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Forgrave R, Evenson GR, Golden HE, Christensen JR, Lane CR, Wu Q, D'Amico E, Prenger J. Wetland-mediated nitrate reductions attenuate downstream: Insights from a modeling study. JOURNAL OF ENVIRONMENTAL MANAGEMENT 2024; 370:122500. [PMID: 39299124 DOI: 10.1016/j.jenvman.2024.122500] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Subscribe] [Scholar Register] [Received: 06/28/2024] [Revised: 09/09/2024] [Accepted: 09/12/2024] [Indexed: 09/22/2024]
Abstract
Connections between agricultural runoff and excess nitrogen in the Upper Mississippi River Basin are well-documented, as is the potential role of constructed wetlands in mitigating this surplus nitrogen. However, limited knowledge exists about the "best" placement of these wetlands for downstream nitrogen reductions within a whole watershed context as well as how far downstream these benefits are realized. In this study, we simulate the cumulative impacts of diverse wetland restoration scenarios on downstream nitrate reductions in different subbasins of the Raccoon River Watershed, Iowa, USA, and spatially trace their relative effects downstream. Our simulated results underscore previous work demonstrating that the total area of wetlands and the wetland-catchment-to-wetland area ratio are both significant factors for determining the nitrate load reduction benefits of wetlands at subbasin scales. Simulated wetland conservation scenarios resulted in nitrate load decreases ranging from 7.5 to 43.2% of our baseline model loads. However, we found these wetland-mediated nitrate reduction benefits are quickly attenuated downstream: load reductions were <1% at the watershed outlet across all model scenarios, despite the magnitude of the subbasin-scale nitrate decreases. The relatively rapid attenuation of wetland effects is largely due to downstream nitrate load contributions from untreated subbasins. However, higher subbasin-scale nitrate reductions from wetland-based conservation practices resulted in longer downstream distances prior to attenuation. This study highlights the importance of considering the spatial location of constructed or restored wetlands relative to the area within the watershed where nitrogen reductions are most needed.
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Affiliation(s)
- Rebecca Forgrave
- Oak Ridge Institute for Science and Education (ORISE) Research Participation Program, Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, OH, USA.
| | - Grey R Evenson
- Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, OH, USA
| | - Heather E Golden
- Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, OH, USA
| | - Jay R Christensen
- Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, OH, USA
| | - Charles R Lane
- Office of Research and Development, U.S. Environmental Protection Agency, Athens, GA, USA
| | - Qiusheng Wu
- Department of Geography and Sustainability, The University of Tennessee, Knoxville, TN, USA
| | - Ellen D'Amico
- Pegasus Technical Services, Inc. C/o, Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, OH, USA
| | - Joseph Prenger
- Natural Resources Conservation Service, U.S. Department of Agriculture, Beltsville, MD, USA
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2
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Assani AA. Analysis of the impacts of climate change, physiographic factors and land use/cover on the spatiotemporal variability of seasonal daily mean flows in southern Quebec (Canada). APPLIED WATER SCIENCE 2024; 14:109. [PMID: 38680133 PMCID: PMC11043041 DOI: 10.1007/s13201-024-02180-9] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Figures] [Subscribe] [Scholar Register] [Received: 05/08/2022] [Accepted: 04/03/2024] [Indexed: 05/01/2024]
Abstract
The objective of this study is to compare the spatiotemporal variability of seasonal daily mean flows measured in 17 watersheds, grouped into three homogeneous hydroclimatic regions, during the period 1930-2023 in southern Quebec. With regard to spatial variability, unlike extreme daily flows, seasonal daily mean flows are very poorly correlated with physiographic factors and land use and land cover. In fall, they are not correlated with any physiographic or climatic factor. In winter, they are positively correlated with the rainfall and winter daily mean maximum temperatures. In spring, they are strongly correlated positively with the snowfall but negatively with the spring daily mean maximum temperatures. However, in summer, they are better correlated with forest area and, to a lesser extent, with the rainfall. As for their temporal variability, the application of six different statistical tests revealed a general increase in daily mean flows in winter due to early snowmelt and increased rainfall in fall. In summer, flows decreased significantly in the snowiest hydroclimatic region on the south shore due to the decrease in the snowfall. In spring, no significant change in flows was globally observed in the three hydroclimatic regions despite the decrease in the snowfall due to the increase in the rainfall. In fall, flows increased significantly south of 47°N on both shores due to the increase in the rainfall. This study demonstrates that, unlike extreme flows, the temporal variability of seasonal daily average flows is exclusively influenced by climatic variables in southern Quebec. Due to this influence, seasonal daily mean flows thus appear to be the best indicator for monitoring the impacts of changes in precipitation regimes and seasonal temperatures on river flows in southern Quebec.
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Affiliation(s)
- Ali A. Assani
- Department of Environmental Sciences and the Research Centre for Watershed-Aquatic Ecosystem Interactions (RIVE, UQTR), University of Quebec at Trois-Rivières, 3351 Boulevard des Forges, Trois-Rivières, QC G9A 5H7 Canada
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3
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de Souza Viana LM, Pestana IA, Tostes ECL, Constantino WD, Luze FHR, de Barros Salomão MSM, de Jesus TB, de Carvalho CEV. Understanding seasonal variations in As and Pb river fluxes and their regulatory mechanisms through monitoring data. ENVIRONMENTAL MONITORING AND ASSESSMENT 2024; 196:333. [PMID: 38430282 DOI: 10.1007/s10661-024-12469-6] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 05/23/2023] [Accepted: 02/17/2024] [Indexed: 03/03/2024]
Abstract
The Doce River Basin (DRB) suffers with the adverse impacts of mining activities, due to its high level of urbanization and numerous industrial operations. In this study, we present novel insights into contaminant flow dynamics, seasonal variations, and the primary factors driving concentration levels within the region. We conducted an extensive analysis using a database sourced from the literature, which contained data on the contamination of arsenic (As) and lead (Pb) in the Doce River. Our primary aim was to investigate the patterns of As and Pb flow throughout the entire basin, their response to seasonal fluctuations, and the key parameters influencing their concentration levels. The results showed significant seasonal fluctuations in As and Pb fluxes, peaking during the rainy season. The 2015 Fundão dam breach in the DRB led to notable changes, elevating elemental concentrations, particularly As and Pb, which were subsequently transported to the Atlantic Ocean. These increased concentrations were primarily associated with iron and manganese oxides, hydroxides, and sulfates, rather than precipitation, as evidenced by regressions with low R2 values for both As (R2 = 0.07) and Pb (R2 < 0.001), concerning precipitation. The PCA analysis further supports the connection between these elements and the oxides and hydroxides of Fe and Mn. The approach employed in this study has proven to be highly effective in comprehending biogeochemical phenomena by leveraging data from the literature and could be a model for optimizing resources by capitalizing on existing information to provide valuable insights for drainage basin management, particularly during crises.
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Affiliation(s)
- Luísa Maria de Souza Viana
- Programa de Pós-Graduação em Ecologia e Recursos Naturais, Laboratório de Ciências Ambientais, Centro de Biociências e Biotecnologia, Universidade Estadual do Norte Fluminense Darcy Ribeiro, Av. Alberto Lamego, 2000 - Parque Califórnia - CEP: 28013-602, Campos dos Goytacazes, Rio de Janeiro, Brazil.
| | - Inácio Abreu Pestana
- Programa de Pós-Graduação em Ecologia e Recursos Naturais, Laboratório de Ciências Ambientais, Centro de Biociências e Biotecnologia, Universidade Estadual do Norte Fluminense Darcy Ribeiro, Av. Alberto Lamego, 2000 - Parque Califórnia - CEP: 28013-602, Campos dos Goytacazes, Rio de Janeiro, Brazil
| | - Eloá Corrêa Lessa Tostes
- Programa de Pós-Graduação em Ecologia e Recursos Naturais, Laboratório de Ciências Ambientais, Centro de Biociências e Biotecnologia, Universidade Estadual do Norte Fluminense Darcy Ribeiro, Av. Alberto Lamego, 2000 - Parque Califórnia - CEP: 28013-602, Campos dos Goytacazes, Rio de Janeiro, Brazil
| | - Wendel Dias Constantino
- Programa de Pós-Graduação em Ecologia e Recursos Naturais, Laboratório de Ciências Ambientais, Centro de Biociências e Biotecnologia, Universidade Estadual do Norte Fluminense Darcy Ribeiro, Av. Alberto Lamego, 2000 - Parque Califórnia - CEP: 28013-602, Campos dos Goytacazes, Rio de Janeiro, Brazil
| | - Felipe Henrique Rossi Luze
- Programa de Pós-Graduação em Ecologia e Recursos Naturais, Laboratório de Ciências Ambientais, Centro de Biociências e Biotecnologia, Universidade Estadual do Norte Fluminense Darcy Ribeiro, Av. Alberto Lamego, 2000 - Parque Califórnia - CEP: 28013-602, Campos dos Goytacazes, Rio de Janeiro, Brazil
| | - Marcos Sarmet Moreira de Barros Salomão
- Programa de Pós-Graduação em Ecologia e Recursos Naturais, Laboratório de Ciências Ambientais, Centro de Biociências e Biotecnologia, Universidade Estadual do Norte Fluminense Darcy Ribeiro, Av. Alberto Lamego, 2000 - Parque Califórnia - CEP: 28013-602, Campos dos Goytacazes, Rio de Janeiro, Brazil
| | - Taíse Bomfim de Jesus
- Departamento de Ciências Exatas, Universidade Estadual de Feira de Santana, Feira de Santana, Bahia, Brazil
| | - Carlos Eduardo Veiga de Carvalho
- Programa de Pós-Graduação em Ecologia e Recursos Naturais, Laboratório de Ciências Ambientais, Centro de Biociências e Biotecnologia, Universidade Estadual do Norte Fluminense Darcy Ribeiro, Av. Alberto Lamego, 2000 - Parque Califórnia - CEP: 28013-602, Campos dos Goytacazes, Rio de Janeiro, Brazil
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Ehnvall B, Ågren AM, Nilsson MB, Ratcliffe JL, Noumonvi KD, Peichl M, Lidberg W, Giesler R, Mörth CM, Öquist MG. Catchment characteristics control boreal mire nutrient regime and vegetation patterns over ~5000 years of landscape development. THE SCIENCE OF THE TOTAL ENVIRONMENT 2023; 895:165132. [PMID: 37379918 DOI: 10.1016/j.scitotenv.2023.165132] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 04/18/2023] [Revised: 06/21/2023] [Accepted: 06/23/2023] [Indexed: 06/30/2023]
Abstract
Vegetation holds the key to many properties that make natural mires unique, such as surface microtopography, high biodiversity values, effective carbon sequestration and regulation of water and nutrient fluxes across the landscape. Despite this, landscape controls behind mire vegetation patterns have previously been poorly described at large spatial scales, which limits the understanding of basic drivers underpinning mire ecosystem services. We studied catchment controls on mire nutrient regimes and vegetation patterns using a geographically constrained natural mire chronosequence along the isostatically rising coastline in Northern Sweden. By comparing mires of different ages, we can partition vegetation patterns caused by long-term mire succession (<5000 years) and present-day vegetation responses to catchment eco-hydrological settings. We used the remote sensing based normalized difference vegetation index (NDVI) to describe mire vegetation and combined peat physicochemical measures with catchment properties to identify the most important factors that determine mire NDVI. We found strong evidence that mire NDVI depends on nutrient inputs from the catchment area or underlying mineral soil, especially concerning phosphorus and potassium concentrations. Steep mire and catchment slopes, dry conditions and large catchment areas relative to mire areas were associated with higher NDVI. We also found long-term successional patterns, with lower NDVI in older mires. Importantly, the NDVI should be used to describe mire vegetation patterns in open mires if the focus is on surface vegetation, since the canopy cover in tree-covered mires completely dominated the NDVI signal. With our study approach, we can quantitatively describe the connection between landscape properties and mire nutrient regime. Our results confirm that mire vegetation responds to the upslope catchment area, but importantly, also suggest that mire and catchment aging can override the role of catchment influence. This effect was clear across mires of all ages, but was strongest in younger mires.
