chapter III, I descrobe field research conducted to examine relationships among hydrology, nutrient concentrations, turbidity, and algal primary production and biomass in the littoral zone of five rivers in Texas, Peru, and Venezuela differing in physicochemical conditions. I used stable isotope signatures to estimate contributions of algal-versus terrestrial-based production sources to consumers during different hydrologic periods. My research indicates that during flow pulses in floodplain rivers, a decrease in algal biomass and productivity, combined with increased inputs of terrestrial organic matter, can result in increased terrestrial support of metazoan consumers in the aquatic food web. In 2007, Texas Senate Bill 3 directed that environmental flow recommendations be developed for river basins. Despite emphasis on use of the "best available science" to develop environmental flow regimes and "stakeholder involvement" to address needs of all water users, for the first two basins to complete the SB3 process, final environmental flow rules did not mimic a natural flow regime. In Chapter IV, I reviewed this process, concluding that incentives for river authorities to increase compromise with diverse stakeholders should result in more sustainable management of freshwater
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