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Understanding hydrodynamic and hydrological processes is therefore critical to sustaining ecosystem functions and productivity in tidal wetlands. We used remote sensing and geographic information system to determine the spatial distributions of Suaeda heteroptera and Phragmites australis plants on the tidal-flats of Liao River Estuary (LRE), China. Next, hydrodynamic modelling was performed to characterize the water levels and tidal currents in these wetland waters. After extensive calibration and validation against field data, we proposed a 2D circulation structure for the LRE that can be used to calculate the hydrological parameters in different areas of the tidal wetlands. The simulation results showed that the hydrological characteristics of the tidal wetlands were primarily dependent on local topography and water level. The prevalent plant community in the LRE, dominated by Suaeda heteroptera, was abundant across a large range of flood times (0.79 ~ 3.22 h\u002Fday), inundation frequencies (11 ~ 52 times\u002Fmonth), and max flooding depths (0.42 ~ 0.81 m). However, certain hydrological conditions did appear to limit the spatial distributions of wetland plant communities. These findings have provided detailed methods of a novel approach to quantitatively assess habitat status in tidal-flat wetlands.",{"EN":235},"Modeling Hydrodynamic and Hydrological Processes in Tidal Wetlands",{"VOID":237},"[\"4176088772544505871\"]",{"EN":239},"",{"VOID":241},"Allinson G (2017) Effect of increasing salinity on development of Giant reed (Arundo donax) from rhizome and culms. Bulletin of Environmental Contamination and Toxicology 99:743–747\nAlongi DM (2008) Mangrove forests: resilience, protection from tsunamis, and responses to global climate change. Estuarine, Coastal and Shelf Science 76(1):1–13\nBarros MLC, daSilva TD, da Cruz AGB et al (2020) Numerical simulation of wetland hydrodynamics andwater quality. Journal of the Brazilian Society of Mechanical Sciences and Engineering 42(444):1–15\nBenz UC, Hofmann P, Willhauck G et al (2004) Multi-resolution, object-oriented fuzzy analysis of remote sensing data for GIS-ready information. ISPRS Journal of Photogrammetry and Remote Sensing 58(3–4):239–258\nBerlanga-Robles CA, Ruiz-Luna A, Bocco G et al (2011) Spatial analysis of the impact of shrimp culture on the coastal wetlands on the northern coast of Sinaloa, Mexico. Ocean and Coastal Management 54(7):535–543\nBullock A, Acreman M (2003) The role of wetlands in the hydrological cycle. Hydrology and Earth System Sciences 7:358–389\nCasanova MT, Brock MA (2000) How do depth, duration and frequency of flooding influence the establishment of wetland plant communities? Plant Ecology 147(2):237–250\nChen YY, Vigouroux G, Bring A et al (2019) Dominant hydro-climatic drivers of water temperature, salinity, and flow variability for the large-scale system of the Baltic coastal wetlands. Water 11:552\nCox BA (2003) A review of currently available in-stream water-quality models and their applicability for simulating dissolved oxygen in lowland rivers. Science of the Total Environment 314-316:335–377\nDonnelly JP, Bertness MD (2001) Rapid shoreward encroachment of salt marsh cordgrass in response to accelerated sea-level rise. Proceedings of the National Academy of Sciences 98(25):14218–14223\nErwin KL (2009) Wetlands and global climate change: the role of wetland restoration in a changing world. Wetlands Ecology and Management 17:71–84\nFan YB, Zhou DM, Ke YH et al (2020) Quantifying the correlated spatial distributions between tidal creeks and coastal wetland vegetation in the Yellow River estuary. Wetlands 40:2701–2711\nGedan KB, Kirwan ML, Wolanski E et al (2011) The present and future role of coastal wetland vegetation inprotecting shorelines: answering recent challenges to the paradigm. Climatic Change 106:7–29\nHammersmark CT, Dobrowski S, Rains MC et al (2010) Simulated effects of stream restoration on herbaceous vegetation distribution. Restoration Ecology 18:882–893\nKeim R, Zoller JA, Braud DWH et al (2013) Classification of forested wetland degradation using ordination of multitemporal reflectance. Wetlands 33(6):1103–1115\nLangevin CD, Swain ED, Wolfert MA (2005) Simulation of integrated surface-water\u002Fground-water flow and salinity for a coastal wetland and adjacent estuary. Journal of Hydrology 314:212–234\nLi X, Bellerby R, Craft C et al (2018) Coastal wetland loss, consequences, and challenges for restoration. Anthropocene Coasts 1:1–15\nLiu J, Engel BA, Dai L et al (2019) Capturing hydrological connectivity structure of wetlands with indices based on graph theory: a case study in Yellow River Delta. Journal of Cleaner Production 239:1–9\nMcClain ME, Boyer EW, Dent CL et al (2003) Biogeochemical hot spots and hot moments at the interface of terrestrial and aquatic ecosystems. Ecosystems 6(4):301–312\nMcKee K, Mendelssohn IA, Materne MD (2004) Acute salt marsh dieback in the Mississippi River deltaic plain: a drought - induced phenomenon? Global Ecology and Biogeography 13(1):65–73\nMitsch WJ, Gosselink JG (2000) Wetlands, 3rd edn. John Wiley & Sons, Inc., NewYork\nQiao HT, Zhang ML, Jiang HZ et al (2018) Numerical study of hydrodynamic and salinity transport processes in the Pink Beach wetlands of the Liao River estuary, China. Ocean Science 14:437–451\nSánchez E, Scordia D, Lino G et al (2015) Salinity and water stress effects on biomass production in different Arundo donaxL. Clones Bioenergy Research 8:1461–1479\nSivaperuman C, Venkatraman C (2015) Coastal and marine bird communities of India. Marine Faunal Diversity in India, 261–281\nSomes NLG, Bishop WA, Wong THF (1999) Numerical simulation of wetland hydrodynamics. Environment International 25(6–7):773–779\nStark J, Plancke Y, Ides S et al (2016) Coastal flood protection by a combined nature-based and engineering approach: modeling the effects of marsh geometry and surrounding dikes. Estuarine, Coastal and Shelf Science 175(20):34–45\nSun ZG, Mou XJ, Sun WL (2016) Potential effects of tidal flat variations on decomposition and nutrient dynamics of Phragmites australis, Suaeda salsa, and Suaeda glauca litter in newly created marshes of the Yellow River estuary, China. Ecological Engineering 93:175–186\nTemmerman S, Bouma TJ, Govers G et al (2005) Impact of vegetation on flow routing and sedimentation patterns: three-dimensional modeling for a tidal marsh. Journal of Geophysical Research 110:F04019. https:\u002F\u002Fdoi.org\u002F10.1029\u002F2005JF000301\nTodd MJ, Muneepeerakul R, Pumo D et al (2010) Hydrological drivers of wetland vegetation community distribution within Everglades National Park. Florida. Advances in Water Resources 33(10):1279–1289\nTwilley RR, Chen R (1998) A water budget and hydrology model of a forest in Rookery Bay. Florida. Marine Freshwater Research 49(4):309–323\nVivian LM, Marshall DJ, Godfree RC (2014) Response of an invasive native wetland plant to environmental flows: implications for managing regulated floodplain ecosystems. Journal of Environmental Management 132:268–277\nWang Y, Liu RH, Gao HW et al (2010) Degeneration mechanism research of Suaeda heteroptera wetland of the Shuangtaizi estuary National Nature Reserve in China. Procedia Environmental Sciences 2:1157–1162\nWester SJ, Grimson R, Minotti PG et al (2018) Hydrodynamic modelling of a tidal delta wetland using an enhanced quasi-2D model. Journal of Hydrology 559:315–326\nXu XL, Zhang Q, Tan ZQ et al (2015) Effects of water-table depth and soil moisture on plant biomass, diversity, and distribution at a seasonally flooded wetland of Poyang Lake, China. Chinese Geographical Science 25:739–756\nZhang Y, Li WH, Sun G et al (2018) Understanding coastal wetland hydrology with a new regional-scale, process-based hydrological model. Hydrological Processes 32(20):3158–3173\nZhao LZ, Chen CS, Vallino J et al (2010) Wetland–estuarine - shelf interactions in the Plum Island sound and Merrimack River in the Massachusetts coast. Journal of Geophysical Research 115:C10039. https:\u002F\u002Fdoi.org\u002F10.1029\u002F2009JC006085",{"VOID":243},"10.1007\u002Fs13157-021-01519-1","PUBLICATION","VERIFIED","2024-05-03T03:31:07.227+00:00","Auto Verify","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs13157-021-01519-1",[250,266],{"id":251,"sortIndex":18,"researcher":17,"roles":252,"affiliations":254,"properties":263,"displayName":265,"givenName":17,"familyName":17},"8ae1267c-de55-4df3-8a49-b0c01f0bb4fb",[253],"AUTHOR",[255],{"id":256,"sortIndex":18,"affiliation":257,"properties":17},"a9e6ecf0-fba9-41ea-a6d0-9c87affd0eb4",{"id":256,"createTime":17,"updateTime":17,"relativeEntities":258,"slug":17,"properties":259,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":262,"statistic":17},[],{"title":260},{"VI":261},"College of Ocean Science and Environment, Dalian Ocean University, Dalian, China",[],{"title":264},{"VI":265},"Yini Wang",{"id":267,"sortIndex":140,"researcher":17,"roles":268,"affiliations":269,"properties":284,"displayName":286,"givenName":17,"familyName":17},"6ba096c8-2397-4c10-b9dd-e05c1b3b8481",[253],[270,276],{"id":256,"sortIndex":18,"affiliation":271,"properties":17},{"id":256,"createTime":17,"updateTime":17,"relativeEntities":272,"slug":17,"properties":273,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":275,"statistic":17},[],{"title":274},{"VI":261},[],{"id":277,"sortIndex":18,"affiliation":278,"properties":17},"42551af4-51b2-4988-9ceb-d1667774f5b3",{"id":277,"createTime":17,"updateTime":17,"relativeEntities":279,"slug":17,"properties":280,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":283,"statistic":17},[],{"title":281},{"VI":282},"State Key Laboratory of Coastal and Offshore Engineering, Dalian University of Technology, Dalian, China",[],{"title":285},{"VI":286},"Mingliang 