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Affiliation(s)
- Betty Ehnvall
- Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, Skogsmarksgränd 17, 90183 Umeå, Sweden.
| | - Anneli M Ågren
- Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, Skogsmarksgränd 17, 90183 Umeå, Sweden
| | - Mats B Nilsson
- Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, Skogsmarksgränd 17, 90183 Umeå, Sweden
| | - Joshua L Ratcliffe
- Unit for Field-Based Forest Research, Swedish University of Agricultural Sciences, 922 91 Vindeln, Sweden
| | - Koffi Dodji Noumonvi
- Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, Skogsmarksgränd 17, 90183 Umeå, Sweden
| | - Matthias Peichl
- Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, Skogsmarksgränd 17, 90183 Umeå, Sweden
| | - William Lidberg
- Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, Skogsmarksgränd 17, 90183 Umeå, Sweden
| | - Reiner Giesler
- Climate Impacts Research Centre Umeå, Sweden, Department of Ecology and Environmental Sciences, Umeå University, 90736 Umeå, Sweden
| | - Carl-Magnus Mörth
- Department of Geological Sciences, Stockholm University, Svante Arrheniusväg 8, 10691 Stockholm, Sweden
| | - Mats G Öquist
- Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, Skogsmarksgränd 17, 90183 Umeå, Sweden
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5
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Lee S, Lee B, Lee J, Song J, McCarty GW. Detecting causal relationship of non-floodplain wetland hydrologic connectivity using convergent cross mapping. Sci Rep 2023; 13:17220. [PMID: 37821495 PMCID: PMC10567775 DOI: 10.1038/s41598-023-44071-0] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 03/03/2023] [Accepted: 10/03/2023] [Indexed: 10/13/2023] Open
Abstract
The hydrologic connectivity of non-floodplain wetlands (NFWs) with downstream water (DW) has gained increased importance, but connectivity via groundwater (GW) is largely unknown owing to the high complexity of hydrological processes and climatic seasonality. In this study, a causal inference method, convergent cross mapping (CCM), was applied to detect the hydrologic causality between upland NFW and DW through GW. CCM is a nonlinear inference method for detecting causal relationships among environmental variables with weak or moderate coupling in nonlinear dynamical systems. We assumed that causation would exist when the following conditions were observed: (1) the presence of two direct causal (NFW → GW and GW → DW) and one indirect causal (NFW → DW) relationship; (2) a nonexistent opposite causal relationship (DW → NFW); (3) the two direct causations with shorter lag times relative to indirect causation; and (4) similar patterns not observed with pseudo DW. The water levels monitored by a well and piezometer represented NFW and GW measurements, respectively, and the DW was indicated by the baseflow at the outlet of the drainage area, including NFW. To elucidate causality, the DW taken at the adjacent drainage area with similar climatic seasonality was also tested as pseudo DW. The CCM results showed that the water flow from NFW to GW and then DW was only present, and any opposite flows did not exist. In addition, direct causations had shorter lag time than indirect causation, and 3-day lag time was shown between NFW and DW. Interestingly, the results with pseudo DW did not show any lagged interactions, indicating non-causation. These results provide the signals for the hydrologic connectivity of NFW and DW with GW. Therefore, this study would support the importance of NFW protection and management.
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Affiliation(s)
- Sangchul Lee
- Department of Environmental Engineering, University of Seoul, Dongdaemun-gu, Seoul, 02504, Republic of Korea.
| | - Byeongwon Lee
- Department of Environmental Engineering, University of Seoul, Dongdaemun-gu, Seoul, 02504, Republic of Korea
| | - Junga Lee
- Division of Environmental Science & Ecological Engineering, College of Life Sciences & Biotechnology, Korea University, Seoul, 02841, Republic of Korea
| | - Jihoon Song
- Ojeong Resilience Institute, Korea University, Seoul, 02841, Republic of Korea
| | - Gregory W McCarty
- USDA-ARS, Hydrology and Remote Sensing Laboratory, Beltsville, MD, 20705, USA.
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6
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Lane CR, D’Amico E, Christensen JR, Golden HE, Wu Q, Rajib A. Mapping global non-floodplain wetlands. EARTH SYSTEM SCIENCE DATA 2023; 15:2927-2955. [PMID: 37841644 PMCID: PMC10569017 DOI: 10.5194/essd-15-2927-2023] [Citation(s) in RCA: 1] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [Abstract] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 10/17/2023]
Abstract
Non-floodplain wetlands - those located outside the floodplains - have emerged as integral components to watershed resilience, contributing hydrologic and biogeochemical functions affecting watershed-scale flooding extent, drought magnitude, and water-quality maintenance. However, the absence of a global dataset of non-floodplain wetlands limits their necessary incorporation into water quality and quantity management decisions and affects wetland-focused wildlife habitat conservation outcomes. We addressed this critical need by developing a publicly available "Global NFW" (Non-Floodplain Wetland) dataset, comprised of a global river-floodplain map at 90 m resolution coupled with a global ensemble wetland map incorporating multiple wetland-focused data layers. The floodplain, wetland, and non-floodplain wetland spatial data developed here were successfully validated within 21 large and heterogenous basins across the conterminous United States. We identified nearly 33 million potential non-floodplain wetlands with an estimated global extent of over 16×106 km2. Non-floodplain wetland pixels comprised 53% of globally identified wetland pixels, meaning the majority of the globe's wetlands likely occur external to river floodplains and coastal habitats. The identified global NFWs were typically small (median 0.039 km2), with a global median size ranging from 0.018-0.138 km2. This novel geospatial Global NFW static dataset advances wetland conservation and resource-management goals while providing a foundation for global non-floodplain wetland functional assessments, facilitating non-floodplain wetland inclusion in hydrological, biogeochemical, and biological model development. The data are freely available through the United States Environmental Protection Agency's Environmental Dataset Gateway (https://gaftp.epa.gov/EPADataCommons/ORD/Global_NonFloodplain_Wetlands/, last access: 24 May 2023) and through https://doi.org/10.23719/1528331 (Lane et al., 2023a).
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Affiliation(s)
- Charles R. Lane
- U.S. Environmental Protection Agency, Office of Research and Development, Center for Environmental Measurement and Modeling, Athens, Georgia, USA
| | - Ellen D’Amico
- Pegasus Technical Service, Inc. c/o U.S. Environmental Protection Agency, Office of Research and Development, Cincinnati, Ohio, USA
| | - Jay R. Christensen
- U.S. Environmental Protection Agency, Office of Research and Development, Center for Environmental Measurement and Modeling, Cincinnati, Ohio, USA
| | - Heather E. Golden
- U.S. Environmental Protection Agency, Office of Research and Development, Center for Environmental Measurement and Modeling, Cincinnati, Ohio, USA
| | - Qiusheng Wu
- Department of Geography & Sustainability, University of Tennessee, Knoxville, Tennessee, USA
| | - Adnan Rajib
- Hydrology and Hydroinformatics Innovation Lab, Department of Civil Engineering, University of Texas at Arlington, Arlington, Texas, USA
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7
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Balerna JA, Kramer AM, Landry SM, Rains MC, Lewis DB. Synergistic effects of precipitation and groundwater extraction on freshwater wetland inundation. JOURNAL OF ENVIRONMENTAL MANAGEMENT 2023; 337:117690. [PMID: 36933535 DOI: 10.1016/j.jenvman.2023.117690] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 11/10/2022] [Revised: 02/10/2023] [Accepted: 03/06/2023] [Indexed: 06/18/2023]
Abstract
Wetlands provide essential ecosystem services, including nutrient cycling, flood protection, and biodiversity support, that are sensitive to changes in wetland hydrology. Wetland hydrological inputs come from precipitation, groundwater discharge, and surface run-off. Changes to these inputs via climate variation, groundwater extraction, and land development may alter the timing and magnitude of wetland inundation. Here, we use a long-term (14-year) comparative study of 152 depressional wetlands in west-central Florida to identify sources of variation in wetland inundation during two key time periods, 2005-2009 and 2010-2018. These time periods are separated by the enactment of water conservation policies in 2009, which included regional reductions in groundwater extraction. We investigated the response of wetland inundation to the interactive effects of precipitation, groundwater extraction, surrounding land development, basin geomorphology, and wetland vegetation class. Results show that water levels were lower and hydroperiods were shorter in wetlands of all vegetation classes during the first (2005-2009) time period, which corresponded with low rainfall conditions and high rates of groundwater extraction. Under water conservation policies enacted in the second (2010-2018) time period, median wetland water depths increased 1.35 m and median hydroperiods increased from 46 % to 83 %. Water-level variation was additionally less sensitive to groundwater extraction. The increase in inundation differed among vegetation classes with some wetlands not displaying signs of hydrological recovery. After accounting for effects of several explanatory factors, inundation still varied considerably among wetlands, suggesting a diversity of hydrological regimes, and thus ecological function, among individual wetlands across the landscape. Policies seeking to balance human water demand with the preservation of depressional wetlands would benefit by recognizing the heightened sensitivity of wetland inundation to groundwater extraction during periods of low precipitation.
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Affiliation(s)
- Jessica A Balerna
- Department of Integrative Biology, University of South Florida, 4202 E Fowler Ave, Tampa, FL, 33620, USA.
| | - Andrew M Kramer
- Department of Integrative Biology, University of South Florida, 4202 E Fowler Ave, Tampa, FL, 33620, USA
| | - Shawn M Landry
- School of Geosciences, University of South Florida, 4202 E Fowler Ave, Tampa, FL, 33620, USA
| | - Mark C Rains
- School of Geosciences, University of South Florida, 4202 E Fowler Ave, Tampa, FL, 33620, USA
| | - David B Lewis
- Department of Integrative Biology, University of South Florida, 4202 E Fowler Ave, Tampa, FL, 33620, USA
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8
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Ghosh R, Pal S. Delineation of vegetation shaded ox-bow lakes in Ganges flood plain, India. ECOL INFORM 2023. [DOI: 10.1016/j.ecoinf.2022.101954] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 12/23/2022]
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9
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Leibowitz SG, Hill RA, Creed IF, Compton JE, Golden HE, Weber MH, Rains MC, Jones CE, Lee EH, Christensen JR, Bellmore RA, Lane CR. National hydrologic connectivity classification links wetlands with stream water quality. NATURE WATER 2023; 1:370-380. [PMID: 37389401 PMCID: PMC10302404 DOI: 10.1038/s44221-023-00057-w] [Citation(s) in RCA: 5] [Impact Index Per Article: 5.0] [Reference Citation Analysis] [Abstract] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/29/2022] [Accepted: 02/27/2023] [Indexed: 07/01/2023]
Abstract
Wetland hydrologic connections to downstream waters influence stream water quality. However, no systematic approach for characterizing this connectivity exists. Here using physical principles, we categorized conterminous US freshwater wetlands into four hydrologic connectivity classes based on stream contact and flowpath depth to the nearest stream: riparian, non-riparian shallow, non-riparian mid-depth and non-riparian deep. These classes were heterogeneously distributed over the conterminous United States; for example, riparian dominated the south-eastern and Gulf coasts, while non-riparian deep dominated the Upper Midwest and High Plains. Analysis of a national stream dataset indicated acidification and organic matter brownification increased with connectivity. Eutrophication and sedimentation decreased with wetland area but did not respond to connectivity. This classification advances our mechanistic understanding of wetland influences on water quality nationally and could be applied globally.
