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A re-examination of fish estuarine dependence: evidence for connectivity between estuarine and ocean habitats. Estuarine, Coastal and Shelf Science 64 (1): 5–17.\nAble, K.W., and M.P. Fahay. 1998. The first year in the life of estuarine fishes in the Middle Atlantic Bight. New Brunswick: Rutgers University Press.\nAble, K.W., D.M. Nemerson, R. Bush, and P. Light. 2001. Spatial variation in Delaware Bay (USA) marsh creek fish assemblages. Estuaries and Coasts 24 (3): 441–452.\nAitkin, M. 1999. Meta-analysis by random effect modelling in generalized linear models. Statistics in Medicine 18 (17–18): 2343–2351.\nBaker, R., and T.J. Minello. 2011. Trade-offs between gear selectivity and logistics when sampling nekton from shallow open water habitats: a gear comparison study. Gulf and Caribbean Research 23 (1): 37–48.\nBaltz, D.M., C. Rakocinski, and J.W. Fleeger. 1993. Microhabitat use by marsh-edge fishes in a Louisiana estuary. Environmental Biology of Fishes 36 (2): 109–126.\nBeck, M.W., K.L. Heck Jr., K.W. Able, D.L. Childers, D.B. Eggleston, B.M. Gillanders, B. Halpern, C.G. Hays, K. Hoshino, T.J. Minello, R.J. Orth, P.F. Sheridan, and M.P. Weinstein. 2001. The identification, conservation, and management of estuarine and marine nurseries for fish and invertebrates. Bioscience 51 (8): 633–641.\nBoesch, D.F., and R.E. Turner. 1984. Dependence of fishery species on salt marshes: the role of food and refuge. Estuaries 7 (4A): 460–468.\nCasella, G., and R.L. Berger. 2002. Statistical inference. 2nd ed. Pacific Grove, California: Duxbury.\nCastellanos, D.L., and L.P. Rozas. 2001. Nekton use of submerged aquatic vegetation, marsh, and shallow unvegetated bottom in the Atchafalaya River Delta, a Louisiana tidal freshwater ecosystem. Estuaries 24 (2): 184–197.\nChabreck, R.H. 1970. Marsh zones and vegetative types in the Louisiana coastal marshes. PhD Dissertation, Louisiana State University.\nChambers, J.R. 1992. Coastal degradation and fish population losses. In Stemming the tide of coastal fish habitat loss, ed. R.H. Stroud, 45–51. Savannah: National Coalition for Marine Conservation.\nChesney, E.J., D.M. Baltz, and R.G. Thomas. 2000. Louisiana estuarine and coastal fisheries and habitats: perspectives from a fish’s eye view. Ecological Applications 10 (2): 350–366.\nDeegan, L.A. 1993. Nutrient and energy transport between estuaries and coastal marine ecosystems by fish migration. Canadian Journal of Fisheries and Aquatic Sciences 50 (1): 74–79.\nDeegan, L.A., J.E. Hughes, and R.A. Rountree. 2000. Salt marsh ecosystem support of marine transient species. In In Concepts and controversies in tidal marsh ecology, 333–365. Boston, Massachusetts: Kluwer Academic Publishers.\nDunson, W.A., and J. Travis. 1991. The role of abiotic factors in community organization. The American Naturalist 138 (5): 1067–1091.\nEnwright, N.M., S.B. Hartley, M.G. Brasher, J.M. Visser, M.K. Mitchell, B.M. Ballard, M.W. Parr, B.R. Couvillion, and B.C. Wilson. 2014. Delineation of marsh types of the Texas Coast from Corpus Christi Bay to the Sabine River in 2010. U.S. Geological Survey Scientific Investigations Report 2014–5110.\nEnwright, N.M., S.B. Hartley, B.R. Couvillion, M.G. Brasher, J.M. Visser, M.K. Mitchell, B.M. Ballard, M.W. Parr, and B.C. Wilson. 2015. Delineation of marsh types from Corpus Christi Bay, Texas, to Perdido Bay, Alabama, in 2010. U.S. Geological Survey Scientific Investigations Map 3336, 1 sheet, scale 1:750,000. 10.3133\u002Fsim3336. Accessed 20 September 2017.\nFelley, J.D. 1987. Nekton assemblages of three tributaries to the Calcasieu estuary, Louisiana. Estuaries 10 (4): 321–329.\nGain, I. 2009. Oyster reefs as nekton habitat in estuarine ecosystems. MS Thesis, Texas A&M University.\nGlancy, T.P., T.K. Frazer, C.E. Cichra, and W.J. Lingberg. 2003. Comparative patterns of occupancy by decapod crustaceans in seagrass, oyster, and marsh-edge habitats in a northeast Gulf of Mexico estuary. Estuaries 26 (5): 1291–1301.