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wetlands, although limited in their spatial extent, provide many important hydrological and ecological services. There is a need to know existing beaver habitation patterns across mountain wetlands because of emerging interest in using beaver to restore and protect riparian and wetland habitats. However, there exist few inventories of wetlands, or their use as beaver habitat, for any mountain region of North America. We studied the distribution of beaver-impacted mineral wetlands and peatlands in a 7,912 km2 area of the Canadian Rocky Mountains. Using aerial photography and an existing wetland database, we inventoried 529 wetlands at elevations of 1,215 to 2,194 m; peat soils were found at 69 % of the 81 field verified wetlands. Wetland distribution and beaver habitation varied by physiography and jurisdiction. While 75 % of the wetlands identified were located in the foothills region, beaver were twice as likely to inhabit those in the mountain region owing to differences in land use activities and wildlife conservation measures. Wetlands inhabited by beaver had an order of magnitude greater area of open water and 12 times the number of individual open water features than those without. Beaver-enhanced open water extent has far-reaching consequences for wetland ecohydrological and biogeochemical functioning.",{"EN":357},"Distribution of Canadian Rocky Mountain Wetlands Impacted by Beaver",{"VOID":359},"[]",{"VOID":361},"Baldwin J (2013) Problematizing beaver habitat identification models for reintroduction application in the western United States. Yearb Assoc Pac C Geo 75:104–120\nBelyea L, Malmer N (2004) Carbon sequestration in peatlands: patterns and mechanisms of response to climate change. Glob Change Biol 10:1042–1052\nBhat MG, Huffaker RG, Lenhart SM (1993) Controlling forest damage by dispersive beaver populations: centralized optimal management strategy. Ecol Appl 3(3):518–530\nBisson PA, Buffington JM, Montgomery DR (2006) Valley segments, stream reaches, and channel units. 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University of California Press, California, pp 161–172\nJohnston CA, Naiman RJ (1987) Boundary dynamics at the aquaticterrestrial interface: The influence of beaver and geo-morphology. Landscape Ecol 1:47–57\nJohnston C, Naiman R (1990) Aquatic patch creation in relation to beaver population trends. Ecology 71(4):1617–1621\nKrankina ON, Pflugmacher D, Friedl M, Cohen WB, Nelson P, Baccini A (2008) Meeting the challenge of mapping peatlands with remotely sensed data. Biogeosciences 5:1809–1820\nLang M, McCarty G (2009) Lidar intensity for improved detection of inundation below the forest canopy. Wetlands 29(4):1166–1178\nMaxa M, Bolstad P (2009) Mapping northern wetlands with high resolution satellite images and lidar. Wetlands 29(1):248–260\nMessmer T (2000) The emergence of human-wildlife conflict: turning challenges into opportunities. Int Biodeterior Biodegrad 45:97–102\nMilbrath J (2013) Land cover change within the peatlands along the Rocky Mountain Front, Montana: 1937–2009. University of Montana, Thesis\nMitchell CC, Niering WA (1993) Vegetation change in a topogenic bog following beaver flooding. Bull Tor Bot Club 120(2):136–147\nMoore K (2012) Negotiating the middle ground in a world-system: The Niitsitapi (Blackfoot) and Ktunaxa (Kootenai) in the Northern Rocky Mountain Fur Trade. University of Arizona, MSc Thesis\nPastor J, Bonde J, Johnston C, Naiman R (1993) Markovian analysis of the spatially dependent dynamics of beaver ponds. Lect Mathe iLife Sc 23:5–28\nPollock MM, Beechie TJ et al (2014) Using beaver dams to restore incised streams. Bioscience. doi:10.1093\u002Fbiosci\u002Fbiu036\nRacine CH, Walters JC (1994) Groundwater-discharge fens in the Tanana lowlands, interior Alaska, U.S.A. Arct Alp Res 26(4):418–426\nRay AM, Rebertus AJ, Ray HL (2001) Macrophyte succession in Minnesota beaver ponds. Can J Bot 79:487–499\nRebertus AJ (1986) Bogs as beaver habitat on north-central Minnesota. 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In Treatise on Geomorphology – Ecogeomorphology (Butler D, Hupp C, eds.), Elsevier, pp 293–306.\nWieder RK, McCormick AM, Lang GE (1981) Vegetational analysis of Big Run Bog, a nonglaciated Sphagnum bog in West Virginia. Castanea 46(1):16–29\nWolff E, Cooper D, Hobbs N (2007) Hydrologic regime and herbivory stabilize an alternative state in Yellowstone National Park. Ecol Appl 17(6):1572–1587\nWoo M-K, Waddington JM (1990) Effects of beaver dams on sub-arctic wetland hydrology. Arctic 43:223–230\nWright J, Flecker A, Jones C (2003) Local vs. landscape controls on plant species richness in beaver meadows. Ecology 84(12):3162–3173\nYavitt J, Lang G, Sexstone A (1990) Methane fluxes in wetland and forest soils, beaver ponds and low-order streams of a temperate forest ecosystem. J Geophys Res 95(D13):22463–22474\nZoltai SC, Siltanen R, Johnson J (2000) A wetland database for the western boreal subarctic and arctic regions of Canada. Natural Resources Canada, Northern Forestry Centre, Information report NOR-X-386",{"VOID":363},"10.1007\u002Fs13157-014-0595-1","2024-09-05T05:34:28.639+00:00","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs13157-014-0595-1",[367,382,395],{"id":368,"sortIndex":18,"researcher":17,"roles":369,"affiliations":370,"properties":379,"displayName":381,"givenName":17,"familyName":17},"c70db02c-bdb4-4562-96ac-e73f057f5d43",[253],[371],{"id":372,"sortIndex":18,"affiliation":373,"properties":17},"7cc6db3e-3749-48f9-b49b-6c254e4330cc",{"id":372,"createTime":17,"updateTime":17,"relativeEntities":374,"slug":17,"properties":375,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":378,"statistic":17},[],{"title":376},{"VI":377},"Centre for Hydrology and Department of Geography and Planning, University of Saskatchewan, Saskatoon, Canada",[],{"title":380},{"VI":381},"Alasdair Morrison",{"id":383,"sortIndex":140,"researcher":17,"roles":384,"affiliations":385,"properties":392,"displayName":394,"givenName":17,"familyName":17},"0072a14b-4eab-4a96-9746-ff7822f00442",[253],[386],{"id":372,"sortIndex":18,"affiliation":387,"properties":17},{"id":372,"createTime":17,"updateTime":17,"relativeEntities":388,"slug":17,"properties":389,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":391,"statistic":17},[],{"title":390},{"VI":377},[],{"title":393},{"VI":394},"Cherie J. 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the wintering grounds, wetland selection by waterfowl is influenced by spatiotemporal resource distribution. The ring-necked duck (Aythya collaris) winters in the southeastern United States where a disproportionate amount of Atlantic Flyway ring-necked duck harvest occurs. We quantified female ring-necked duck selection for wetland characteristics during and after the 2017–2018 and 2018–2019 waterfowl hunting seasons using discrete choice modeling under a Bayesian framework. Relative probability of selection was primarily influenced by characteristics at the local wetland scale. Relative probability of selection was higher for flooded agriculture and vegetated wetlands than open water and was positively influenced by wetland area during the winter. After the hunting season, the relative probability of selection decreased for flooded agriculture but increased for vegetated wetlands, and the effect of wetland area decreased in magnitude. We attribute changes in selection during and after the hunting season to dietary shifts related to migratory preparation, resource depletion, and reproductive pairing. Understanding the wetland characteristics that wintering waterfowl select, and the spatial scale at which selection occurs, is important for informing effective wetland management and waterfowl harvest practices.",{"EN":479},"Wetland Selection by Female Ring-Necked Ducks (Aythya collaris) in the Southern Atlantic Flyway",{"VOID":481},"[\"1133114164421593997\"]",{"VOID":483},"Anteau MJ, Afton AD (2004) Nutrient reserves of lesser scaup (Aythya affinis) during spring migration in the Mississippi Flyway: a test of the spring condition hypothesis. The Auk 121:917–929\nAnteau MJ, Afton AD (2009) Lipid reserves of lesser scaup (Aythya affinis) migrating across a large landscape are consistent with the “spring condition” hypothesis. 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natural wetlands disappear, constructed wetlands may play vital roles in amphibian conservation. However, previous investigations have concluded that artificial wetlands do not adequately replace lost wildlife habitat. Nevertheless, constructed wetlands serve as breeding habitat for amphibians where extensive natural wetland loss has occurred. To investigate the roles of engineered wetland features on amphibian abundance, we surveyed 49 constructed wetlands throughout northern Missouri. Cricket frogs (Acris crepitans), bullfrogs (Lithobates catesbeianus), and leopard frogs (Lithobates blairi\u002Fsphenocephalus complex) each occurred in over 80% of surveyed wetlands. Salamanders and hylid frogs were rarely encountered. We used an information theoretic approach to examine relationships between individual species and habitat features associated with wetland designs and placements. We found that models incorporating design features of open water ponds best explained abundances of most commonly encountered species. At the placement level, models that included nearby aquatic habitat ranked highest for common species. Salamanders and most hylid frogs responded positively to aquatic vegetative cover but negatively to fish abundance and anthropogenic disturbance-related features in the landscape. Our results indicate that to be effective amphibian conservation tools, constructed wetlands should be fish-free, heavily vegetated, include shallows, and placed within