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Affiliation(s)
- Scott G. Leibowitz
- US Environmental Protection Agency (EPA), Center for Public Health and Environmental Assessment (CPHEA), Pacific Ecological Systems Division (PESD), Corvallis, OR, USA
| | - Ryan A. Hill
- US Environmental Protection Agency (EPA), Center for Public Health and Environmental Assessment (CPHEA), Pacific Ecological Systems Division (PESD), Corvallis, OR, USA
| | - Irena F. Creed
- Department of Physical and Environmental Science, University of Toronto, Toronto, Ontario, Canada
| | - Jana E. Compton
- US Environmental Protection Agency (EPA), Center for Public Health and Environmental Assessment (CPHEA), Pacific Ecological Systems Division (PESD), Corvallis, OR, USA
| | - Heather E. Golden
- US EPA, Center for Environmental Measurement and Modeling (CEMM), Watershed and Ecosystem Characterization Division, Cincinnati, OH, USA
| | - Marc H. Weber
- US Environmental Protection Agency (EPA), Center for Public Health and Environmental Assessment (CPHEA), Pacific Ecological Systems Division (PESD), Corvallis, OR, USA
| | - Mark C. Rains
- School of Geosciences, University of South Florida, Tampa, FL, USA
| | - Chas E. Jones
- ORISE Post-doctoral Participant, c/o US EPA, CPHEA, PESD, Corvallis, OR, USA
- Present address: Affiliated Tribes of Northwest Indians, Portland, OR, USA
| | - E. Henry Lee
- US Environmental Protection Agency (EPA), Center for Public Health and Environmental Assessment (CPHEA), Pacific Ecological Systems Division (PESD), Corvallis, OR, USA
| | - Jay R. Christensen
- US EPA, Center for Environmental Measurement and Modeling (CEMM), Watershed and Ecosystem Characterization Division, Cincinnati, OH, USA
| | - Rebecca A. Bellmore
- National Research Council, c/o US EPA, CPHEA, PESD, Corvallis, OR, USA
- Present address: Southeast Alaska Watershed Coalition, Juneau, AK, USA
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10
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Beyene MT, Leibowitz SG, Dunn CJ, Bladon KD. To burn or not to burn: An empirical assessment of the impacts of wildfires and prescribed fires on trace element concentrations in Western US streams. THE SCIENCE OF THE TOTAL ENVIRONMENT 2023; 863:160731. [PMID: 36502971 PMCID: PMC9988007 DOI: 10.1016/j.scitotenv.2022.160731] [Citation(s) in RCA: 2] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 07/23/2022] [Revised: 11/12/2022] [Accepted: 12/02/2022] [Indexed: 05/23/2023]
Abstract
The use of low-severity prescribed fires has been increasingly promoted to reduce the impacts from high-severity wildfires and maintain ecosystem resilience. However, the effects of prescribed fires on water quality have rarely been evaluated relative to the effects of wildfires. In this study, we assessed the effects of 54 wildfires and 11 prescribed fires on trace element (arsenic, selenium, and cadmium) concentrations of streams draining burned watersheds in the western US. To obtain results independent of the choice of method, we employed three independent analytical approaches to evaluate fire effects on water quality for the first three post-fire years. In general, we observed significant increases in trace element concentrations in streams burned by large, high-severity wildfires, despite substantial variability across sites. Comparatively, we did not observe increases in the spring mean concentration of arsenic, selenium, and cadmium in watersheds burned by prescribed fires. Our analysis indicated that the post-fire trace element response in streams was primarily influenced by burn area, burn severity, post-fire weather, surface lithology, watershed physiography, and land cover. This study's results demonstrate that prescribed burns could lessen the post-fire trace element loads in downstream waters if prescribed fires reduce subsequent high severity fires in the landscape.
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Affiliation(s)
- Mussie T Beyene
- Oak Ridge Institute for Science and Education (ORISE) Post-doc, c/o U.S. Environmental Protection Agency, Corvallis, OR 97330, USA.
| | - Scott G Leibowitz
- U.S. Environmental Protection Agency, Center for Public Health and Environmental Assessment, Corvallis, OR 97330, USA.
| | - Christopher J Dunn
- Oregon State University, Department of Forest Engineering, Resources, and Management, Corvallis, OR 97330, USA.
| | - Kevin D Bladon
- Oregon State University, Department of Forest Engineering, Resources, and Management, Corvallis, OR 97330, USA.
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11
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Liu L, Dobson B, Mijic A. Optimisation of urban-rural nature-based solutions for integrated catchment water management. JOURNAL OF ENVIRONMENTAL MANAGEMENT 2023; 329:117045. [PMID: 36549055 DOI: 10.1016/j.jenvman.2022.117045] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 09/17/2022] [Revised: 11/22/2022] [Accepted: 12/13/2022] [Indexed: 06/17/2023]
Abstract
Nature-based solutions (NBS) have co-benefits for water availability, water quality, and flood management. However, searching for optimal integrated urban-rural NBS planning to maximise co-benefits at a catchment scale is still limited by fragmented evaluation. This study develops an integrated urban-rural NBS planning optimisation framework based on the CatchWat-SD model, which is developed to simulate a multi-catchment integrated water cycle in the Norfolk region, UK. Three rural (runoff attenuation features, regenerative farming, floodplain) and two urban (urban green space, constructed wastewater wetlands) NBS interventions are integrated into the model at a range of implementation scales. A many-objective optimisation problem with seven water management objectives to account for flow, quality and cost indicators is formulated, and the NSGAII algorithm is adopted to search for optimal NBS portfolios. Results show that rural NBS have more significant impacts across the catchment, which increase with the scale of implementation. Integrated urban-rural NBS planning can improve water availability, water quality, and flood management simultaneously, though trade-offs exist between different objectives. Runoff attenuation features and floodplains provide the greatest benefits for water availability. Regenerative farming is most effective for water quality and flood management, though it decreases water availability by up to 15% because it retains more water in the soil. Phosphorus levels are best reduced by expansion of urban green space to decrease loading on combined sewer systems, though this trades off against water availability, flood, nitrogen and suspended solids. The proposed framework enables spatial prioritisation of NBS, which may ultimately guide multi-stakeholder decision-making, bridging the urban-rural divide in catchment water management.
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Affiliation(s)
- Leyang Liu
- Department of Civil and Environmental Engineering, Imperial College London, London, United Kingdom.
| | - Barnaby Dobson
- Department of Civil and Environmental Engineering, Imperial College London, London, United Kingdom
| | - Ana Mijic
- Department of Civil and Environmental Engineering, Imperial College London, London, United Kingdom
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12
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Norman LM, Lal R, Wohl E, Fairfax E, Gellis AC, Pollock MM. Natural infrastructure in dryland streams (NIDS) can establish regenerative wetland sinks that reverse desertification and strengthen climate resilience. THE SCIENCE OF THE TOTAL ENVIRONMENT 2022; 849:157738. [PMID: 35932871 DOI: 10.1016/j.scitotenv.2022.157738] [Citation(s) in RCA: 5] [Impact Index Per Article: 2.5] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 02/28/2022] [Revised: 07/15/2022] [Accepted: 07/27/2022] [Indexed: 06/15/2023]
Abstract
In this article we describe the natural hydrogeomorphological and biogeochemical cycles of dryland fluvial ecosystems that make them unique, yet vulnerable to land use activities and climate change. We introduce Natural Infrastructure in Dryland Streams (NIDS), which are structures naturally or anthropogenically created from earth, wood, debris, or rock that can restore implicit function of these systems. This manuscript further discusses the capability of and functional similarities between beaver dams and anthropogenic NIDS, documented by decades of scientific study. In addition, we present the novel, evidence-based finding that NIDS can create wetlands in water-scarce riparian zones, with soil organic carbon stock as much as 200 to 1400 Mg C/ha in the top meter of soil. We identify the key restorative action of NIDS, which is to slow the drainage of water from the landscape such that more of it can infiltrate and be used to facilitate natural physical, chemical, and biological processes in fluvial environments. Specifically, we assert that the rapid drainage of water from such environments can be reversed through the restoration of natural infrastructure that once existed. We then explore how NIDS can be used to restore the natural biogeochemical feedback loops in these systems. We provide examples of how NIDS have been used to restore such feedback loops, the lessons learned from installation of NIDS in the dryland streams of the southwestern United States, how such efforts might be scaled up, and what the implications are for mitigating climate change effects. Our synthesis portrays how restoration using NIDS can support adaptation to and protection from climate-related disturbances and stressors such as drought, water shortages, flooding, heatwaves, dust storms, wildfire, biodiversity losses, and food insecurity.
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Affiliation(s)
- Laura M Norman
- U.S. Geological Survey, Western Geographic Science Center, Tucson, AZ 85719, USA.
| | - Rattan Lal
- Ohio State University, CFAES Rattan Lal Center for Carbon Management and Sequestration, Columbus, OH 43210, USA
| | - Ellen Wohl
- Colorado State University, Department of Geosciences, Warner College of Natural Resources, Ft Collins, CO 80523, USA
| | - Emily Fairfax
- California State University Channel Islands, Department of Environmental Science and Research Management, Camarillo, CA 93012, USA
| | - Allen C Gellis
- U.S. Geological Survey, Maryland-Delaware-D.C. Water Science Center, Baltimore, MD 21228, USA
| | - Michael M Pollock
- NOAA Fisheries-Northwest Fisheries Science Center, Watershed Program, Seattle, WA 98112, USA
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Lv C, Liao H, Ling M, Wu Z, Yan D. Assessment of eco-economic effects of urban water system connectivity project. ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH INTERNATIONAL 2022; 29:53353-53363. [PMID: 35288849 DOI: 10.1007/s11356-022-19552-w] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 11/15/2021] [Accepted: 02/28/2022] [Indexed: 06/14/2023]
Abstract
As one of the large ecological infrastructures, the urban water system connectivity (UWSC) project is an important part of urban ecosystem construction. It is helpful for the scientific planning and construction of the project to systematically evaluate the effects. However, due to the complex and various effects of UWSC project, there is no complete effect system and quantitative method. Against this backdrop, the composition and mechanism of positive and negative effects of ecological economics of UWSC project were deeply analyzed to improve the composition system of eco-economic effects in this study. At the same time, the emergy theory was used to put forward the quantification method of eco-economic effect system. Taking the UWSC project in Xuchang as an example, its ecological, social, and economic effects were evaluated. The result showed that the average eco-economic effect of the project is 49.97 million dollars/year. Economic effect and ecological effect are significant, accounting for 82.49% and 15.89% of total effect, respectively. This study can provide reference for comprehensive and unified assessment of eco-economic effects of UWSC project.