\nGoodman, L.A. 1960. On the exact variance of products. Journal of the American Statistical Association 55 (292): 708–713.\nGunter, G. 1961. Some relations of estuarine organisms to salinity. Limnology and Oceanography 6 (2): 182–190.\nHiggins, J.P.T., and S. Green, editors. 2011. Cochrane handbook for systematic reviews of interventions. Version 5.1.0. The Cochrane Collaboration. http:\u002F\u002Fwww.cochrane-handbook.org. Accessed 1 July 2019.\nHijuelos, A.C., S.E. Sable, A.M. O’Connell, J.P. Geaghan, D.C. Lindquist, and E.D. White. 2017. Application of species distribution models to identify estuarine hot spots for juvenile nekton. Estuaries and Coasts 40 (4): 1183–1194.\nHilbe, J.M. 2014. Modeling count data. New York: Cambridge University Press.\nHitch, A.T., K.M. Purcell, S.B. Martin, P.L. Klerks, and P.L. Leberg. 2011. Interactions of salinity, marsh fragmentation and submerged aquatic vegetation on resident nekton assemblages of coastal marsh ponds. Estuaries and Coasts 34 (3): 653–662.\nHollweg, T.A., M.C. Christman, J. Lipton, B.P. Wallace, M.T. Huisenga, D. Lane, and K.G. Benson. 2019. Meta-analysis of nekton recovery following marsh restoration in the northern Gulf of Mexico. Submitted to same special section of Estuaries and Coasts. https:\u002F\u002Fdoi.org\u002F10.1007\u002Fs12237-019-00630-1.\nKang, S.-R., and S.L. King. 2013. Effects of hydrologic connectivity and environmental variables on nekton assemblage in a coastal marsh system. Wetlands 33 (2): 321–334.\nKneib, R.T. 1997. The role of tidal marshes in the ecology of estuarine nekton. In Oceanography and marine biology: an annual review, ed. A.D. Ansell, R.N. Gibson, and M. Barnes, 163–220. Bristol, Pennsylvania: UCL Press.\nKneib, R.T., and S.L. Wagner. 1994. Nekton use of vegetated marsh habitats at different stages of tidal inundation. Marine Ecology Progress Series 106: 227–238.\nLang, E.T., N.J. Brown-Peterson, M.S. Peterson, and W.T. Slack. 2012. Seasonal and tidally driven reproductive patterns in the saltmarsh topminnow, Fundulus jenkinsi. Copeia 2012 (3): 451–459.\nLellis-Dibble, K.A., K.E. McGlynn, and T.E. Bigford. 2008. Estuarine fish and shellfish species in U.S. commercial and recreational fisheries: economic value as an incentive to protect and restore estuarine habitat. NOAA Technical Memorandum NMFS-F\u002FSPO-90. U.S. Department of Commerce.\nLima, S.L., and L.M. Dill. 1990. Behavioral decisions made under the risk of predation: a review and prospectus. Canadian Journal of Zoology 68 (4): 619–640.\nLopez, J.D., M.S. Peterson, E.T. Lang, and A.M. Charbonnet. 2010. Linking habitat and life history for conservation of the rare saltmarsh topminnow Fundulus jenkinsi: morphometrics, reproduction, and trophic ecology. Endangered Species Research 12 (2): 141–155.\nMace, M.M., III, and L.P. Rozas. 2017. Population dynamics and secondary production of juvenile white shrimp (Litopenaeus setiferus) along an estuarine salinity gradient. Fishery Bulletin 115 (1).\nMartino, E.J., and K.W. Able. 2003. Fish assemblages across the marine to low salinity transition zone of a temperate estuary. Estuarine, Coastal and Shelf Science 56 (5): 969–987.\nMcIvor, C.C., and W.E. Odum. 1988. Food, predation risk, and microhabitat selection in a marsh fish assemblage. Ecology 69 (5): 1341–1351.\nMcIvor, C.C., and L.P. Rozas. 1996. Direct nekton use of intertidal saltmarsh habitat and linkage with adjacent habitats: a review from the southeastern United States. In Estuarine shores: evolution, environments and human alterations, ed. K.F. Nordstrom and C.T. Roman, 311–334. New York: John Wiley & Sons.\nMinello, T.J. 1999. Nekton densities in shallow estuarine habitats of Texas and Louisiana and the identification of essential fish habitat. American Fisheries Society Symposium 22: 43–75.\nMinello, T.J., and L.P. Rozas. 