areas of low anthropogenic disturbance.",{"EN":670},"Influences of Design and Landscape Placement Parameters on Amphibian Abundance in Constructed Wetlands",{"VOID":672},"[\"990100549337102674\"]",{"VOID":674},"citation_journal_title=Ecological Letters; citation_title=Indirect facilitation of an anuran invasion by non-native fishes; citation_author=M Adams, C Pearl, R Bury; citation_volume=6; citation_publication_date=2003; citation_pages=343-351; citation_doi=10.1046\u002Fj.1461-0248.2003.00435.x; citation_id=CR1\ncitation_title=An evaluation of compensatory mitigation projects permitted under Clean Water Act Section 401 by the Los Angeles Regional Quality Control Board, 1991–2002; citation_publication_date=2004; citation_id=CR2; citation_author=R Ambrose; citation_author=S Lee; citation_publisher=California State Water Resources Control Board\ncitation_journal_title=Conservation Biology; citation_title=Suitability of golf course ponds for amphibian metamorphosis when bullfrogs are removed; citation_author=M Boone, R Semlitsch, C Mosby; citation_volume=22; citation_publication_date=2008; citation_pages=172-179; citation_doi=10.1111\u002Fj.1523-1739.2007.00817.x; citation_id=CR3\ncitation_journal_title=Conservation Biology; citation_title=Value of artificial habitats for amphibian reproduction in altered landscapes; citation_author=A Brand, J Snodgrass; citation_volume=24; citation_publication_date=2010; citation_pages=295-301; citation_doi=10.1111\u002Fj.1523-1739.2009.01301.x; citation_id=CR4\ncitation_title=Model selection and multimodel inference: a practical information-theoretic approach; citation_publication_date=2002; citation_id=CR5; citation_author=K Burnham; citation_author=D Anderson; citation_publisher=Springer-Verlag\ncitation_title=Wetlands losses in the United States, 1780′s to 1980′s; citation_publication_date=1990; citation_id=CR6; citation_author=T Dahl; citation_publisher=U.S. Fish and Wildlife Service\ncitation_title=Status and trends of wetlands in the conterminous United States 1999–2004; citation_publication_date=2006; citation_id=CR7; citation_author=T Dahl; citation_publisher=U.S. Dept. of the Interior, Fish and Wildlife Service\nDaniel R, Edmond B (2010) Atlas of Missouri amphibians and reptiles for 2009. \n                    http:\u002F\u002Fatlas.moherp.org\u002Fpubs\u002Fatlas09.pdf\n                    \n                  . 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interdisciplinary approach to research in wetlands is necessary to avoid incorrect extrapolations and projections about broad wetland functiors based on limited knowledge. The values of several lesser-used disciplines or fields of study are often overlooked and therefore not incorporated into study designs. To address this problem, a model was developed that relates ten ecological and environmental science disciplines to each other (geohydrology, surface water hydrology, water chemistry, soil\u002Fsediment chemistry, stratigraphy\u002Fsedimentology, paleoecology, plant ecology, animal ecology, remote sensing, and seedbank studies). A matrix and compartmentalized model cross-identify each discipline as a research tool and as a type of study for which a given tool can be used in data collection. Use of the model is demonstrated by assessing the research approach utilized in the study of three wetland systems (shallow dune ponds, bog, fen) at Indiana Dunes National Lakeshore and the study of the pocosin wetlands as presented in a comprehensive volume on that subject.",{"EN":820},"A model for assessing interdisciplinary approaches to wetland research",{"VOID":822},"[\"1382555188355962505\"]",{"VOID":824},"Andrus, R.E. and D.A. Wilcox. 1985. New records for Sphagnum in Indiana. Michigan Botanist 24: 147–152.\nApfelbaum, S.I., K.A. Heiman, and J.A. Probes. 1983. Ecological condition and management opportunity for the Great Marsh system, Indiana Dunes National Lakeshore. Report to Indiana Dunes National Lakeshore, 60 pp.\nArihood, L.D. 1975. Water-quality assessment of the Indiana Dunes National Lakeshore, 1973–74. U.S. Geological Survey Water-Resources Investigations Report 14-75. 56 pp.\nBoelter, D. H. 1978. An appraisal of the organic deposits in the interdunal wetlands of the Indiana Dunes National Lakeshore. Special Report SDA-Forest Service, Washington. 15 pp.\nCampbell, R. G. and J. H. Hughes. 1981. Forest management systems in North Carolina pocosins: Weyerhaeuser, p. 199–213.In C. J. Richardson (ed.) Pocosin Wetlands. Hutchinson Ross Publishing Company, Stroudsburg, PA. 364 pp.\nCarter, V. and R. Stottlemyer. 1978. Ecology of Cowles Bog Wetland Complex. Indiana Dunes National Lakeshore Special Study. National Park Service, Porter, Indiana. 38 pp.\nChristensen, N., R. Burchell, A. Liggett, and E. Simms. 1981. The structure and development of pocosin vegetation, p. 43–61.In C. J. Richardson (ed.) Pocosin Wetlands. Hutchinson Ross Publishing Company. Stroudsburg, PA. 364 pp.\nCohen, D. A. and R. J. Shedlock. 1986. Shallow ground-water flow, water levels, and quality of water, 1980–1984, Cowles Unit, Indiana Dunes National Lakeshore. U.S. Geological Survey Water-Resources Investigations Report 85-4340. 25 pp.\nDaniel III, C. 1981. Hydrology, geology, and soils of pocosins: a comparison of natural and altered systems, p. 69–108.In Richardson (ed.) Pocosin Wetlands. Hutchinson Ross Publishing Company, Stroudsburg, PA. 364 pp.\nFutyma, R.P. 1985. Palcobotanical studies at Indiana Dunes National Lakeshore. National Park Service, Porter, Indiana, USA. 242 pp.\nGilliam, J.W. and R.W. Skaggs. 1981. Drainage and agricultural development: effects on drainage waters, p. 109–124.In Richardson (ed.) Pocosin Wetlands. Hutchinson Ross Publishing Company, Stroudsburg, PA. 364 pp.\nGillies, D.C. and W.W. Lapham. 1980. Reassessment of the effects of construction dewatering on ground water levels in the Cowles Unit. Indiana Dunes National Lakeshore, Indiana. Supplement to Geological Survey Water-Resources Investigations 78–138. U.S. Geological Survey Open-File Report 80-1105. 50 pp.\nHardy, M. A. 1981. Effects of coal fly-ash disposal on water quality in and around the Indiana Dunes National Lakeshore, Indiana. U.S. Geological Survey Water-Resources Investigations Report 81-16. 64 pp.\nHendrickson, W. H. and D. A. Wilcox. 1979. Relationship between some physical properties and the vegetation found in Cowles Bog National Landmark, Indiana. Proceedings of Second Conference on Scientific Research on the National Parks 5: 642–666.\nJackson, S.T., R.P. Futyma, and D.A. Wilcox. 1988. A paleoecological test of a classical hydrosere in the Lake Michigan dunes. Ecology 69: (in press).\nMarie, J. R. 1976. Model analysis of effects on water levels at Indiana Dunes National Lakeshore caused by construction dewatering. U.S. Geological Survey Water-Resources Investigations Report 76-82. 32 pp.\nMeyer, W. and P. Tucci. 1978. Effects of seepage from fly-ash settling ponds and construction dewatering on ground-water levels in the Cowles Unit, Indiana Dunes National Lakeshore, Indiana. U.S. Geological Survey Water-Resources Investigations Report 78-138. 95 pp.\nMiller, B. B. and T. A. Thompson. 1987. Molluscan faunal changes in the Cowles Bog area (Indiana Dunes National Lakeshore) following the low-water Lake Chippewa phase.In A.F. Schneider, and G. S. Fraser (eds.) Geological Society of America Special Paper (in press).\nMonschein, T. 1981. Values of pocosins to game and fish species in North Carolina, p. 155–170. In C. J. Richardson (ed.) Pocosin Wetlands. Hutchinson Ross Publishing Company, Stroudsburg, PA. 364 pp.\nPatterson, J. C. and D. G. Fenn. 1978. A report on the analyses of selected soil substrates from Indiana Dunes National Lakeshore. Indiana Dunes National Lakeshore Special Study. National Park Service, Porter, Indiana. 88 pp.\nRichardson, C. J. (ed.) 1981. Pocosin Wetlands. Hutchinson Ross Publishing Company, Stroudsburg, PA. 364 pp.\nRichardson, C.J., R. Evans, and D. Carr. 1981. Pocosins: an ecosystem in transition. p. 3–19.In C. J. Richardson (ed.) Pocosin Wetlands. Hutchinson Ross Publishing Company, Stroudsburg, PA. 364 pp.\nTexas Instruments Ecological Services, Inc. 1974-1981. Annual Reports. Bailly Nuclear-1 Site. Northern Indiana Public Service Company. Texas Instruments, Inc, Dallas.\nThompson, T.A. 1986. Sedimentology, internal architechture, and depositional history of the Indiana Dunes National Lakeshore and State Park. Ph.D. Thesis. Indiana University, Bloomington, Indiana.\nTitlow, B. 1986. Vegetation mapping of Indiana Dunes National Lakeshore. Indiana Dunes National Lakeshore special study. National Park Service, Porter, Indiana.\nWhitehead, D. R. 1972. Developmental and environmental history of the Dismal Swamp. Ecological Monographs 42: 301–315.\nWhitman, R. L., R. L. Peloquin, and R. J. Werth. 1986. Ecology of Miller Woods, Indiana Dunes National Lakeshore. National Park Service, Porter Indiana. 231 pp.\nWilbur, H. 1981. Pocosin fauna. p. 62–68.In C.J. Richardson (ed.) Pocosin Wetlands. Hutchinson Ross Publishing Company, Stroudsburg, PA. 364 pp.\nWilcox, D. A. 1979. Salt intrusion at Pinhook Bog, Indiana Dunes National Lakeshore. Proceedings of the Second Conference on Scientific Research in the National Parks 5: 618–641.\nWilcox, D. A. 1982. The effects of deicing salts on water chemistry and vegetation in Pinhook Bog, Indiana. Ph.D. dissertation. Purdue University, 139 pp.\nWilcox, D. A. 1984. The effects of NaCl deicing salts on Sphagnum recurvum P. Beauv. Environmental and Experimental Botany 24: 295–304.\nWilcox, D. A. 1986a. The effects of deicing salts on water chemistry in Pinhook Bog, Indiana. Water Resources Bulletin 22: 57–65.\nWilcox, D. A. 1986b. The effects of deicing salts on vegetation in Pinhook Bog, Indiana. Canadian Journal of Botany 64: 865–874.\nWilcox, D.A. and R.E. Andrus. 