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Affiliation(s)
- Cuimei Lv
- School of Water Conservancy Engineering, Zhengzhou University, Zhengzhou, Henan, 450001, People's Republic of China
| | - Huali Liao
- School of Water Conservancy Engineering, Zhengzhou University, Zhengzhou, Henan, 450001, People's Republic of China
| | - Minhua Ling
- School of Water Conservancy Engineering, Zhengzhou University, Zhengzhou, Henan, 450001, People's Republic of China.
| | - Zening Wu
- School of Water Conservancy Engineering, Zhengzhou University, Zhengzhou, Henan, 450001, People's Republic of China
| | - Denghua Yan
- Water Resources Department, China Institute of Water Resources and Hydropower Research, Beijing, 100038, People's Republic of China
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14
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Variability of Mean Annual Flows in Southern Quebec (Canada). WATER 2022. [DOI: 10.3390/w14091370] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 11/16/2022]
Abstract
Snow is the main source of streamflow in temperate regions characterized by very cold and snowy winters. Due to global warming, these regions are experiencing a significant decrease in snowfall. The main objective of this study is to analyze the impacts of snowfall on the spatio-temporal variability of mean annual flows (MAFs) of 17 rivers, grouped into three hydroclimatic regions, from 1930 to 2019 in southern Quebec. In terms of spatial variability, snowfall is the variable most correlated with MAFs (positive correlation), followed by drainage density (positive correlation) and wetland surface areas (negative correlation). Due to the influence of these three factors, MAF values are generally higher in the most agricultural watersheds of the southeastern hydroclimatic region on the south shore than in the less agricultural watersheds of the southwestern hydroclimatic region on the north shore of the St. Lawrence River. As for temporal variability, the four statistical tests applied to the hydrological series detect no significant downward trend in MAFs, despite having reduced snowfall. Instead, they suggest an evolution toward an increase in mean annual flows, as a result of increased rainfall due to the increase in temperature. This evolution is more pronounced on the north shore than on the south shore, likely due to the presence of wetlands and others water bodies, whose runoff water storage capacity does not change over time to be able to store the surplus of the quantity of water brought by the increase in rain.
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Park J, Kumar M, Lane CR, Basu NB. Seasonality of inundation in geographically isolated wetlands across the United States. ENVIRONMENTAL RESEARCH LETTERS : ERL [WEB SITE] 2022; 17:1-54005. [PMID: 35662858 PMCID: PMC9161429 DOI: 10.1088/1748-9326/ac6149] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.5] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/31/2023]
Abstract
Inundation area is a major control on the ecosystem services provisioned by geographically isolated wetlands. Despite its importance, there has not been any comprehensive study to map out the seasonal inundation characteristics of geographically isolated wetlands over the continental United States (CONUS). This study fills the aforementioned gap by evaluating the seasonality or the long-term intra-annual variations of wetland inundation in ten wetlandscapes across the CONUS. We also assess the consistency of these intra-annual variations. Finally, we evaluate the extent to which the seasonality can be explained based on widely available hydrologic fluxes. Our findings highlight significant intra-annual variations of inundation within most wetlandscapes, with a standard deviation of the long-term averaged monthly inundation area ranging from 15% to 151% of its mean across the wetlandscapes. Stark differences in inundation seasonality are observed between snow-affected vs. rain-fed wetlandscapes. The former usually shows the maximum monthly inundation in April following spring snowmelt (SM), while the latter experiences the maximum in February. Although the magnitude of inundation fraction has changed over time in several wetlandscapes, the seasonality of these wetlands shows remarkable constancy. Overall, commonly available regional hydrologic fluxes (e.g. rainfall, SM, and evapotranspiration) are found to be able to explain the inundation seasonality at wetlandscape scale with determination coefficients greater than 0.57 in 7 out of 10 wetlandscapes. Our methodology and presented results may be used to map inundation seasonality and consequently account for its impact on wetland functions.
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Affiliation(s)
- Junehyeong Park
- Department of Civil, Construction and Environmental Engineering, University of Alabama, Tuscaloosa, AL, United States of America
| | - Mukesh Kumar
- Department of Civil, Construction and Environmental Engineering, University of Alabama, Tuscaloosa, AL, United States of America
| | - Charles R Lane
- US Environmental Protection Agency, Office of Research and Development, Cincinnati, OH, United States of America
| | - Nandita B Basu
- Department of Civil and Environmental Engineering, University of Waterloo, Waterloo, ON, Canada
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Abstract
AbstractWatershed resilience is the ability of a watershed to maintain its characteristic system state while concurrently resisting, adapting to, and reorganizing after hydrological (for example, drought, flooding) or biogeochemical (for example, excessive nutrient) disturbances. Vulnerable waters include non-floodplain wetlands and headwater streams, abundant watershed components representing the most distal extent of the freshwater aquatic network. Vulnerable waters are hydrologically dynamic and biogeochemically reactive aquatic systems, storing, processing, and releasing water and entrained (that is, dissolved and particulate) materials along expanding and contracting aquatic networks. The hydrological and biogeochemical functions emerging from these processes affect the magnitude, frequency, timing, duration, storage, and rate of change of material and energy fluxes among watershed components and to downstream waters, thereby maintaining watershed states and imparting watershed resilience. We present here a conceptual framework for understanding how vulnerable waters confer watershed resilience. We demonstrate how individual and cumulative vulnerable-water modifications (for example, reduced extent, altered connectivity) affect watershed-scale hydrological and biogeochemical disturbance response and recovery, which decreases watershed resilience and can trigger transitions across thresholds to alternative watershed states (for example, states conducive to increased flood frequency or nutrient concentrations). We subsequently describe how resilient watersheds require spatial heterogeneity and temporal variability in hydrological and biogeochemical interactions between terrestrial systems and down-gradient waters, which necessitates attention to the conservation and restoration of vulnerable waters and their downstream connectivity gradients. To conclude, we provide actionable principles for resilient watersheds and articulate research needs to further watershed resilience science and vulnerable-water management.
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Cai Y, Liang J, Zhang P, Wang Q, Wu Y, Ding Y, Wang H, Fu C, Sun J. Review on strategies of close-to-natural wetland restoration and a brief case plan for a typical wetland in northern China. CHEMOSPHERE 2021; 285:131534. [PMID: 34329151 DOI: 10.1016/j.chemosphere.2021.131534] [Citation(s) in RCA: 21] [Impact Index Per Article: 7.0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 04/25/2021] [Revised: 07/03/2021] [Accepted: 07/09/2021] [Indexed: 06/13/2023]
Abstract
Wetlands play an important role in sustaining ecosystems on the earth, which regulate water resources, adjust local climate and produce food for human beings, etc. However, wetlands are facing huge challenges due to human activities and other natural evolution, such as area shrinkage, function weakening and biodiversity decrease, and so on, therefore, some wetlands need to be urgently restored. In this study, the main technology components of close-to-natural restoration of wetlands were summarized. The ecological water requirement and water resource allocation can be optimized for the water balance between social, economy and ecology, which is a key prerequisite for maintaining wetland ecosystem. The pollution of wetland sediments and soils can be assessed by various indicators to provide the scientific basis for natural restoration of wetland base, and suitable strategies should be taken according to the actual conditions of wetland bases. The hydrological connectivity in wetlands and with related water system can be numerically simulated to make the optimal plan for improvement of hydrological connectivity. The ecological restoration of wetlands with the synergetic function of plants, animals and microorganisms was summarized, to improve the quality of wetland water environment and maintain the ecosystem stability. Based on the wetland close-to-natural restoration strategies, a brief ecological restoration plan for a typical wetland, Zaozhadian Wetland, near Xiong'an New Area in the north China was proposed from water resource guarantee, base pollution management, hydrological connectivity improvement and biological restoration. The close-to-natural restoration shows more effective, sustainable and long-lasting and thus a practical prospect.
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Affiliation(s)
- Yajing Cai
- College of Environmental Science and Engineering, Beijing Forestry University, Beijing, 100083, China
| | - Jinsong Liang
- College of Environmental Science and Engineering, Beijing Forestry University, Beijing, 100083, China
| | - Panyue Zhang
- College of Environmental Science and Engineering, Beijing Forestry University, Beijing, 100083, China; School of Environmental Chemical Engineering, Chongqing Three Gorges University, Chongqing, 404632, China.
| | - Qingyan Wang
- College of Environmental Science and Engineering, Beijing Forestry University, Beijing, 100083, China
| | - Yan Wu
- School of Environmental Chemical Engineering, Chongqing Three Gorges University, Chongqing, 404632, China
| | - Yiran Ding
- College of Environmental Science and Engineering, Beijing Forestry University, Beijing, 100083, China
| | - Hongjie Wang
- Xiong'an Institute of Eco-Environment, Hebei University, Baoding, 071002, China
| | - Chuan Fu
- School of Environmental Chemical Engineering, Chongqing Three Gorges University, Chongqing, 404632, China
| | - Jiajun Sun
- Beijing Engineering Research Center of Process Pollution Control, Institute of Process Engineering, Chinese Academy of Sciences, Beijing, 100190, China; University of Chinese Academy of Sciences, Beijing, 100049, China
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18
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Abstract
Surface water contamination by pathogen bacteria remains a threat to public health in the rural areas of developing countries. Fecal indicator bacteria (FIB) like Escherichia coli (E. coli) are widely used to assess water contamination, but their behavior in tropical ecosystems is poorly documented. Our study focused on headwater wetlands which are likely to play a key role in stream water purification of fecal pollutants. Our main objectives were to: (i) evaluate decay rates (k) of the total, particle-attached and free-living E. coli; (ii) quantify the relative importance of solar radiation exposition and suspended particles deposition on k; and (iii) investigate E. coli survival in the deposited sediment. We installed and monitored 12 mesocosms, 4500 mL each, across the main headwater wetland of the Houay Pano catchment, northern Lao People’s Democratic Republic (Lao PDR), for 8 days. The four treatments with triplicates were: sediment deposition-light (DL); sediment deposition-dark (DD); sediment resuspension-light (RL); and sediment resuspension-dark (RD). Particle-attached bacteria predominated in all mesocosms (97 ± 6%). Decay rates ranged from 1.43 ± 0.15 to 1.17 ± 0.13 day−1 for DL and DD treatments, and from 0.50 ± 0.15 to −0.14 ± 0.37 day−1 for RL and RD treatments. Deposition processes accounted for an average of 92% of E. coli stock reduction, while solar radiation accounted for around 2% over the experiment duration. The sampling of E. coli by temporary resuspension of the deposited sediment showed k values close to zero, suggesting potential survival or even growth of bacteria in the sediment. The present findings may help parameterizing hydrological and water quality models in a tropical context.
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Chen W, Nover D, Xia Y, Zhang G, Yen H, He B. Assessment of extrinsic and intrinsic influences on water quality variation in subtropical agricultural multipond systems. ENVIRONMENTAL POLLUTION (BARKING, ESSEX : 1987) 2021; 276:116689. [PMID: 33592448 DOI: 10.1016/j.envpol.2021.116689] [Citation(s) in RCA: 2] [Impact Index Per Article: 0.7] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/16/2020] [Revised: 12/18/2020] [Accepted: 02/03/2021] [Indexed: 06/12/2023]
Abstract
Understanding wetland water quality dynamics and associated influencing factors is important to assess the numerous ecosystem services they provide. We present a combined self-organizing map (SOM) and linear mixed-effects model (LMEM) to relate water quality variation of multipond systems (MPSs, a common type of non-floodplain wetlands in agricultural regions of southern China) to their extrinsic and intrinsic influences for the first time. Across the 6 test MPSs with environmental gradients, ammonium nitrogen (NH4+-N), total nitrogen (TN), and total phosphate (TP) almost always exceeded the surface water quality standard (2.0, 2.0, and 0.4 mg/L, respectively) in the up- and midstream ponds, while chlorophyll-a (Chl-a) exhibited hypertrophic state (≥28 μg/L) in the midstream ponds during the wet season. Synergistic influences explained 69±12% and 73±10% of the water quality variations in the wet and dry season, respectively. The adverse, extrinsic influences were generally 1.4, 6.9, 3.2, and 4.3 times of the beneficial, intrinsic influences for NH4+-N, nitrate nitrogen (NO3--N), TP, and potassium permanganate index (CODMn), respectively, although the influencing direction and degree of forest and water area proportion were spatiotemporally unstable. While CODMn was primarily linked with rural residential areas in the midstream, higher TN and TP concentrations in the up- and midstream were associated with agricultural land, and NH4+-N reflected a small but non-negligible source of free-range poultry feeding. Pond surface sediments exhibited consistent, adverse effects with amplifications during rainfall, while macrophyte biomass can reflect the biological uptake of CODMn and Chl-a, especially in the mid- and downstream during the wet season. Our study advances nonpoint source pollution (NPSP) research for small water bodies, explores nutrient "source-sink" dynamics, and provides a timely guide for rural planning and pond management. The modelling procedures and analytical results can inform refined assessment of similar NFWs elsewhere, where restoration efforts are required.