1987. The role ofSphagnum fimbriatum in secondary succession in a road-salt impacted bog. Canadian Journal of Botany 65: (in press).\nWilcox, D.A., S.I. Apfelbaum, and R.D. Hiebert. 1984. Cattail invasion of sedge meadows following hydrologic disturbance in the Cowles Bog Wetland Complex, Indiana Dunes National Lakeshore. Wetlands 4:115–128.\nWilcox, D. A. and R. W. Buchholz. 1986. Vegetation restoration in a road-salt impacted bog. Restoration and Management Notes 4(1): 28.\nWilcox, D. A., R. P. Futyma and R. J. Shedlock. 1985. The hydrogeological and vegetational development of wetlands in the Cowles Bog Wetland Complex, Indiana Dunes National Lakeshore. Bulletin of the Ecological Society of America 66(2): 294.\nWilcox, D. A., R. J. Shedlock, and W. H. Hendrickson. 1986. Hydrology, water chemistry, and ecological relations in the raised mound of Cowles Bog. Journal of Ecology 74: 1103–1117.\nWilcox, D. A. and H. A. Simonin. 1987. A chronosequence of aquatic macrophyte communities in dune ponds. Aquatic Botany 28: (in press).\nWilcox, D.A., H.A. Simonin, and J. Alden. 1984. The stratigraphy and development of Pinhook Bog. Program of the Fifth Annual Meeting of the Society of Wetland Scientists, p. 24–25.\nWilhelm, G. S. 1980. Report on the special vegetation of the Indiana Dunes National Lakeshore. INDU Research Program Report 80-01. 262 pp.",{"VOID":826},"10.1007\u002FBF03160801","2024-05-16T10:30:37.038+00:00","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002FBF03160801",[830],{"id":831,"sortIndex":18,"researcher":17,"roles":832,"affiliations":833,"properties":842,"displayName":844,"givenName":17,"familyName":17},"eb0f9732-87e2-4836-a6a3-e9b1ee58ca6e",[253],[834],{"id":835,"sortIndex":18,"affiliation":836,"properties":17},"382248a2-5dc3-4c31-9bef-9a24e911ab52",{"id":835,"createTime":17,"updateTime":17,"relativeEntities":837,"slug":17,"properties":838,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":841,"statistic":17},[],{"title":839},{"VI":840},"National Park Service, Indiana Dunes National Lakeshore, Porter, Indiana",[],{"title":843},{"VI":844},"Douglas A. Wilcox",{"url":828,"publisher":846,"properties":894},{"id":6,"createTime":7,"updateTime":8,"relativeEntities":847,"slug":10,"properties":848,"entityType":15,"verifyStatus":16,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":18,"subjectFields":851,"manageAffiliations":863,"indexDatabases":874,"url":17,"thumbnailPath":17,"statistic":889,"gsStatistic":17,"type":220,"analyzePriority":17},[],{"issn":849,"title":850},{"VOID":13},{"EN":10},[852,855,859],{"id":21,"createTime":17,"updateTime":17,"relativeEntities":853,"label":854,"description":17,"parentId":17,"standard":17,"scholarHubFieldId":17},[],{"EN":24},{"id":26,"createTime":17,"updateTime":17,"relativeEntities":856,"label":857,"description":858,"parentId":17,"standard":17,"scholarHubFieldId":17},[],{"EN":29},{},{"id":32,"createTime":17,"updateTime":17,"relativeEntities":860,"label":861,"description":862,"parentId":17,"standard":17,"scholarHubFieldId":17},[],{"EN":35},{},[864,869],{"id":39,"createTime":17,"updateTime":17,"relativeEntities":865,"slug":17,"properties":866,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":868,"statistic":17},[],{"title":867},{"EN":43},[],{"id":46,"createTime":17,"updateTime":17,"relativeEntities":870,"slug":17,"properties":871,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":873,"statistic":17},[],{"title":872},{"EN":50},[52],[875,882],{"id":55,"indexDatabase":876,"url":66,"indexYears":67,"academicFieldIds":881,"indexDatabaseRanking":72},{"id":57,"createTime":17,"updateTime":17,"relativeEntities":877,"label":878,"description":879,"key":63,"publicationTags":880,"standard":17},[],{"EN":60,"VI":60},{"EN":60,"VI":62},[65],[69,70,71],{"id":74,"indexDatabase":883,"url":87,"indexYears":17,"academicFieldIds":888,"indexDatabaseRanking":17},{"id":76,"createTime":17,"updateTime":17,"relativeEntities":884,"label":885,"description":886,"key":83,"publicationTags":887,"standard":17},[],{"EN":79,"VI":79},{"EN":81,"VI":82},[85,86],[89,90],{"impactFactor":18,"impactFactorByYear":890,"i10Index":102,"i10IndexLast5Year":103,"totalPublication":104,"totalPublicationByYear":891,"totalCitation":137,"totalCitationByYear":892,"totalCitationPerPublication":176,"totalCitationPerPublicationByYear":893,"hindexLast5Year":219,"hindex":219},{"2012":93,"2013":94,"2014":95,"2015":96,"2016":97,"2017":98,"2018":99,"2019":94,"2020":100,"2021":95,"2022":98,"2023":101},{"1981":106,"1982":103,"1983":107,"1984":107,"1985":107,"1986":108,"1987":109,"1988":110,"1989":111,"1990":103,"1991":112,"1992":113,"1993":113,"1994":114,"1995":115,"1996":116,"1997":117,"1998":118,"1999":119,"2000":118,"2001":120,"2002":121,"2003":122,"2004":123,"2005":124,"2006":125,"2007":126,"2008":126,"2009":127,"2010":125,"2011":128,"2012":129,"2013":130,"2014":131,"2015":129,"2016":132,"2017":127,"2018":127,"2019":133,"2020":134,"2021":135,"2022":129,"2023":136,"2024":115},{"1981":108,"1982":139,"1983":140,"1984":115,"1985":141,"1988":142,"1989":120,"1990":106,"1991":143,"1992":144,"1993":145,"1994":146,"1995":147,"1996":148,"1997":149,"1998":150,"1999":151,"2000":152,"2001":153,"2002":154,"2003":155,"2004":156,"2005":157,"2006":158,"2007":159,"2008":160,"2009":161,"2010":162,"2011":163,"2012":164,"2013":165,"2014":166,"2015":167,"2016":168,"2017":169,"2018":170,"2019":147,"2020":171,"2021":172,"2022":173,"2023":174,"2024":175},{"1981":178,"1982":179,"1983":180,"1984":181,"1985":182,"1988":183,"1989":184,"1990":185,"1991":186,"1992":187,"1993":188,"1994":189,"1995":190,"1996":191,"1997":192,"1998":193,"1999":194,"2000":195,"2001":196,"2002":197,"2003":198,"2004":199,"2005":200,"2006":201,"2007":202,"2008":194,"2009":203,"2010":204,"2011":205,"2012":206,"2013":207,"2014":208,"2015":209,"2016":210,"2017":211,"2018":212,"2019":213,"2020":214,"2021":215,"2022":216,"2023":217,"2024":218},{"pages":895,"volume":897},{"VOID":896},"39-49",{"VOID":898},"7",{"total":18,"publishYear":900,"statisticByYear":901},1987,{},"1987-12-01","DONE_ANALYZE_CITATION","2026-07-30T12:00:46.769+00:00",[85,72],{"id":907,"createTime":908,"updateTime":909,"relativeEntities":910,"slug":911,"properties":912,"entityType":244,"verifyStatus":245,"verifyTime":923,"verifyNote":247,"languages":17,"translateLanguages":17,"viewCount":18,"primaryUrl":924,"fullTextUrl":17,"authors":925,"publicationType":287,"publisherRelationship":1010,"citationCount":1064,"citationInfo":1065,"publishDate":1069,"publishYear":1066,"citationAnalyzeStatus":903,"lastCitationAnalyze":1070,"indexDatabases":1071,"openAccess":17,"references":17,"isForceReanalyzing":346},"d170f0ea-7e78-4d88-8157-ced42b739221","2024-02-10T14:12:15.381+00:00","2026-07-26T16:06:00.451+00:00",[],"A-comparison-of-the-vegetation-and-soils-of-natural-restored-and-created-coastal-lowland-wetlands-in-Hawai-i",{"abstract":913,"title":915,"gsPaper":917,"references":919,"doi":921},{"EN":914},"The loss of coastal wetlands throughout the Hawaiian Islands has increased the numbers of created (CW) and restored (RW) wetlands. An assessment of these wetlands has yet to occur, and it has not been determined whether CWs and RWs provide the same functions as natural wetlands (NWs). To address these concerns, vegetation and soil characteristics of 35 wetlands were compared within sites along hydrologic gradients and among sites with different surface water salinity and status (i.e., CW, RW, NW). Only 16 of 85 plant species identified were native and three of the four most abundant species were exotic. Vegetative characteristics differed primarily across salinity classes, then along hydrologic zones, and to a lesser extent among CWs, RWs, and NWs. Soil properties exhibited fewer differences across salinity classes and along hydrologic zones and greater differences among CWs, RWs, and NWs. The dominant presence of invasive species in coastal Hawaiian wetlands suggests that it will be difficult to locate reference sites that can be used as restoration targets. Differences in edaphic characteristics suggested that RWs\u002FCWs do not exhibit the same functions as NWs. Future restoration and creation should include planting of native vegetation, controlling invasive vegetation, and alleviating inadequate soil conditions.",{"EN":916},"A comparison of the vegetation and soils of natural, restored, and created coastal lowland wetlands in Hawai‘i",{"VOID":918},"[\"2677421705362509725\"]",{"VOID":920},"Allen, J. A. 1998. Mangroves as alien species: the case of Hawai’i. Global Ecology and Biogeography Letters 7: 61–71.\nAOAC International. 1997. Official Methods of Analysis of AOAC International, 16th Edition. AOAC International, Arlington, VA, USA.\nBalcombe, C. K., J. T. Anderson, R. H. Fortney, J. S. Rentch, W. N. Grafton, and W. S. Kordek. 2005. A comparison of plant communities in mitigation and reference wetlands in the mid-Appalachians. Wetlands 25: 130–42.\nBaldwin, A. H., K. L. McKee, and I. A. Mendelssohn. 1996. The influence of vegetation, salinity, and inundation on seed banks or oligohaline coastal marshes. American Journal of Botany 83: 470–79.\nBishel-Machung, L. R., P. Brooks, S. S. Yates, and K. L. Hoover. 1996. Soil Properties of reference wetlands and wetland creation projects in Pennsylvania. Wetlands 16: 532–41.\nBrinson, M. M. and R. Rheinhardt. 1996. The role of reference wetlands in functional assessment and mitigation. Ecological Applications 6: 69–76.\nBruland, G. L. 2008. Coastal wetlands: function and role in reducing impact of land-based management. p. 85–124.In A. Fares and A. I. Al-Kadi (eds.) Coastal Watershed Management. WIT Press, Southhampton, UK.\nBruland, G. L., M. F. Hanchey, and C. J. Richardson. 2003. Effects of agriculture and wetland restoration on hydrology, soils, and water quality of a Carolina Bay complex. Wetlands Ecology and Management 11: 141–56.