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Affiliation(s)
- Wenjun Chen
- Jinling Institute of Technology, Nanjing, 211169, China; Key Laboratory of Watershed Geographic Science, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing, 210008, China.
| | - Daniel Nover
- School of Engineering, University of California Merced, Merced, CA, 95343, USA
| | - Yongqiu Xia
- State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing, 210008, China
| | - Guangxin Zhang
- Key Laboratory of Wetland Ecology and Environment, Northeast Institute of Geography and Agroecology, Chinese Academy of Sciences, Changchun, 130102, China
| | - Haw Yen
- Blackland Research and Extension Center, Texas A&M Agrilife Research, Texas A&M University, Temple, TX, 76502, USA
| | - Bin He
- Key Laboratory of Watershed Geographic Science, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing, 210008, China; Guangdong Institute of Eco-environmental Science & Technology, Guangdong Academy of Sciences, Guangzhou, 510650, China
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Interannual and Seasonal Variations of Hydrological Connectivity in a Large Shallow Wetland of North China Estimated from Landsat 8 Images. REMOTE SENSING 2021. [DOI: 10.3390/rs13061214] [Citation(s) in RCA: 9] [Impact Index Per Article: 3.0] [Reference Citation Analysis] [Abstract] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 11/17/2022]
Abstract
Hydrological connectivity is an important characteristic of wetlands that maintains the stability and functions of an ecosystem. This study investigates the temporal variations of hydrological connectivity and their driving mechanism in Baiyangdian Lake, a large shallow wetland in North China, using a time series of open water surface area data derived from 36 Landsat 8 multispectral images from 2013–2019 and in situ measured water level data. Water area classification was implemented using the Google Earth Engine. Six commonly used indexes for extracting water surface data from satellite images were compared and the best performing index was selected for the water classification. A composite hydrological connectivity index computed from open water area data derived from Landsat 8 images was developed based on several landscape pattern indices and applied to Baiyangdian Lake. The results show that, reflectance in the near-infrared band is the most accurate index for water classification with >98% overall accuracy because of its sensitivity to different land cover types. The slopes of the best-fit linear relationships between the computed hydrological connectivity and observed water level show high variability between years. In most years, hydrological connectivity generally increases when water levels increase, with an average R2 of 0.88. The spatial distribution of emergent plants also varies year to year owing to interannual variations of the climate and hydrological regime. This presents a possible explanation for the variations in the annual relationship between hydrological connectivity and water level. For a given water level, the hydrological connectivity is generally higher in spring than summer and autumn. This can be explained by the fact that the drag force exerted by emergent plants, which reduces water flow, is smaller than that for summer and autumn owing to seasonal variations in the phenological characteristics of emergent plants. Our study reveals that both interannual and seasonal variations in the hydrological connectivity of Baiyangdian Lake are related to the growth of emergent plants, which occupy a large portion of the lake area. Proper vegetation management may therefore improve hydrological connectivity in this wetland.
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Chen W, Nover D, Yen H, Xia Y, He B, Sun W, Viers J. Exploring the multiscale hydrologic regulation of multipond systems in a humid agricultural catchment. WATER RESEARCH 2020; 184:115987. [PMID: 32688156 DOI: 10.1016/j.watres.2020.115987] [Citation(s) in RCA: 3] [Impact Index Per Article: 0.8] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 02/01/2020] [Revised: 05/24/2020] [Accepted: 05/25/2020] [Indexed: 06/11/2023]
Abstract
Assessing the hydrologic processes over scales ranging from single wetland to regional is critical to understand the hydrologically-driven ecosystem services especially nutrient buffering of wetlands. Here, we present a novel approach to quantify the multiscale hydrologic regulation of multipond systems (MPSs), a common type of small, scattered wetland in humid agricultural regions, because previous studies have stopped in commending the catchment scale flood and drought resilience of these waters, and contemporary models do not adequately represent the corresponding intra-catchment fill-spill relationships. A new version of Soil and Water Assessment Tool (SWAT) was developed to incorporate improved representation of: (1) perennial or intermittent spillage connections of pond-to-pond and pond-to-stream, and (2) bidirectional exchange between pond surface water and shallow groundwater. We present SWAT-MPS, which adopts rule-based artificial intelligence to model the possibilities of different spillage directions and GA-based parameter optimization over the two simulation years (June 2017 to May 2019), with successfully replicated streamflow and pond water-level variations in a 4.8 km2 test catchment, southern China. Water balance analysis and scenario simulations were then executed to assess the hydrologic regulation at single pond, single MPS, and entire catchment scales. Results revealed (1) the presence of 9 series- or series-parallel connected MPSs, in which pond overflow accounted for as much as 59% of the catchment water yield; (2) seasonally- and MPS-independent baseflow support and quickflow attenuation, with ranked level of pond water storage for baseflow support across different landuse types: forest > farm > village, and inversed correlation of pond spillage to baseflow and quickflow variations in the farmland; and (3) MPS-aggregated catchment flood peak reduction (>20%) and baseflow increment (26%) in the following dry days. Meteorological data analysis and simulated average daily values indicated these hydrologic patterns are credible even if extending to a 5-year period. As a first modelling attempt to explore the intra-catchment details of MPSs, our study underscores the water storage and connectivity in their hydrologic regulation, and suggests inventories, long-term field monitoring, and several research directions of the new model for integrated pond management in watersheds and river basins. These findings can inform refined assessment of similar small, scattered wetlands elsewhere, where restoration efforts are required.
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Affiliation(s)
- Wenjun Chen
- Jinling Institute of Technology, 99 Hongjing Road, Nanjing, 211169, China; Key Laboratory of Watershed Geographic Science, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing, 210008, China.
| | - Daniel Nover
- School of Engineering, University of California Merced, Merced, CA, 95343, USA
| | - Haw Yen
- Blackland Research and Extension Center, Texas A&M University, Temple, TX, 76502, USA
| | - Yongqiu Xia
- State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing, 210008, China
| | - Bin He
- Guangdong Institute of Eco-environmental Science & Technology, Guangdong Academy of Sciences, Guangzhou, 510650, China
| | - Wei Sun
- Key Laboratory of Watershed Geographic Science, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing, 210008, China
| | - Joshua Viers
- School of Engineering, University of California Merced, Merced, CA, 95343, USA
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22
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Rajib A, Golden HE, Lane CR, Wu Q. Surface Depression and Wetland Water Storage Improves Major River Basin Hydrologic Predictions. WATER RESOURCES RESEARCH 2020; 56:e2019WR026561. [PMID: 33364639 PMCID: PMC7751708 DOI: 10.1029/2019wr026561] [Citation(s) in RCA: 9] [Impact Index Per Article: 2.3] [Reference Citation Analysis] [Abstract] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 10/16/2019] [Accepted: 04/30/2020] [Indexed: 05/12/2023]
Abstract
Surface water storage in small yet abundant landscape depressions-including wetlands and other small waterbodies-is largely disregarded in conventional hydrologic modeling practices. No quantitative evidence exists of how their exclusion may lead to potentially inaccurate model projections and understanding of hydrologic dynamics across the world's major river basins. To fill this knowledge gap, we developed the first-ever major river basin-scale modeling approach integrating surface depressions and focusing on the 450,000-km2 Upper Mississippi River Basin (UMRB) in the United States. We applied a novel topography-based algorithm to estimate areas and volumes of ~455,000 surface depressions (>1 ha) across the UMRB (in addition to lakes and reservoirs) and subsequently aggregated their effects per subbasin. Compared to a "no depression" conventional model, our depression-integrated model (a) improved streamflow simulation accuracy with increasing upstream abundance of depression storage, (b) significantly altered the spatial patterns and magnitudes of water yields across 315,000 km2 (70%) of the basin area, and (c) provided realistic spatial distributions of rootzone wetness conditions corresponding to satellite-based data. Results further suggest that storage capacity (i.e., volume) alone does not fully explain depressions' cumulative effects on landscape hydrologic responses. Local (i.e., subbasin level) climatic and geophysical drivers and downstream flowpath-regulating structures (e.g., reservoirs and dams) influence the extent to which depression storage volume in a subbasin causes hydrologic effects. With these new insights, our study supports the integration of surface depression storage and thereby catalyzes a reassessment of current hydrological modeling and management practices for basin-scale studies.
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Affiliation(s)
- Adnan Rajib
- Department of Environmental Engineering, Texas A&M University, Kingsville, TX, USA
- Formerly at Oak Ridge Institute for Science and Education, US Environmental Protection Agency, Office of Research and Development, Cincinnati, OH, USA
| | - Heather E Golden
- US Environmental Protection Agency, Office of Research and Development, Cincinnati, OH, USA
| | - Charles R Lane
- US Environmental Protection Agency, Office of Research and Development, Cincinnati, OH, USA
| | - Qiusheng Wu
- Department of Geography, University of Tennessee, Knoxville, TN, USA
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Meng B, Liu JL, Bao K, Sun B. Methodologies and Management Framework for Restoration of Wetland Hydrologic Connectivity: A Synthesis. INTEGRATED ENVIRONMENTAL ASSESSMENT AND MANAGEMENT 2020; 16:438-451. [PMID: 32100941 DOI: 10.1002/ieam.4256] [Citation(s) in RCA: 5] [Impact Index Per Article: 1.3] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 07/23/2019] [Revised: 12/13/2019] [Accepted: 02/20/2020] [Indexed: 06/10/2023]
Abstract
Under the dual influences of high-intensity anthropogenic activity and climate change, wetland hydrologic connectivity (HC) has decreased significantly, resulting in the severe fragmentation of wetlands, a decrease in wetland area, and a degradation of hydrological functions, resulting in a worsening disaster response to floods and droughts. Dynamic changes in wetland HC are affected by a variety of factors. Many degraded wetlands have undergone measures to restore HC. Recovery can improve the HC pattern of degraded wetlands. Based on the knowledge of practitioners and a review of the literature, it was found that recovery measures can be divided into structural recovery and functional recovery according to the specific recovery objectives. However, the current recovery method lacks a holistic analysis of the HC pattern. To this end, we propose a hydrologic network-water balance-based HC recovery and management framework that overcomes the limitations of single-drive-factor repair and local repair effects. Integr Environ Assess Manag 2020;16:438-451. © 2020 SETAC.
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Affiliation(s)
- Bo Meng
- State Key Joint Laboratory of Environmental Simulation and Pollution Control, School of Environment, Beijing Normal University, Beijing, China
| | - Jing-Ling Liu
- State Key Joint Laboratory of Environmental Simulation and Pollution Control, School of Environment, Beijing Normal University, Beijing, China
| | - Kun Bao
- State Key Joint Laboratory of Environmental Simulation and Pollution Control, School of Environment, Beijing Normal University, Beijing, China
| | - Bin Sun
- State Key Joint Laboratory of Environmental Simulation and Pollution Control, School of Environment, Beijing Normal University, Beijing, China
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Neff BP, Rosenberry DO, Leibowitz SG, Mushet DM, Golden HE, Rains MC, Renée Brooks J, Lane CR. A Hydrologic Landscapes Perspective on Groundwater Connectivity of Depressional Wetlands. WATER 2019; 12:50. [PMID: 34012619 PMCID: PMC8128703 DOI: 10.3390/w12010050] [Citation(s) in RCA: 8] [Impact Index Per Article: 1.6] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Download PDF] [Figures] [Subscribe] [Scholar Register] [Indexed: 11/16/2022]
Abstract
Research into processes governing the hydrologic connectivity of depressional wetlands has advanced rapidly in recent years. Nevertheless, a need persists for broadly applicable, non-site-specific guidance to facilitate further research. Here, we explicitly use the hydrologic landscapes theoretical framework to develop broadly applicable conceptual knowledge of depressional-wetland hydrologic connectivity. We used a numerical model to simulate the groundwater flow through five generic hydrologic landscapes. Next, we inserted depressional wetlands into the generic landscapes and repeated the modeling exercise. The results strongly characterize groundwater connectivity from uplands to lowlands as being predominantly indirect. Groundwater flowed from uplands and most of it was discharged to the surface at a concave-upward break in slope, possibly continuing as surface water to lowlands. Additionally, we found that groundwater connectivity of the depressional wetlands was primarily determined by the slope of the adjacent water table. However, we identified certain arrangements of landforms that caused the water table to fall sharply and not follow the surface contour. Finally, we synthesize our findings and provide guidance to practitioners and resource managers regarding the management significance of indirect groundwater discharge and the effect of depressional wetland groundwater connectivity on pond permanence and connectivity.
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Affiliation(s)
- Brian P. Neff
- Former post-doctoral Research Hydrologist, National Research Program, U.S. Geological Survey, Lakewood, CO 80225, USA
| | - Donald O. Rosenberry
- Earth System Processes Division, Water Mission Area, U.S. Geological Survey, Lakewood, CO 80225, USA
| | - Scott G. Leibowitz
- Pacific Ecological Systems Division, Center for Public Health and Environmental Assessment, U.S. Environmental Protection Agency, Corvallis, OR 97333, USA
| | - Dave M. Mushet
- Northern Prairie Wildlife Research Center, U.S. Geological Survey, Jamestown, ND 58401-7317, USA
| | - Heather E. Golden
- Center for Environmental Measurement and Modeling, Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, OH 45268, USA
| | - Mark C. Rains
- School of Geosciences, University of South Florida, Tampa, FL 33620, USA
| | - J. Renée Brooks
- Pacific Ecological Systems Division, Center for Public Health and Environmental Assessment, U.S. Environmental Protection Agency, Corvallis, OR 97333, USA
| | - Charles R. Lane
- Center for Environmental Measurement and Modeling, Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, OH 45268, USA
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25
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Zhang W, Pueppke SG, Li H, Geng J, Diao Y, Hyndman DW. Modeling phosphorus sources and transport in a headwater catchment with rapid agricultural expansion. ENVIRONMENTAL POLLUTION (BARKING, ESSEX : 1987) 2019; 255:113273. [PMID: 31627173 DOI: 10.1016/j.envpol.2019.113273] [Citation(s) in RCA: 5] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 07/03/2019] [Revised: 08/27/2019] [Accepted: 09/17/2019] [Indexed: 06/10/2023]
Abstract
Increasing riverine phosphorus (P) levels in headwaters due to expanded and intensified human activities are worldwide concerns, because P is a well-known limiting nutrient for freshwater eutrophication. Here we adopt the conceptual framework of the SPAtially Referenced Regressions On Watershed attributes (SPARROW) model to describe total phosphorus (TP) sources and transport in a headwater watershed undergoing rapid agricultural expansion in the upper Taihu Lake Basin, China. Our models, which include variables for land cover, river length, runoff depth, and pond density, explain 94% of the spatio-temporal variability in TP loads. Agricultural lands contribute the largest percentage (61%) of the TP loads delivered downstream, followed by forestland (21%) and urban land (18%). Future agricultural expansion to 15% of the total basin area is possible, which could lead to a 50% increase in TP loads. According to our analysis, an average of 24% of the total P export from the watershed landscape was intercepted in ponds. The exported amount was subsequently retained by tributaries and along the mainstem river, accounting for 14% and 43% of their inflowing loads, respectively. The remaining ∼6 tons yr-1 of TP was eventually transported into Tianmu Lake, in Southeastern China. The model identified several sub-catchments as hotspots of TP loss and thus logical sites for targeted management. Our study underscores the significance of agricultural expansion as a factor that can exacerbate headwater TP pollution, highlighting the importance of landscapes to buffer TP losses from sensitive hilly catchments. This also points to a need for an integrated management strategy that considers the spatial-varying P sources and associated transport of TP in precious headwater resources.
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Affiliation(s)
- Wangshou Zhang
- Key Laboratory of Watershed Geographic Sciences, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China
| | - Steven G Pueppke
- Center for Global Change and Earth Observations, Michigan State University, East Lansing, MI 48824, USA; Asia Hub, Nanjing Agricultural University, Nanjing 210095, China
| | - Hengpeng Li
- Key Laboratory of Watershed Geographic Sciences, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China.
| | - Jianwei Geng
- Key Laboratory of Watershed Geographic Sciences, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China
| | - Yaqin Diao
- Key Laboratory of Watershed Geographic Sciences, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China
| | - David W Hyndman
- Department of Earth and Environmental Sciences, Michigan State University, East Lansing, MI, 48854, USA
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26
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Golden HE, Rajib A, Lane CR, Christensen JR, Wu Q, Mengistu S. Non-floodplain Wetlands Affect Watershed Nutrient Dynamics: A Critical Review. ENVIRONMENTAL SCIENCE & TECHNOLOGY 2019; 53:7203-7214. [PMID: 31244063 PMCID: PMC9096804 DOI: 10.1021/acs.est.8b07270] [Citation(s) in RCA: 25] [Impact Index Per Article: 5.0] [Reference Citation Analysis] [Abstract] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/25/2023]
Abstract
Wetlands have the capacity to retain nitrogen and phosphorus and are thereby often considered a viable option for improving water quality at local scales. However, little is known about the cumulative influence of wetlands outside of floodplains, i.e., non-floodplain wetlands (NFWs), on surface water quality at watershed scales. Such evidence is important to meet global, national, regional, and local water quality goals effectively and comprehensively. In this critical review, we synthesize the state of the science about the watershed-scale effects of NFWs on nutrient-based (nitrogen, phosphorus) water quality. We further highlight where knowledge is limited in this research area and the challenges of garnering this information. On the basis of previous wetland literature, we develop emerging concepts that assist in advancing the science linking NFWs to watershed-scale nutrient conditions. Finally, we ask, "Where do we go from here?" We address this question using a 2-fold approach. First, we demonstrate, via example model simulations, how explicitly considering NFWs in watershed nutrient modeling changes predicted nutrient yields to receiving waters-and how this may potentially affect future water quality management decisions. Second, we outline research recommendations that will improve our scientific understanding of how NFWs affect downstream water quality.
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Affiliation(s)
- Heather E Golden
- National Exposure Research Laboratory , U.S. Environmental Protection Agency , Office of Research and Development, 26 West Martin Luther King Drive , Cincinnati , Ohio 45268 , United States
| | - Adnan Rajib
- Oak Ridge Institute for Science and Education , c/o Environmental Protection Agency, Office of Research and Development, 26 West Martin Luther King Drive , Cincinnati , Ohio 45268 , United States
| | - Charles R Lane
- National Exposure Research Laboratory , U.S. Environmental Protection Agency , Office of Research and Development, 26 West Martin Luther King Drive , Cincinnati , Ohio 45268 , United States
| | - Jay R Christensen
- National Exposure Research Laboratory , U.S. Environmental Protection Agency , Office of Research and Development, 26 West Martin Luther King Drive , Cincinnati , Ohio 45268 , United States
| | - Qiusheng Wu
- Department of Geography , University of Tennessee , Knoxville , Tennessee 37996 , United States
| | - Samson Mengistu
- National Research Council , National Academy of Sciences, c/o Environmental Protection Agency, Office of Research and Development, 26 West Martin Luther King Drive , Cincinnati , Ohio 45268 , United States
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27
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Sullivan SMP, Rains MC, Rodewald AD. Opinion: The proposed change to the definition of "waters of the United States" flouts sound science. Proc Natl Acad Sci U S A 2019; 116:11558-11561. [PMID: 31186378 PMCID: PMC6576110 DOI: 10.1073/pnas.1907489116] [Citation(s) in RCA: 23] [Impact Index Per Article: 4.6] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/18/2022] Open
Affiliation(s)
- S Mažeika P Sullivan
- Schiermeier Olentangy River Wetland Research Park, School of Environment & Natural Resources, The Ohio State University, Columbus, OH 43202;
| | - Mark C Rains
- School of Geosciences, University of South Florida, Tampa, FL 33620
| | - Amanda D Rodewald
- Cornell Lab of Ornithology, Cornell University, Ithaca, NY 14850
- Department of Natural Resources, Cornell University, Ithaca, NY 14850
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28
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Vanderhoof MK, Lane CR. The potential role of very high-resolution imagery to characterise lake, wetland and stream systems across the Prairie Pothole Region, United States. INTERNATIONAL JOURNAL OF REMOTE SENSING 2019; 40:5768-5798. [PMID: 33408426 PMCID: PMC7784670 DOI: 10.1080/01431161.2019.1582112] [Citation(s) in RCA: 5] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [Abstract] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/20/2018] [Accepted: 01/01/2019] [Indexed: 05/22/2023]
Abstract
Aquatic features critical to watershed hydrology range widely in size from narrow, shallow streams to large, deep lakes. In this study we evaluated wetland, lake, and river systems across the Prairie Pothole Region to explore where pan-sharpened high-resolution (PSHR) imagery, relative to Landsat imagery, could pro-vide additional data on surface water distribution and movement, missed by Landsat. We used the monthly Global Surface Water (GSW) Landsat product as well as surface water derived from Landsat imagery using a matched filtering algorithm (MF Landsat) to help consider how including partially inundated Landsat pixels as water influenced our findings. The PSHR outputs (and MF Landsat) were able to identify ~60-90% more surface water interactions between waterbodies, relative to the GSW Landsat product. However, regardless of Landsat source, by doc-umenting many smaller (<0.2 ha), inundated wetlands, the PSHR outputs modified our interpretation of wetland size distribution across the Prairie Pothole Region.
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Affiliation(s)
- Melanie K Vanderhoof
- U.S. Geological Survey, Geosciences and Environmental Change Science Center, Denver, CO, USA
| | - Charles R Lane
- U.S. Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, Cincinnati, OH, USA
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29
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Jones CN, Ameli A, Neff BP, Evenson GR, McLaughlin DL, Golden HE, Lane CR. Modeling Connectivity of Non-floodplain Wetlands: Insights, Approaches, and Recommendations. JOURNAL OF THE AMERICAN WATER RESOURCES ASSOCIATION 2019; 55:559-577. [PMID: 34316250 PMCID: PMC8312621 DOI: 10.1111/1752-1688.12735] [Citation(s) in RCA: 3] [Impact Index Per Article: 0.6] [Reference Citation Analysis] [Abstract] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 02/22/2018] [Accepted: 01/17/2019] [Indexed: 05/25/2023]
Abstract
Representing hydrologic connectivity of non-floodplain wetlands (NFWs) to downstream waters in process-based models is an emerging challenge relevant to many research, regulatory, and management activities. We review four case studies that utilize process-based models developed to simulate NFW hydrology. Models range from a simple, lumped parameter model to a highly complex, fully distributed model. Across case studies, we highlight appropriate application of each model, emphasizing spatial scale, computational demands, process representation, and model limitations. We end with a synthesis of recommended "best modeling practices" to guide model application. These recommendations include: (1) clearly articulate modeling objectives, and revisit and adjust those objectives regularly; (2) develop a conceptualization of NFW connectivity using qualitative observations, empirical data, and process-based modeling; (3) select a model to represent NFW connectivity by balancing both modeling objectives and available resources; (4) use innovative techniques and data sources to validate and calibrate NFW connectivity simulations; and (5) clearly articulate the limits of the resulting NFW connectivity representation. Our review and synthesis of these case studies highlights modeling approaches that incorporate NFW connectivity, demonstrates tradeoffs in model selection, and ultimately provides actionable guidance for future model application and development.