\nBruland, G. L. and C. J. Richardson. 2004. Hydrologic gradient and topsoil additions affect soil properties of Virginia created wetlands. Soil Science Society of America Journal 68: 2069–77.\nBruland, G. L. and C. J. Richardson. 2005. Spatial variability of soil properties in created, restored, and paired natural wetlands. Soil Science Society of America Journal 69: 273–84.\nBruland, G. L. and C. J. Richardson. 2006. Comparison of soil organic matter in created, restored, and paired natural wetlands in North Carolina. Wetlands Ecology and Management 14: 245–51.\nCampbell, D. A., C. A. Cole, and R. P. Brooks. 2002. A comparison of created and natural wetlands in Pennsylvania, USA. Wetlands Ecology and Management 10: 41–49.\nCowardin, L. M., V. Carter, F. C. Golet, and E. T. LaRoe. 1979. Classification of Wetlands and Deepwater Habitats of the United States. U.S. Department of the Interior, Fish and Wildlife Service, Office of Biological Services, FWS\u002FOBC-79\u002F 31, Washington DC, USA.\nCraft, C. B., S. Broome, and C. Campbell. 2002. Fifteen years of vegetation and soil development after brackish-water marsh creation. Restoration Ecology 10: 248–58.\nCraft, C. B., S. Broom, and E. D. Seneca. 1988. Nitrogen, phosphorus and organic carbon pools in natural and transplanted marsh soils. Estuaries 11: 272–80.\nCuiddihy, L. W. and C. P. Stone. 1990. Alteration of native Hawaiian vegetation: effects of humans, their activities, and introductions. University of Hawaii Cooperative National Parks Resources Studies Unit, Honolulu, HI, USA.\nDahl, T. E. 1990. Wetlands losses in the United States 1790’s to 1980’s. U.S. Department of the Interior, Fish and Wildlife Service, Washington, DC, USA.\nEnvironmental Laboratory. 1987. Corps of Engineers Wetland Delineation Manual. Technical Report Y-8-1. U.S. Army Engineer Waterways Experiment Station, Vicksburg, MS, USA.\nErickson, T. and C. Puttock. 2006. Hawaii Wetlands Field Guide: An Ecological and Identification Guide to Wetlands and Wetland Plants of the Hawaiian Islands. Bess Press Books, Honolulu, HI, USA.\nErvin, G. N., B. N. Herman, J. T. Bried, and D. C. Holly. 2006. Evaluating non-native species and wetlands indicator status as components of wetlands floristic assessment. Wetlands 26: 1114–29.\nFearnley, S. 2008. The soil physical and chemical properties of restored and natural back-barrier salt marsh on Isles Dernieres, Louisiana. Journal of Coastal Research 24: 84–94.\nFennessy, S. and J. Roehrs. 1997. A functional assessment of mitigation wetlands in Ohio: comparisons with natural systems. Ohio Environmental Protection Agency, Division of Surface Waters, Columbus, OH, USA.\nFrazer, T. K., S. K. Notestein, C. A. Jacoby, C. J. Littles, S. R. Keller, and R. A. Swett. 2006. Effects of storm-induced salinity changes on submerged aquatic vegetation in Kings Bay, Florida. Estuaries and Coasts 29: 943–53.\nHeaven, J. B., F. E. Gross, and A. T. Gannon. 2003. Vegetation comparison of natural and a created emergent marsh wetlands. Southeastern Naturalist 2: 195–206.\nHogan, D. M., T. E. Jordan, and M. R. Walbridge. 2004. Phosphorus retention and soil organic carbon in restored and natural freshwater wetlands. Wetlands 24: 573–85.\nHogan, D. M. and M. R. Walbridge. 2007. Urbanized and nutrient retention in freshwater riparian wetlands. Ecological Applications 17: 1142–55.\nHoward, R. J. and I. A. Mendelssohn. 1999. Salinity as a constraint on growth of oligohaline marsh macrophytes. I. Species variation in stress tolerance. American Journal of Botany 86: 785–94.\nHue, N. V., R. Uchida, and M. C. Ho. 2000. Sampling and analysis of soils and plant tissues: how to take representative samples, how the samples are tested. p. 23–30.In J. A. Silva and R. S. Uchida (eds.) Plant Nutrient Management in Hawaii Soils: Approaches for Tropical and Subtropical Agriculture. CTAHR, University of Hawaii Manoa, Honolulu, HI, USA.\nKent, M. and P. Coker. 1992. Vegetation Description and Analysis: A Practical Approach. CRC Press, Inc., Boca Raton, FL, USA.\nKentula, M. E. 2000. Perspectives on setting success criteria for wetlands restoration. Ecological Engineering 15: 199–209.\nKentula, M. E., S. E. Gwin, and S. M. Pierson. 2004. Tracking changes in wetlands with urbanization: sixteen years of experience in Portland, Oregon, USA. Wetlands 24: 734–43.\nKosaka, E. 1990. Technical review of draft report, wetland losses in the United States 1780’s to 1980’s. U.S. Department of the Interior, Fish and Wildlife Service, Washington, DC, USA.\nLangis, R., M. Zalejko, and J. B. Zedler. 1991. Nitrogen assessments in a constructed and natural salt marsh of San Diego Bay. Ecological Applications 1: 40–51.\nMcCune, B. and J. B. Grace. 2002. Analysis of Ecological Communities. MjM Software Design, Gleneden Beach, OR, USA.\nMitsch, W. J. and J. G. Gosselink. 2007. Wetlands, 4th edition. John Wiley & Sons, Inc., New York, NY, USA.\nMoore, H. H., W. A. Niering, L. J. Marsicano, and M. Dowdell. 1999. Vegetation change in created emergent wetlands (1988–1996) in Connecticut (USA). Wetland Ecology and Management 7: 177–91.\nOlsen, S. R. and L. E. Sommers. 1982. Phosphorus. p. 403–30.In A. L. Page, R. H. Miller, and D. R. Keeney (eds.) Methods of Soil Analysis: Part 2. SSSA Inc., Madison, WI, USA.\nReinartz, J. A. and E. L. Warne. 1993. Development of vegetation in small created wetlands in Southeastern Wisconsin. Wetlands 13: 153–64.\nRauzon, M. J. and D. C. Drigot. 2002. Red mangrove eradication and pickelweed control in a Hawaiian wetland, waterbird responses, and lessons learned. p. 240–48.In C. R. Veitch and M. N. Clout (eds.) Turning the Tide: The Eradication of Invasive Species. IUCN SSC Invasive Species Specialist Group, IUCN, Gland, Switzerland and Cambridge, UK.\nSeabloom, E. W. and A. G. van der Valk. 2003. Plant diversity, composition, and invasion of restored and natural prairie pothole wetlands: Implications for restoration. Wetlands 23: 1–12.\nShaffer, P. W. and T. L. Ernst. 1999. Distribution of soil organic matter in freshwater emergent open water wetlands in Portland, Oregon metropolitan area. Wetlands 19: 505–16.\nSpieles, D. J. 2005. Vegetation development in created, restored, and enhanced mitigation wetlands banks if the United Stated. Wetlands 25: 51–63.\nStarr, F. and K. Starr. 2007. Plants of Hawaii. Available online at \u003Chttp:\u002F\u002Fwww.hear.org\u002Fstarr\u002Fhiplants\u002F>\u002F.\nStauffer, A. L. and R. P. Brooks. 1997. Plant and soil responses to salvages marsh surface and organic matter amendments at a created wetland in central Pennsylvania. Wetlands 17: 90–105.\nStedman, S. and J. Hanson. 2007. Part one: Wetlands, Fisheries, and Economics in the Pacific Coastal States.In Habitat Connections: Wetlands Fisheries and Economics. Department of Commerce, National Marine Fisheries Service, Available online at http:\u002F\u002Fwww.nmfs.noaa.gov\u002Fhabitat\u002Fhabitatconservation\u002F publications\u002Fhabitatconnections\u002Fhabitatatconnections.htm.\nStolt, M. H., M. H. Genthner, W. Lee Daniels, V. A. Groover, S. Nagle, and K. C. Haering. 2000. Comparison of soil and other environmental conditions in constructed and adjacent palustrine reference wetlands. Wetlands 20: 671–83.\nTan, K. H. 1996. Soil Sampling, Preparation, and Analysis. Marcel Dekker, Inc., New York, NY, USA.\nUSDA and NRCS. 2008. The PLANTS Database: Wetland Indicator Status. Available online at http:\u002F\u002Fplants.usda.gov\u002F wetland.html.\nWhistler, W. A. 1994. Wayside Plants of the Islands: A Guide to the Lowland Flora of the Pacific Islands. Isle Botanica, Honolulu, HI, USA.\nWilke, B. M. 2005. Determination of chemical and physical soil properties. p. 74–76.In R. Margensin and F. Schinner (eds.) Manual of Soil Analysis: Monitoring and Assessing Bioremediation. Springer, Heidelberg, Germany.\nZampella, R. A. and K. J. Laidig. 2003. Functional equivalency of natural and excavated coastal plain ponds. Wetlands 23: 860–76.\nZedler, J. B. 1996. Ecological issues in wetlands mitigation: an introduction to the forum. Ecological Application 6: 33–37.\nZedler, J. B. and J. C. Callaway. 1999. Tracking wetland restoration: do mitigation sites follow desired trajectories? Restoration Ecology 7: 69–73.\nZedler, J. B. and S. Kercher. 2004. Causes and consequences of invasive plants in wetlands: opportunities, opportunists, and outcomes. Critical Reviews in Plant Science 23: 431–52.",{"VOID":922},"10.1672\u002F08-127.1","2024-06-24T23:50:42.810+00:00","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1672\u002F08-127.1",[926,950,963,980,995],{"id":927,"sortIndex":18,"researcher":17,"roles":928,"affiliations":929,"properties":947,"displayName":949,"givenName":17,"familyName":17},"3557069a-22ca-42b7-9aa7-dbb1d331f3d8",[253],[930,938],{"id":931,"sortIndex":18,"affiliation":932,"properties":17},"cb7b7f33-9a01-4efa-abd8-3dbaa01dad2a",{"id":931,"createTime":17,"updateTime":17,"relativeEntities":933,"slug":17,"properties":934,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":937,"statistic":17},[],{"title":935},{"VI":936},"Department of Natural Resources Environmental Management, University of Hawai’i, Honolulu, USA",[],{"id":939,"sortIndex":140,"affiliation":940,"properties":946},"926b7403-1dc5-4199-96bc-0901161f30de",{"id":939,"createTime":17,"updateTime":17,"relativeEntities":941,"slug":17,"properties":942,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":945,"statistic":17},[],{"title":943},{"VI":944},"U.S. Army Corps of Engineers Honolulu District, Fort Shafter, USA",[],{},{"title":948},{"VI":949},"Meris Bantilan-Smith",{"id":951,"sortIndex":140,"researcher":17,"roles":952,"affiliations":953,"properties":960,"displayName":962,"givenName":17,"familyName":17},"9dd9ffd7-2428-4889-9c3d-7111e7022413",[253],[954],{"id":931,"sortIndex":18,"affiliation":955,"properties":17},{"id":931,"createTime":17,"updateTime":17,"relativeEntities":956,"slug":17,"properties":957,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":959,"statistic":17},[],{"title":958},{"VI":936},[],{"title":961},{"VI":962},"Gregory L. 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often show patterns of small-scale topographic self-organization, such as hummock and hollow assemblages. When attempting to characterize peatland pore-water quality, little attention is typically paid to the micro-site characteristics of the sampling location, or only one microtopographical form is sampled for consistency. However, no information exists regarding whether or not these microtopographic landforms exert a direct influence over, or are influenced by, the chemistry of peat pore waters beneath them. As part of a larger study examining the role of peatlands in catchment-scale methylmercury cycling, the pore waters beneath several peatland microtopographical landforms were sampled for methylmercury. Porewater methylmercury (MeHg) concentrations at the water table followed the trend: Shallow Hollow > Lawn > Hummock > Deep Hollow, with the shallow hollows having pore-water methylmercury concentrations over 3.5 times higher than that found in deep hollows. There was no significant difference in MeHg concentrations in pore waters from −25 cm. More detailed profiles of MeHg, sulfate and DOC concentrations, and pH in a poor fen shallow and deep hollow and a raised bog hollow show strong differences in porewater solute chemistry, suggesting a complex interplay among hydrology, biogeochemistry, and microtopography. Evidence of wide variation in pore-water quality between sites and over time has significant implications for the sampling approaches used to characterize peatland pore-water chemistry.",{"EN":1082},"Does microtopography influence subsurface pore-water chemistry? Implications for the study of methylmercury in peatlands",{"VOID":1084},"[\"11962859806292211214\"]",{"VOID":1086},"Benoit, J. M., C. C. Gilmour, and R. P. Mason. 1999. Estimation of mercury-sulfide speciation in sediment pore waters using octanol-water partitioning and implications for availability to methylating bacteria. Environmental Toxicology and Chemistry 18:138–2141.\nBloom, N. S. and W. F. Fitzgerald. 1988. Determination of volatile mercury species at the picogram level by low temperature gas chromatography with cold-vapor atomic fluorescence detection. Analytica Chimica Acta 208:151–161.\nBranfireun, M. 2000. The role of decomposing plant litter in methylmercury cycling in a boreal poor fen. M.Sc. Thesis. McGill University, Montreal, Quebec, Canada.\nBranfireun, B. A., A. Heyes, and N. T. Roulet. 1996. The hydrology and methylmercury dynamics of a Precambrian Shield headwater peatland, Water Resources Research 32:1785–1974.\nBranfireum, B. A. and N. T. Roulet. 2002. Controls on the fate and transport of methylmercury in a boreal headwater catchment, northwestern Ontario. Hydrology and Earth Systems Science. 6: 785–794.\nBranfireun, B. A., N. T. Roulet, C. A. Kelly, and J. W. M. Rudd. 1999. In situ sulphate stimulation of mercury methylation in a boreal peatland: toward a link between acid rain and methylmercury contamination in remote environments. Global Biogeochemical Cycles 13:743–750.\nFoster, D. R., G. A. King, P. H. Glaser, and H. E. Wright. 1983. Origin of string patterns in boreal peatlands. Nature 306:256–258.\nGilmour, C. C., G. S. Riedel, M. C Ederington, J. T. Bell, J. M. Benoit, G. A. Gill, and M. C. Stordal. 1998. Methylmercury concentrations and production rates across a trophic gradient in the northern Everglades. Biogeochemistry 40:327–345.\nHeyes, A., T. R. Moore, J. W. M. Rudd, and J. J. Dugoua. 2000. Methyl mercury in pristine and impounded boreal peatlands, Experimental Lakes Area, Ontario, Canadian Journal of Fisheries and Aquatic Sciences. 57:2211–2222.\nHorvat, M., N. S. Bloom, and L. Liang. 1993. Comparison of distillation with other current isolation methods for the determination of methyl mercury compounds in low level environmental samples. Part 1. Sediments. Analytica Chimica Acta 281:135–152.\nHunt, R. J., D. P. Krabbenhoft, and M. P. Anderson. 1997. Assessing hydrogeochemical heterogeneity in natural and constructed wetlands. Biogeochemistry 39:271–293.\nKing, J. K., J. E. Kostka, M. E. Frischer, F. M. Saunders, and J. A. Jahnke. 2001. A quantitative relationship that demonstrates mercury methylation rates in marine sediments are based on the community composition and activity of sulfate-reducing bacteria. Environmental Science and Technology 35:2491–2496.\nKolka, R. K., D. F. Grigal, E. S. Verry, and E. A. Nater. 1999. Mercury and organic carbon relationships in streams draining forested upland\u002Fpeatland watersheds. Journal of Environmental Quality 28:766–775.\nKrabbenhoft, D. P., J. P. Hurley, M. L. Olson, and L. B. Cleckner. 1998. Diel variability of mercury phase and species distributions in the Florida Everglades. Biogeochemistry 40:311–325.\nMikkela, C., I. Sundh, B. H. Svennson, and M. Nilsson 1995. Diurnal variation in methane emission in relation to the water-table, soil-temperature, climate and vegetation cover in a Swedish acid mire. Biogeochemistry 28:93–114.\nWaddington, J. M. and N. T. Roulet. 1996. Atmosphere-wetland carbon exchanges: scale dependency of CO2 and CH4 exchange on the developmental topography of a peatland. Global Biogeochemical Cycles 10:233–245.",{"VOID":1088},"10.1672\u002F0277-5212(2004)024[0207:DMISPC]2.0.CO;2","2024-05-08T16:34:41.515+00:00","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1672\u002F0277-5212(2004)024[0207:DMISPC]2.0.CO;2",[1092],{"id":1093,"sortIndex":18,"researcher":17,"roles":1094,"affiliations":1095,"properties":1104,"displayName":1106,"givenName":17,"familyName":17},"139f4f19-1771-403a-bed0-ea43bc2e348a",[253],[1096],{"id":1097,"sortIndex":18,"affiliation":1098,"properties":17},"90abda3f-3005-4663-8bd3-b4884edbd58f",{"id":1097,"createTime":17,"updateTime":17,"relativeEntities":1099,"slug":17,"properties":1100,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":1103,"statistic":17},[],{"title":1101},{"VI":1102},"Department of Geography, University of Toronto at Mississauga, Mississauga, Canada",[],{"title":1105,"gsAuthor":1107},{"VI":1106},"Brian A. Branfireun",{"VOID":1108},"[\"BIparxkAAAAJ\"]",{"url":1090,"publisher":1110,"properties":1158},{"id":6,"createTime":7,"updateTime":8,"relativeEntities":1111,"slug":10,"properties":1112,"entityType":15,"verifyStatus":16,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":18,"subjectFields":1115,"manageAffiliations":1127,"indexDatabases":1138,"url":17,"thumbnailPath":17,"statistic":1153,"gsStatistic":17,"type":220,"analyzePriority":17},[],{"issn":1113,"title":1114},{"VOID":13},{"EN":10},[1116,1119,1123],{"id":21,"createTime":17,"updateTime":17,"relativeEntities":1117,"label":1118,"description":17,"parentId":17,"standard":17,"scholarHubFieldId":17},[],{"EN":24},{"id":26,"createTime":17,"updateTime":17,"relativeEntities":1120,"label":1121,"description":1122,"parentId":17,"standard":17,"scholarHubFieldId":17},[],{"EN":29},{},{"id":32,"createTime":17,"updateTime":17,"relativeEntities":1124,"label":1125,"description":1126,"parentId":17,"standard":17,"scholarHubFieldId":17},[],{"EN":35},{},[1128,1133],{"id":39,"createTime":17,"updateTime":17,"relativeEntities":1129,"slug":17,"properties":1130,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":1132,"statistic":17},[],{"title":1131},{"EN":43},[],{"id":46,"createTime":17,"updateTime":17,"relativeEntities":1134,"slug":17,"properties":1135,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":1137,"statistic":17},[],{"title":1136},{"EN":50},[52],[1139,1146],{"id":55,"indexDatabase":1140,"url":66,"indexYears":67,"academicFieldIds":1145,"indexDatabaseRanking":72},{"id":57,"createTime":17,"updateTime":17,"relativeEntities":1141,"label":1142,"description":1143,"key":63,"publicationTags":1144,"standard":17},[],{"EN":60,"VI":60},{"EN":60,"VI":62},[65],[69,70,71],{"id":74,"indexDatabase":1147,"url":87,"indexYears":17,"academicFieldIds":1152,"indexDatabaseRanking":17},{"id":76,"createTime":17,"updateTime":17,"relativeEntities":1148,"label":1149,"description":1150,"key":83,"publicationTags":1151,"standard":17},[],{"EN":79,"VI":79},{"EN":81,"VI":82},[85,86],[89,90],{"impactFactor":18,"impactFactorByYear":1154,"i10Index":102,"i10IndexLast5Year":103,"totalPublication":104,"totalPublicationByYear":1155,"totalCitation":137,"totalCitationByYear":1156,"totalCitationPerPublication":176,"totalCitationPerPublicationByYear":1157,"hindexLast5Year":219,"hindex":219},{"2012":93,"2013":94,"2014":95,"2015":96,"2016":97,"2017":98,"2018":99,"2019":94,"2020":100,"2021":95,"2022":98,"2023":101},{"1981":106,"1982":103,"1983":107,"1984":107,"1985":107,"1986":108,"1987":109,"1988":110,"1989":111,"1990":103,"1991":112,"1992":113,"1993":113,"1994":114,"1995":115,"1996":116,"1997":117,"1998":118,"1999":119,"2000":118,"2001":120,"2002":121,"2003":122,"2004":123,"2005":124,"2006":125,"2007":126,"2008":126,"2009":127,"2010":125,"2011":128,"2012":129,"2013":130,"2014":131,"2015":129,"2016":132,"2017":127,"2018":127,"2019":133,"2020":134,"2021":135,"2022":129,"2023":136,"2024":115},{"1981":108,"1982":139,"1983":140,"1984":115,"1985":141,"1988":142,"1989":120,"1990":106,"1991":143,"1992":144,"1993":145,"1994":146,"1995":147,"1996":148,"1997":149,"1998":150,"1999":151,"2000":152,"2001":153,"2002":154,"2003":155,"2004":156,"2005":157,"2006":158,"2007":159,"2008":160,"2009":161,"2010":162,"2011":163,"2012":164,"2013":165,"2014":166,"2015":167,"2016":168,"2017":169,"2018":170,"2019":147,"2020":171,"2021":172,"2022":173,"2023":174,"2024":175},{"1981":178,"1982":179,"1983":180,"1984":181,"1985":182,"1988":183,"1989":184,"1990":185,"1991":186,"1992":187,"1993":188,"1994":189,"1995":190,"1