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Affiliation(s)
| | - Ali Ameli
- University of Maryland, School of Environment and Sustainability
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30
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Wu Q, Lane CR, Wang L, Vanderhoof MK, Christensen JR, Liu H. Efficient Delineation of Nested Depression Hierarchy in Digital Elevation Models for Hydrological Analysis Using Level-Set Methods. JOURNAL OF THE AMERICAN WATER RESOURCES ASSOCIATION 2019; 55:354-368. [PMID: 33776405 PMCID: PMC7995241 DOI: 10.1111/1752-1688.12689] [Citation(s) in RCA: 18] [Impact Index Per Article: 3.6] [Reference Citation Analysis] [Abstract] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 02/01/2018] [Accepted: 08/20/2018] [Indexed: 05/22/2023]
Abstract
In terrain analysis and hydrological modeling, surface depressions (or sinks) in a digital elevation model (DEM) are commonly treated as artifacts and thus filled and removed to create a depressionless DEM. Various algorithms have been developed to identify and fill depressions in DEMs during the past decades. However, few studies have attempted to delineate and quantify the nested hierarchy of actual depressions, which can provide crucial information for characterizing surface hydrologic connectivity and simulating the fill-merge-spill hydrological process. In this paper, we present an innovative and efficient algorithm for delineating and quantifying nested depressions in DEMs using the level-set method based on graph theory. The proposed level-set method emulates water level decreasing from the spill point along the depression boundary to the lowest point at the bottom of a depression. By tracing the dynamic topological changes (i.e., depression splitting/merging) within a compound depression, the level-set method can construct topological graphs and derive geometric properties of the nested depressions. The experimental results of two fine-resolution Light Detection and Ranging-derived DEMs show that the raster-based level-set algorithm is much more efficient (~150 times faster) than the vector-based contour tree method. The proposed level-set algorithm has great potential for being applied to large-scale ecohydrological analysis and watershed modeling.
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Affiliation(s)
- Qiusheng Wu
- Department of Geography, Binghamton University, Binghamton, New York, USA
| | - Charles R Lane
- Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, Ohio, USA
| | - Lei Wang
- Department of Geography and Anthropology, Louisiana State University, Baton Rouge, Louisiana, USA
| | - Melanie K Vanderhoof
- Geosciences and Environmental Change Science Center, U.S. Geological Survey, Denver, Colorado, USA
| | - Jay R Christensen
- Office of Research and Development, U.S. Environmental Protection Agency, Las Vegas, Nevada, USA
| | - Hongxing Liu
- Department of Geography, University of Cincinnati, Cincinnati, Ohio, USA
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31
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Yeo IY, Lee S, Lang MW, Yetemen O, McCarty GW, Sadeghi AM, Evenson G. Mapping landscape-level hydrological connectivity of headwater wetlands to downstream waters: A catchment modeling approach - Part 2. THE SCIENCE OF THE TOTAL ENVIRONMENT 2019; 653:1557-1570. [PMID: 30527888 DOI: 10.1016/j.scitotenv.2018.11.237] [Citation(s) in RCA: 3] [Impact Index Per Article: 0.6] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Subscribe] [Scholar Register] [Received: 05/28/2018] [Revised: 10/30/2018] [Accepted: 11/16/2018] [Indexed: 06/09/2023]
Abstract
In Part 1 of this two-part manuscript series, we presented an effective assessment method for mapping inundation of geographically isolated wetlands (GIWs) and quantifying their cumulative landscape-scale hydrological connectivity with downstream waters using time series remotely sensed data (Yeo et al., 2018). This study suggested strong hydrological coupling between GIWs and downstream waters at the seasonal timescale via groundwater. This follow-on paper investigates the hydrological connectivity of GIWs with downstream waters and cumulative watershed-scale hydrological impacts over multiple time scales. Modifications were made to the representation of wetland processes within the Soil and Water Assessment Tool (SWAT). A version of SWAT with improved wetland function, SWAT-WET, was applied to Greensboro Watershed, which is located in the Mid-Atlantic Region of USA, to simulate hydrological processes over 1985-2015 under two contrasting land use scenarios (i.e., presence and absence of GIWs). Comparative analysis of simulation outputs elucidated how GIWs could influence partitioning of precipitation between evapotranspiration (ET) and terrestrial water storage, and affect water transport mechanisms and routing processes that generate streamflow. Model results showed that GIWs influenced the watershed water budget and stream flow generation processes over the long-term (30 year), inter-annual, and monthly time scales. GIWs in the study watershed increased terrestrial water storage during the wet season, and buffered the dynamics of shallow groundwater during the dry season. The inter-annual modeling analysis illustrated that densely distributed GIWs can exert strong hydrological influence on downstream waters by regulating surface water runoff, while maintaining groundwater recharge and ET under changing (wetter) climate conditions. The study findings highlight the hydrological connectivity of GIWs with downstream waters and the cumulative hydrological influence of GIWs as hydrologic sources to downstream ecosystems through different runoff processes over multiple time scales.
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Affiliation(s)
- In-Young Yeo
- School of Engineering, The University of Newcastle, Callaghan, NSW 2308, Australia; Department of Geographical Sciences, University of Maryland, College Park, MD 20742, USA.
| | - Sangchul Lee
- Department of Environmental Science and Technology, University of Maryland, College Park, MD 20742, USA; US Department of Agriculture - Agricultural Research Service, Hydrology and Remote Sensing Laboratory, Beltsville, MD 20705, USA
| | - Megan W Lang
- Department of Geographical Sciences, University of Maryland, College Park, MD 20742, USA
| | - Omer Yetemen
- School of Engineering, The University of Newcastle, Callaghan, NSW 2308, Australia
| | - Gregory W McCarty
- US Department of Agriculture - Agricultural Research Service, Hydrology and Remote Sensing Laboratory, Beltsville, MD 20705, USA
| | - Ali M Sadeghi
- US Department of Agriculture - Agricultural Research Service, Hydrology and Remote Sensing Laboratory, Beltsville, MD 20705, USA
| | - Grey Evenson
- Department of Food, Agricultural and Biological Engineering, The Ohio State University, Columbus, OH 43210, USA
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Rajib A, Evenson GR, Golden HE, Lane CR. Hydrologic model predictability improves with spatially explicit calibration using remotely sensed evapotranspiration and biophysical parameters. JOURNAL OF HYDROLOGY 2018; 567:668-683. [PMID: 31395990 PMCID: PMC6687302 DOI: 10.1016/j.jhydrol.2018.10.024] [Citation(s) in RCA: 12] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/10/2023]
Abstract
A hydrologic model, calibrated using only streamflow data, can produce acceptable streamflow simulation at the watershed outlet yet unrealistic representations of water balance across the landscape. Recent studies have demonstrated the potential of multi-objective calibration using remotely sensed evapotranspiration (ET) and gaged streamflow data to spatially improve the water balance. However, methodological clarity on how to "best" integrate ET data and model parameters in multi-objective model calibration to improve simulations is lacking. To address these limitations, we assessed how a spatially explicit, distributed calibration approach that uses (1) remotely sensed ET data from the Moderate Resolution Imaging Spectroradiometer (MODIS) and (2) frequently overlooked biophysical parameters can improve the overall predictability of two key components of the water balance: streamflow and ET at different locations throughout the watershed. We used the Soil and Water Assessment Tool (SWAT), previously modified to represent hydrologic transport and filling-spilling of landscape depressions, in a large watershed of the Prairie Pothole Region, United States. We employed a novel stepwise series of calibration experiments to isolate the effects (on streamflow and simulated ET) of integrating biophysical parameters and spatially explicit remotely sensed ET data into model calibration. Results suggest that the inclusion of biophysical parameters involving vegetation dynamics and energy utilization mechanisms tend to increase model accuracy. Furthermore, we found that using a lumped, versus a spatially explicit, approach for integrating ET into model calibration produces a sub-optimal model state with no potential improvement in model performance across large spatial scales. However, when we utilized the same MODIS ET datasets but calibrated each sub-basin in the spatially explicit approach, water yield prediction uncertainty decreased, including a distinct improvement in the temporal and spatial accuracy of simulated ET and streamflow. This further resulted in a more realistic simulation of vegetation growth when compared to MODIS Leaf-Area Index data. These findings afford critical insights into the efficient integration of remotely sensed "big data" into hydrologic modeling and associated watershed management decisions. Our approach can be generalized and potentially replicated using other hydrologic models and remotely sensed data resources - and in different geophysical settings of the globe.
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Affiliation(s)
- Adnan Rajib
- Oak Ridge Institute for Science and Education, US Environmental Protection Agency, Office of Research and Development, Cincinnati, OH, USA
| | - Grey R. Evenson
- Department of Food, Agricultural and Biological Engineering, Ohio State University, Columbus, OH, USA
| | - Heather E. Golden
- US Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, Cincinnati, OH, USA
| | - Charles R. Lane
- US Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, Cincinnati, OH, USA
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Evenson GR, Jones CN, McLaughlin DL, Golden HE, Lane CR, DeVries B, Alexander LC, Lang MW, McCarty GW, Sharifi A. A watershed-scale model for depressional wetland-rich landscapes. JOURNAL OF HYDROLOGY: X 2018; 1:100002. [PMID: 31448367 PMCID: PMC6707518 DOI: 10.1016/j.hydroa.2018.10.002] [Citation(s) in RCA: 6] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 04/26/2023]
Abstract
Wetlands are often dominant features in low relief, depressional landscapes and provide an array of hydrologically driven ecosystem services. However, contemporary models do not adequately represent the role of spatially distributed wetlands in watershed-scale water storage and flows. Such tools are critical to better understand wetland hydrological, biogeochemical, and biological functions and predict management and policy outcomes at varying spatial scales. To develop a new approach for simulating depressional landscapes, we modified the Soil and Water Assessment Tool (SWAT) model to incorporate improved representations of depressional wetland structure and hydrological processes. Specifically, we refined the model to incorporate: (1) water storage capacity and surface flowpaths of individual wetlands and (2) local wetland surface and subsurface exchange. We utilized this model, termed SWAT-DSF (DSF for Depressional Storage and Flows), to simulate the ~289 km2 Greensboro watershed within the Delmarva Peninsula of the US Coastal Plain. Model calibration and verification used both daily streamflow observations and remotely sensed surface water extent data (ca. 2-week temporal resolution), allowing us to assess model performance with respect to both streamflow and watershed inundation patterns. Our findings demonstrate that SWAT-DSF can successfully replicate distributed wetland processes and resultant watershed-scale hydrology. SWAT-DSF provides improved temporal and spatial characterization of watershed-scale water storage and flows in depressional landscapes, providing a new tool to quantify wetland functions at broad spatial scales.
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Affiliation(s)
- Grey R. Evenson
- Department of Food, Agricultural, and Biological Engineering, The Ohio State University, Columbus, OH, USA
| | - C. Nathan Jones
- The National Socio-Environmental Synthesis Center, University of Maryland, Annapolis, MD, USA
| | - Daniel L. McLaughlin
- Department of Forest Resources and Environmental Conservation, Virginia Polytechnic Institute and State University, Blacksburg, VA, USA
| | - Heather E. Golden
- US Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, Cincinnati, OH, USA
| | - Charles R. Lane
- US Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, Cincinnati, OH, USA
| | - Ben DeVries
- Department of Geographical Sciences, University of Maryland, College Park, MD, USA
| | - Laurie C. Alexander
- US Environmental Protection Agency, Office of Research and Development, Washington, DC, USA
| | - Megan W. Lang
- USFWS National Wetlands Inventory Program, Falls Church, VA, USA
| | - Gregory W. McCarty
- US Department of Agriculture – Agricultural Research Service, Hydrology and Remote Sensing Laboratory, Beltsville, MD, USA
| | - Amirreza Sharifi
- Government of the District of Columbia, Department of Energy and Environment, Water Quality Division, Washington, DC, USA
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34
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Brazil's Native Vegetation Protection Law threatens to collapse pond functions. Perspect Ecol Conserv 2018. [DOI: 10.1016/j.pecon.2018.08.003] [Citation(s) in RCA: 9] [Impact Index Per Article: 1.5] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 12/19/2022] Open
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35
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Fritz KM, Schofield KA, Alexander LC, McManus MG, Golden HE, Lane CR, Kepner WG, LeDuc SD, DeMeester JE, Pollard AI. PHYSICAL AND CHEMICAL CONNECTIVITY OF STREAMS AND RIPARIAN WETLANDS TO DOWNSTREAM WATERS: A SYNTHESIS. JOURNAL OF THE AMERICAN WATER RESOURCES ASSOCIATION 2018; 54:323-345. [PMID: 30245566 PMCID: PMC6145469 DOI: 10.1111/1752-1688.12632] [Citation(s) in RCA: 21] [Impact Index Per Article: 3.5] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/03/2023]
Abstract
Streams, riparian areas, floodplains, alluvial aquifers and downstream waters (e.g., large rivers, lakes, oceans) are interconnected by longitudinal, lateral, and vertical fluxes of water, other materials and energy. Collectively, these interconnected waters are called fluvial hydrosystems. Physical and chemical connectivity within fluvial hydrosystems is created by the transport of nonliving materials (e.g., water, sediment, nutrients, contaminants) which either do or do not chemically change (chemical and physical connections, respectively). A substantial body of evidence unequivocally demonstrates physical and chemical connectivity between streams and riparian wetlands and downstream waters. Streams and riparian wetlands are structurally connected to downstream waters through the network of continuous channels and floodplain form that make these systems physically contiguous, and the very existence of these structures provides strong geomorphologic evidence for connectivity. Functional connections between streams and riparian wetlands and their downstream waters vary geographically and over time, based on proximity, relative size, environmental setting, material disparity, and intervening units. Because of the complexity and dynamic nature of connections among fluvial hydrosystem units, a complete accounting of the physical and chemical connections and their consequences to downstream waters should aggregate over multiple years to decades.
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Affiliation(s)
- Ken M Fritz
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
| | - Kate A Schofield
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
| | - Laurie C Alexander
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
| | - Michael G McManus
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
| | - Heather E Golden
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
| | - Charles R Lane
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
| | - William G Kepner
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
| | - Stephen D LeDuc
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
| | - Julie E DeMeester
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
| | - Amina I Pollard
- Respectively, Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Research Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (McManus), National Center for Environmental Assessment, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Physical Scientist (Golden), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, Ohio 45268; Research Ecologist (Kepner), National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, Nevada 89119; Ecologist (LeDuc), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Director of Water Resources (DeMeester), North Carolina Chapter of The Nature Conservancy, Durham, North Carolina; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460 (26 West Martin Luther King Drive, Cincinnati, Ohio 45268; Fritz: )
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Leibowitz SG, Wigington PJ, Schofield KA, Alexander LC, Vanderhoof MK, Golden HE. CONNECTIVITY OF STREAMS AND WETLANDS TO DOWNSTREAM WATERS: AN INTEGRATED SYSTEMS FRAMEWORK. JOURNAL OF THE AMERICAN WATER RESOURCES ASSOCIATION 2018; 54:298-322. [PMID: 30078985 PMCID: PMC6071435 DOI: 10.1111/1752-1688.12631] [Citation(s) in RCA: 43] [Impact Index Per Article: 7.2] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/03/2023]
Abstract
Interest in connectivity has increased in the aquatic sciences, partly because of its relevance to the Clean Water Act. This paper has two objectives: (1) provide a framework to understand hydrological, chemical, and biological connectivity, focusing on how headwater streams and wetlands connect to and contribute to rivers; and (2) review methods to quantify hydrological and chemical connectivity. Streams and wetlands affect river structure and function by altering material and biological fluxes to the river; this depends on two factors: (1) functions within streams and wetlands that affect material fluxes; and (2) connectivity (or isolation) from streams and wetlands to rivers that allows (or prevents) material transport between systems. Connectivity can be described in terms of frequency, magnitude, duration, timing, and rate of change. It results from physical characteristics of a system, e.g., climate, soils, geology, topography, and the spatial distribution of aquatic components. Biological connectivity is also affected by traits and behavior of the biota. Connectivity can be altered by human impacts, often in complex ways. Because of variability in these factors, connectivity is not constant but varies over time and space. Connectivity can be quantified with field-based methods, modeling, and remote sensing. Further studies using these methods are needed to classify and quantify connectivity of aquatic ecosystems and to understand how impacts affect connectivity.
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Affiliation(s)
- Scott G Leibowitz
- Research Ecologist (Leibowitz) and formerly Research Hydrologist (Wigington), National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency, 200 SW 35 St, Corvallis, Oregon 97333; Ecologist (Schofield and Alexander), National Center for Environmental Assessment, U.S. Environmental Protection Agency, Arlington, Virginia 22202; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, U.S. Geological Survey, Denver, Colorado 80225; and Research Physical Scientist (Golden), National Exposure Research Laboratory, U.S. Environmental Protection Agency, Cincinnati, Ohio 45268 (Email/Leibowitz: )
| | - Parker J Wigington
- Research Ecologist (Leibowitz) and formerly Research Hydrologist (Wigington), National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency, 200 SW 35 St, Corvallis, Oregon 97333; Ecologist (Schofield and Alexander), National Center for Environmental Assessment, U.S. Environmental Protection Agency, Arlington, Virginia 22202; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, U.S. Geological Survey, Denver, Colorado 80225; and Research Physical Scientist (Golden), National Exposure Research Laboratory, U.S. Environmental Protection Agency, Cincinnati, Ohio 45268 (Email/Leibowitz: )
| | - Kate A Schofield
- Research Ecologist (Leibowitz) and formerly Research Hydrologist (Wigington), National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency, 200 SW 35 St, Corvallis, Oregon 97333; Ecologist (Schofield and Alexander), National Center for Environmental Assessment, U.S. Environmental Protection Agency, Arlington, Virginia 22202; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, U.S. Geological Survey, Denver, Colorado 80225; and Research Physical Scientist (Golden), National Exposure Research Laboratory, U.S. Environmental Protection Agency, Cincinnati, Ohio 45268 (Email/Leibowitz: )
| | - Laurie C Alexander
- Research Ecologist (Leibowitz) and formerly Research Hydrologist (Wigington), National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency, 200 SW 35 St, Corvallis, Oregon 97333; Ecologist (Schofield and Alexander), National Center for Environmental Assessment, U.S. Environmental Protection Agency, Arlington, Virginia 22202; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, U.S. Geological Survey, Denver, Colorado 80225; and Research Physical Scientist (Golden), National Exposure Research Laboratory, U.S. Environmental Protection Agency, Cincinnati, Ohio 45268 (Email/Leibowitz: )
| | - Melanie K Vanderhoof
- Research Ecologist (Leibowitz) and formerly Research Hydrologist (Wigington), National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency, 200 SW 35 St, Corvallis, Oregon 97333; Ecologist (Schofield and Alexander), National Center for Environmental Assessment, U.S. Environmental Protection Agency, Arlington, Virginia 22202; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, U.S. Geological Survey, Denver, Colorado 80225; and Research Physical Scientist (Golden), National Exposure Research Laboratory, U.S. Environmental Protection Agency, Cincinnati, Ohio 45268 (Email/Leibowitz: )
| | - Heather E Golden
- Research Ecologist (Leibowitz) and formerly Research Hydrologist (Wigington), National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency, 200 SW 35 St, Corvallis, Oregon 97333; Ecologist (Schofield and Alexander), National Center for Environmental Assessment, U.S. Environmental Protection Agency, Arlington, Virginia 22202; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, U.S. Geological Survey, Denver, Colorado 80225; and Research Physical Scientist (Golden), National Exposure Research Laboratory, U.S. Environmental Protection Agency, Cincinnati, Ohio 45268 (Email/Leibowitz: )
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Schofield KA, Alexander LC, Ridley CE, Vanderhoof MK, Fritz KM, Autrey BC, DeMeester JE, Kepner WG, Lane CR, Leibowitz SG, Pollard AI. BIOTA CONNECT AQUATIC HABITATS THROUGHOUT FRESHWATER ECOSYSTEM MOSAICS. JOURNAL OF THE AMERICAN WATER RESOURCES ASSOCIATION 2018; 54:372-399. [PMID: 31296983 PMCID: PMC6621606 DOI: 10.1111/1752-1688.12634] [Citation(s) in RCA: 25] [Impact Index Per Article: 4.2] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/20/2023]
Abstract
Freshwater ecosystems are linked at various spatial and temporal scales by movements of biota adapted to life in water. We review the literature on movements of aquatic organisms that connect different types of freshwater habitats, focusing on linkages from streams and wetlands to downstream waters. Here, streams, wetlands, rivers, lakes, ponds, and other freshwater habitats are viewed as dynamic freshwater ecosystem mosaics (FEMs) that collectively provide the resources needed to sustain aquatic life. Based on existing evidence, it is clear that biotic linkages throughout FEMs have important consequences for biological integrity and biodiversity. All aquatic organisms move within and among FEM components, but differ in the mode, frequency, distance, and timing of their movements. These movements allow biota to recolonize habitats, avoid inbreeding, escape stressors, locate mates, and acquire resources. Cumulatively, these individual movements connect populations within and among FEMs and contribute to local and regional diversity, resilience to disturbance, and persistence of aquatic species in the face of environmental change. Thus, the biological connections established by movement of biota among streams, wetlands, and downstream waters are critical to the ecological integrity of these systems. Future research will help advance our understanding of the movements that link FEMs and their cumulative effects on downstream waters.
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Affiliation(s)
- Kate A Schofield
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - Laurie C Alexander
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - Caroline E Ridley
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - Melanie K Vanderhoof
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - Ken M Fritz
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - Bradley C Autrey
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - Julie E DeMeester
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - William G Kepner
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - Charles R Lane
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - Scott G Leibowitz
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
| | - Amina I Pollard
- Respectively, Ecologist (Schofield), National Center for Environmental Assessment, US Environmental Protection Agency, 1200 Pennsylvania Avenue. NW, Mail Code 8623R, Washington, DC 20460; Ecologist (Alexander), National Center for Environmental Assessment, US Environmental Protection Agency, Washington, DC 20460; Ecologist (Ridley), National Center for Environmental Assessment, US Environmental Protection Agency, Research Triangle Park, NC 27711; Research Geographer (Vanderhoof), Geosciences and Environmental Change Science Center, US Geological Survey, Lakewood, CO 80225; Research Ecologist (Fritz), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Program Analyst (Autrey), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; Water Program Director (DeMeester), The Nature Conservancy, Durham, NC 27701; Research Ecologist (Kepner), Research Ecologist (Lane), National Exposure Research Laboratory, US Environmental Protection Agency, Cincinnati, OH 45268; National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119; Research Ecologist (Leibowitz), National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Corvallis, OR 97333; Research Ecologist (Pollard), Office of Water, US Environmental Protection Agency, Washington, DC 20460
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