996":191,"1997":192,"1998":193,"1999":194,"2000":195,"2001":196,"2002":197,"2003":198,"2004":199,"2005":200,"2006":201,"2007":202,"2008":194,"2009":203,"2010":204,"2011":205,"2012":206,"2013":207,"2014":208,"2015":209,"2016":210,"2017":211,"2018":212,"2019":213,"2020":214,"2021":215,"2022":216,"2023":217,"2024":218},{"pages":1159,"volume":1161},{"VOID":1160},"207-211",{"VOID":1162},"24",34,{"total":1163,"publishYear":1165,"statisticByYear":1166},2004,{"2005":140,"2006":108,"2007":175,"2008":108,"2009":140,"2010":341,"2011":140,"2012":175,"2013":175,"2014":108,"2015":140,"2016":341,"2018":175,"2019":140,"2021":140,"2022":140,"2023":175},"2004-03-01","2026-07-23T21:47:29.641+00:00",[85,72],{"id":1171,"createTime":1172,"updateTime":1173,"relativeEntities":1174,"slug":1175,"properties":1176,"entityType":244,"verifyStatus":245,"verifyTime":1186,"verifyNote":247,"languages":17,"translateLanguages":17,"viewCount":18,"primaryUrl":1187,"fullTextUrl":17,"authors":1188,"publicationType":287,"publisherRelationship":1230,"citationCount":17,"citationInfo":17,"publishDate":1284,"publishYear":1285,"citationAnalyzeStatus":466,"lastCitationAnalyze":1286,"indexDatabases":1287,"openAccess":17,"references":17,"isForceReanalyzing":346},"fbc74a20-b9c7-46de-815a-ff65a0c41855","2024-01-17T04:08:55.686+00:00","2026-07-23T06:07:26.117+00:00",[],"Observations-on-the-feeding-behavior-and-local-distribution-ofVallentinia-gabriellae-Hydrozoa-Olindiidae-A-new-record-from-mangrove-wetlands-of-the-Indian-River-Lagoon-Florida",{"abstract":1177,"title":1179,"gsPaper":1181,"references":1182,"doi":1184},{"EN":1178},"Vallentinia gabriellae (Hydrozoa) was collected from shallow water in a mangrove wetland along the eastern shore of the Indian River Lagoon, Florida. Adult (gravid) medusae were collected in September 1990 and October 1990, non-gravid medusa in May 1991, and juvenile and gravid medusae in July 1991. All were observed or collected in the perimeter ditch of a mosquito impoundment (Impoundment 19A) in St. Lucie County, Florida. This impoundment has culverts installec along the perimeter dike that connect impoundment waters with those of the Indian River Lagoon. No specimens were found in other adjoining wetland impoundments or in adjacent lagoon waters. No polyps were found despite intensive field collection efforts. To our knowledge, this represents the first record ofV. gabriellae from the Indian River Lagoon. Laboratory feeding studies indicate thatV. gabriellae can feed on a variety of zooplankters commonly found in impoundment waters. These data suggest that, when present, this predatory hydrozoan may be an important predator of zooplankton in mangrove wetland food chains. Preliminary data on food selection show some size selectivity in the feeding process.",{"EN":1180},"Observations on the feeding behavior and local distribution ofVallentinia gabriellae (Hydrozoa: Olindiidae): A new record from mangrove wetlands of the Indian River Lagoon, Florida",{"VOID":359},{"VOID":1183},"Carlson, D. B., R. G. Gilmore, and J. R. Rey. 1985. Salt marsh impoundment management on Florida’s central east coast: Reintegrating isolated high marshes to the estuary. p. 47–63.In F. J. Webb (ed.) Proceedings of the 12th Conference on Wetlands Restoration and Creation. Tampa, FL, USA.\nClark, K. B. 1971. The construction of a collecting device for small aquatic organisms and a method for rapid weighing of small invertebrates. Veliger 13:364–367.\nFoster, N. R. 1971.Vallentinia, the hitch-hiking jellyfish. Frontiers 36:14–19.\nFoster, N. R. 1973. Occurrence ofVallentinia gabriellae (Hydrozoa: Olindiidae) in coastal Yucatan, with notes on its biology and laboratory culture. Proceedings of the Academy of Natural Sciences of Philadelphia 125:69–74.\nGilmore, R. G. 1987. Fish, macrocrustacean and avian population dynamics and cohabitation in tidally-influenced impounded subtropical wetlands. p. 372–394.In W. R. Whitman and W. H. Meredith (eds.) Proceedings of the Symposium on Waterfowl and Wetland Management along the Coastal Zone of the Atlantic Flyway. Delaware Department of Natural Resources, Dover, DE, USA.\nHonegger, T. G. 1984. Ultrastructure of the adhesive tentacles of the limnomedusaVallentinia gabriellae (Hydrozoa, Olindiidae). Zoomorphology 104:26–32.\nKramp, P. L. 1959. The hydromedusae of the Atlantic Ocean and adjacent waters. Carlsberg Foundation, Dana-Report 46:1–283.\nLytle, C. F. 1964. Reproduction and development of the limnomedusaVallentinia gabrielle. American Zoologist 4:331.\nKrumholz, L. A. 1963. Relationships between fertility, sex ratio, and exposure to predation in populations of the mosquitofishGambusia manni Hubbs at Bimini, Bahamas. Internationale Revue der Gesamten Hydrobiologie 48:201–256.\nRey, J. R., R. A. Crossman, T. R. Kain, F. E. Vose, and M. S. Peterson. 1987. Sampling zooplankton in shallow marsh and estuarine habitats: gear description and field tests. Estuaries 10: 61–67.\nRey, J. R., J. Shaffer, R. Crossman, and D. Tremain. 1990. Effects of re-establishing tidal connections in two impounded subtropical marshes on fishes and physical conditions. Wetlands 10:27–45.\nRey, J. R., T. Kain, R. Crossman, M. Peterson, J. Shaffer, and F. Vose. 1991. Zooplankton of impounded marshes and shallow areas of a subtropical lagoon. Florida Scientist 54:191–203.\nRey, J. R., J. Shaffer, T. Kain, and R. Crossman. 1992. Sulfide variation in the pore and surface waters of artificial salt marsh ditches and a natural tidal creek. Estuaries 15:257–269.\nVannuci Mendes, M. 1948. OnVallentinia gabriellae, n. sp. (Limno-medusae). Universidade de São Paulo, Boletins, da Faculdade de Filosofia Ciencias e Letras: Zoologia 13:73–91.\nYoungbluth, M. R., R. Gibson, P. Blades, D. Meyer, C. Stephens, and R. Mahoney. 1976. Plankton in the Indian River Lagoon. p. 40–60.In Indian River Coastal Zone Study, 1975. Harbor Branch Consortium, Ft. Pierce, FL, USA.",{"VOID":1185},"10.1007\u002FBF03160613","2024-06-25T10:09:26.401+00:00","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002FBF03160613",[1189,1204,1217],{"id":1190,"sortIndex":18,"researcher":17,"roles":1191,"affiliations":1192,"properties":1201,"displayName":1203,"givenName":17,"familyName":17},"c0ddb2e8-299f-40b8-b15b-a6fad8b12277",[253],[1193],{"id":1194,"sortIndex":18,"affiliation":1195,"properties":17},"60165a01-3cf8-4789-97ed-b5646333cd91",{"id":1194,"createTime":17,"updateTime":17,"relativeEntities":1196,"slug":17,"properties":1197,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":1200,"statistic":17},[],{"title":1198},{"VI":1199},"Florida Medical Entomology Laboratory, University of Florida (IFAS), Vero Beach",[],{"title":1202},{"VI":1203},"Jorge R. Rey",{"id":1205,"sortIndex":140,"researcher":17,"roles":1206,"affiliations":1207,"properties":1214,"displayName":1216,"givenName":17,"familyName":17},"7e94dbe0-23b2-46d5-b4e2-200e66745dae",[253],[1208],{"id":1194,"sortIndex":18,"affiliation":1209,"properties":17},{"id":1194,"createTime":17,"updateTime":17,"relativeEntities":1210,"slug":17,"properties":1211,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":1213,"statistic":17},[],{"title":1212},{"VI":1199},[],{"title":1215},{"VI":1216},"Tim Kain",{"id":1218,"sortIndex":175,"researcher":17,"roles":1219,"affiliations":1220,"properties":1227,"displayName":1229,"givenName":17,"familyName":17},"e7943d38-c871-47d3-809d-6092b2118f25",[253],[1221],{"id":1194,"sortIndex":18,"affiliation":1222,"properties":17},{"id":1194,"createTime":17,"updateTime":17,"relativeEntities":1223,"slug":17,"properties":1224,"entityType":17,"verifyStatus":17,"verifyTime":17,"verifyNote":17,"languages":17,"translateLanguages":17,"viewCount":17,"url":17,"parentIds":1226,"statistic":17},[],{"title":1225},{"VI":1199},[],{"title":1228},{"VI":1229},"Duane E. De 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N":1296},"Potential damage to wetlands by land-use practices has prompted a need for relatively inexpensive, reliable indicators in monitoring ecological conditions. In this study, soil classification and the following soil tests, sodium bicarbonate-extractable P, nitrate (NO3\n                        −), organic matter (OM), pH, clectrical conductivity (EC), and137Cs distribution, were used to compare four wetlands surrounded by cultivated land or grassland. Cumulic A horizons greater than 60-cm thick were found covering the wet meadow zone of the wetland surrounded by cultivated land. No cumulic A horizons were observed in wet meadow zones adjacent to grassland. Laboratory analyses of surface (0–15 cm) soil showed that the wetland surrounded by cultivated land had P cencentrations 2.5 to 6 times higher in the wet meadow and shallow marsh zones than did the other wetlands. In the wetland surrounded by cultivated land, the dominant soil separate in the wet meadow was silt, while sand was the dominant soil separate in the wet meadow zone in the other three wetlands. Phosphorus, OM, and NO3\n                        − concentrations in wet meadow subsoils (15–60 cm) were higher in the wetland surrounded by cultivated land than in the wetlands surrounded by grasslands. Cesium-137 activities were about 3 to 6 times greater in surface (0–15 cm) soils collected from upland grassy slopes compared to cultivated slopes. Soil morphology,137Cs, P, and OM data indicate higher sedimentation and fertilization rates in wetlands next to cultivated fields.",{"EN":1298},"Soil indicators of agricultural impacts on northern prairie wetlands: Cottonwood lake research area, north Dakota, USA",{"VOID":1300},"[\"4115491142766208964\"]",{"VOID":1302},"Andraski, B. J., D. H. Mucller, and T. C. Daniel. 1985. Phosphorus losses in runoff as affected by tillage. Scil Science Society of America Journal 49:1523–1527.\nCrumpton, W. G. 1989. Algae in northern Prairie Wetlands. p. 188–203.In A. van der Valk (ed.) Northern Prairie Wetlands. Iowa State University Press, Ames, IA, USA.\nDahnke, W. C. and D. A. Whitney. 1988. Measurement of salinity p. 32–34.In W.C. Dahnke (ed.) Recommended chemical soil test procedures for the North Central Region. North Dakota Agricultural Experiment Station, North Dakota State University, Fargo, ND, USA. North Central Region Publication 221 (revised).\nDay, P. R.. 1965. Particle fractionation and particle size analysis, p. 535–540.In C.A. Black (ed.) Methods of Soil Analysis, Part I. American Society of Agronomy, Madison, WI, USA. Agronomy Monograph 9.\nDeLaune, R. D., W. H. Patrick, Jr., and R. J. Buresh. 1978. Sedimentation rates determined by133Cs dating in a rapidly accreting salt marsh. Nature 274:532–533.\nEuliss, N. H. Jr. and D. M. Mushet. 1996. Water-level fluctuation in wetlands as a function of landscape condition in the prairie pothole region. Wetlands 16:587–593.\nGreat Plains Flora Association. 1986. Flora of the Great Plains. University of Kansas Press, Lawrence, KS, USA.\nKnudsen, D. and D. Beegle. 1988. Recommended phosphorus tests. p. 12–15.In W.C. Dahnke (ed.) Recommended chemical soil test procedures for the North Central Region. North Dakota Agricultural Experiment Station. North Dakota State University, Fargo, ND, USA. North Central Region Publication 221 (revised).\nLaBaugh, J. W. 1989. Chemical characteristics of water in northern prairie wetlands. p. 57–90.In A. van der Valk (ed.) Northern Praire Wetlands. Iowa State University Press, Ames, IA, USA.\nLisscy, A. 1971. Depression-focused transient groundwater flow patterns in Manitoba. Geological Association of Canada Special Paper 9:333–341.\nMartin, D. B. and W. A. Hartman. 1987. The effect of cultivation on sediment composition and deposition in prairie pothole wetlands. Water Air Soil Pollution 34:45–53.\nMiller, R. W. and R. L. Donahue. 1990. Soils: an Introduction to Soils and Plant Growth 6th ed. Prentice Hall, Englewood Cliffs, NJ, USA.\nNeely, R. K. and J. L. Baker. 1989. Nitrogen and phosphorus dynamics and the fate of agricultural runoff. p. 92–131.In A. van der Valk, (ed.) Northern Prairie Wetlands. Iowa State University Press, Ames, IA, USA.\nOlsen, S. R., C. V. Cole, E. S. Watenabe, and L. A. Dean. 1954. p. 1–19.In Estimation of available phosphorus in soils by extraction with sodium bicarbonate. U.S. Department of Agriculture, Washington, DC, USA. Circular 939.\nPennock, D. J. and E. de Jong. 1990. Spatial pattern of soil redistribution in Boroll landscapes, southern Saskatehewan. Canadian Journal of Soil Science 150:867–873.\nRitchie J. C. and J. F. McHenry. 1978. Fallour Cesium-137 in cultivated and noncultivated north central United States watersheds. Journal of Environmental Quality 7:40–44.\nRitchie, J. C., J. R. McHenry, and A. C. Gill. 1973. Dating recent reservoir sediments. Limnology and Oceanography 18:254–263.\nSchindler, D. W. 1977. Evolution of phosphorus limitation in lakes. Science 195:260–262.\nSchulte, E. E. 1988. Recommended soil organic matter tests. p. 29–32.In W. C. Dahnke (ed.) Recommended chemical soil test procedures for the North Central Region. North Dakota Agricultural Experiment Station, North Dakota State University, Fargo, ND, USA. North Central Region Publication 221 (revised).\nSharpley, A. N. and S. J. Smith. 1983. Distribution of phosphorus forms in virgin and cultivated soils and the potential for erosion losses. Soil Science Society of America Journal 47:581–586.\nSoil Survey Staff. 1992. Keys to Soil Taxanomy. SMSS Technical Monograph No. 19. 5th ed. Pocahontas Press, Blacksburg, VA, USA.\nSoileau, J. M., B. F. Hajek, and J. T. Touchton. 1990. Soil erosion and deposition evidence in a small watershed using fallout137Cs. Soil Science Society of America Journal 54:1712–1719.\nStewart, R. E. and H. A. Kantrud. 1971. Classification of natural ponds and lakes in the glaciated prairie region. U.S. Fish and Wildlife Service, Washington, DC, USA. Professional Paper 585-D.\nVendrell, P. E. and J. Zupancic. 1990. Determination of soil nitrate by transnitration of salicylic acid. Communications in Soil Science and Plant Analysis 21:1705–1713.\nWalker, P. H. 1966. Post glacial environments in relation to landscape and soils on the Cary Drift. Iowa. Iowa Agricultural Experiment Station Research Bulletin 549:838–875.\nWendt, R. C. and R. B. Corey. 1980. Phosphorus variations in surface runoff from agricultural lands as a function of land use. Journal of Environmental Quality 9:130–136.\nWinter, T. C. and M. R. Carr. 1980. Hydrologic setting of wetlands in the Cottonwood Lake Area, Stutsman County, North Dakota. U.S. Geological Survey Water Resource Investigations 80–89.\nWinter, T. C. and D. O. Rosenberry. 1995. The interaction of ground water with prairie pothole wetlands in the Cottonwood Lake area, east-central North Dakota 1979–1990. 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subsidence and erosion are the principal processes that form accommodation space in interior coastal wetlands when they are converted to open water. The relative contribution of subsidence and erosion to wetland loss can be estimated by comparing elevations and vertical offsets of stratigraphic contacts that are correlated between adjacent sediment cores. Accommodation-space measurements assume that wetland-sediment thicknesses and the elevation of stratigraphic contacts were originally nearly uniform over short horizontal distances (tens to hundreds of meters). The accommodation space attributable to erosion equals the difference in wetland-sediment thickness between wetland cores and adjacent open-water cores taken at formerly emergent wetland sites. The accommodation space attributable to subsidence equals the elevation difference of a stratigraphic marker correlated between the two cores using the wetland core as the reference standard. Together, subsidence plus erosion at an open-water core location equals the accommodation space created by land loss, which is the difference between the adjacent emergent wetland elevation and the existing water depth.",{"EN":1420},"Simple methods for evaluating accommodation space formation in coastal wetlands",{"VOID":1422},"[\"10062816733241571024\"]",{"VOID":1424},"Barras, J. A., J. C. Bernier, and R. A. Morton. 2008. Land area change in coastal Louisiana-A multidecadal perspective (from 1956 to 2006). U.S. Geological Survey Scientific Investigations Map 3019, scale 1:250,000.\nBoumans, R. M. J. and J. W. Day Jr. 1993. High precision measurements of sediment elevation in shallow coastal areas using a sediment-erosion table. Estuaries 16: 375–80.\nCahoon, D. R., P. E. Marin, B. K. Black, and J. C. Lynch. 2000. A method for measuring vertical accretion, elevation, and compaction of soft, shallow-water sediments. Journal of Sedimentary Research 70: 1250–53.\nDahl, T. E. 2000. Status and trends of wetlands in the conterminous United States 1986 to 1997. U.S. Department of the Interior, Fish and Wildlife Service, Washington, DC, USA.\nJervey, M. T. 1988. Quantitative geological modeling of siliciclastic rock sequences and their seismic expression. p. 47–69.In C. K. Wilgus, B. S. Hastings, C. A. Ross, H. Posamentier, J. Van Wagoner, and C. G. St. C. Kendall (eds.) Sea-level changes: An integrated approach. Society of Economic Paleontologists and Mineralogists, Special Publication 42.\nJowsey, P. C. 1966. An improved peat sampler. New Phytologist 65: 245–48.\nKuecher, G. J. 1994. Geologic framework and consolidation settlement potential of the Lafourche Delta, topstratum valley fill: Implications for wetland loss in Terrebonne and Lafourche Parishes, Louisiana. Ph.D. Dissertation, Louisiana State University, Baton Rouge, La, USA.\nLanesky, D. E., B. W. Logan, R. G. Brown, and A. C. Hine. 1979. A new approach to portable vibracoring underwater and on land. Journal of Sedimentary Research 49: 654–57.\nLeibowitz, S. G. and J. M. Hill. 1987. Spatial analyses of Louisiana coastal land loss, v. II, p. 331–55.In R. E. Turner and D. R. Cahoon (eds.) Causes of wetland loss in the coastal central Gulf of Mexico. Minerals Management Service Outer Continental Shelf (OCS) Study MMS87-0120, technical narrative.\nMorton, R. A. 1991. Response of Holocene depositional systems tracts to sediment influx, northern Gulf of Mexico. Proceedings of Gulf Coast Section Society of Economic Paleontologists and Mineralogists Twelfth Annual Research Conference, Houston, TX, USA.\nMorton, R. A. and W. A. White. 1997. Characteristics of and corrections for core shortening in unconsolidated sediments. Journal of Coastal Research 13: 761–69.\nMorton, R. A., N. A. Purcell, and R. Peterson. 2001. Field evidence of subsidence and faulting induced by hydrocarbon production in coastal southeast Texas. Transactions Gulf Coast Association of Geological Societies 51: 239–48.\nMorton, R. A., G. Tiling, and N. F. Ferina. 2003. Causes of hotspot wetland loss in the Mississippi delta plain. Environmental Geosciences 10: 71–80.\nMorton, R. A., J. C. Bernier, and J. A. Barras, and N. F. Ferina. 2005. Rapid subsidence and historical wetland loss in the south-central Mississippi delta plain: Likely causes and future implications: U. S. Geological Survey Open-File Report 2005-16. http:\u002F\u002Fpubs.usgs.gov\u002Fof\u002F2005\u002F1216\u002F.\nMorton, R. A., J. C. Bernier, and J. A. Barras. 2006. Evidence of regional subsidence and associated interior wetland loss induced by hydrocarbon production, Gulf coast region, USA. Environmental Geology 50: 261–74.\nNational Research Council. 2006. Drawing Louisiana’s new map. National Academies Press, Washington, DC, USA.\nReed, D. J. (ed.) Status and trends of hydrologic modification, reduction in sediment availability, and habitat loss\u002Fmodification in the Barataria-Terrebonne estuarine system. 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