2002. Nekton in Gulf Coast wetlands: fine-scale distributions, landscape patterns, and restoration implications. Ecological Applications 12 (2): 441–455.\nMinello, T.J., and J.W. Webb. 1997. Use of natural and created Spartina alterniflora salt marshes by fishery species and other aquatic fauna in Galveston Bay, Texas, USA. Marine Ecology Progress Series 151: 165–179.\nMinello, T.J., and R.J. Zimmerman. 1991. The role of estuarine habitats in regulating growth and survival of juvenile penaeid shrimp. In Frontiers in shrimp research, ed. P. DeLoach, W.J. Dougherty, and M.A. Davidson, 1–16. Amsterdam: Elsevier Scientific Publications.\nMinello, T.J., and R.J. Zimmerman. 1992. Utilization of natural and transplanted Texas salt marshes by fish and decapod crustaceans. Marine Ecology Progress Series 90: 273–285.\nMinello, T.J., L.P. Rozas, and R. Baker. 2012. Geographic variability in salt marsh flooding patterns may affect nursery value for fishery species. Estuaries and Coasts 35 (2): 501–514.\nMinello, T.J., R.J. Zimmerman, and R. Medina. 1994. The importance of edge for natant macrofauna in a created salt marsh. Wetlands 14 (3): 184–198.\nMinello, T.J., K.W. Able, M.P. Weinstein, and C.G. Hays. 2003. Salt marshes as nurseries for nekton: testing hypotheses on density, growth and survival through meta-analysis. Marine Ecology Progress Series 246: 39–59.\nMinello, T.J., G.A. Matthews, P.A. Caldwell, and L.P. Rozas. 2008. Population and production estimates for decapod crustaceans in wetlands of Galveston Bay, Texas. Transactions of the American Fisheries Society 137 (1): 129–146.\nNevins, J.A., J.B. Pollack, and G.W. Stunz. 2014. 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Dynamics of littoral fishes and decapods along a coastal river-estuarine gradient. Estuarine, Coastal and Shelf Science 33 (5): 467–483.\nQuinn, G.P., and M.J. Keough. 2002. Experimental design and data analysis for biologists. Cambridge: Cambridge University Press.\nRakocinski, C.F., D.M. Baltz, and J.W. Fleeger. 1992. Correspondence between environmental gradients and the community structure of marsh-edge fishes in a Louisiana estuary. Marine Ecology Progress Series 80: 135–148.\nRobillard, M.M.R., G.W. Stunz, and J. Simons. 2010. Relative value of deep subtidal oyster reefs to other estuarine habitat types using a novel sampling method. Journal of Shellfish Research 29 (2): 291–302.\nRogers, S.G., T.E. Targett, and S.B. Van Sant. 1984. Fish-nursery use in Georgia salt-marsh estuaries: the influence of springtime freshwater conditions. Transactions of the American Fisheries Society 113 (5): 595–606.\nRozas, L.P. 1995. 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The impact of a severe drought on the vegetation of a subtropical estuary. Estuaries 25 (6A): 1184–1195.\nWagner, C.M., and H.M. Austin. 1999. Correspondence between environmental gradients and summer littoral fish assemblages in low salinity reaches of the Chesapeake Bay, USA. Marine Ecology Progress Series 177: 197–212.\nWeinstein, M.P., S.L. Weiss, and M.F. Walters. 1980. Multiple determinants of community structure in shallow marsh habitats, Cape Fear River Estuary, North Carolina, USA. Marine Biology 58 (3): 227–243.\nWerner, E.E., J.F. Gilliam, D.J. Hall, and G.G. Mittelbach. 1983. An experimental test of the effects of predation risk on habitat use in fish. Ecology 64 (6): 1540–1548.\nWhaley, S.D., and T.J. Minello. 2002. The distribution of benthic infauna of a Texas salt marsh in relation to the marsh edge. Wetlands 22 (4): 753–766.\nZeug, S.C., V.R. Shervette, D.J. Hoeinghaus, and S.E.I. Davis. 2007. Nekton assemblage structure in natural and created marsh-edge habitats of the Guadalupe Estuary, Texas, USA. Estuarine, Coastal and Shelf Science 71 (3-4): 457–466.\nZimmerman, R.J., and T.J. Minello. 1984. Densities of Penaeus aztecus, Penaeus setiferus, and other natant macrofauna in a Texas salt marsh. Estuaries 7 (4A): 421–433.\nZimmerman, R.J., T.J. Minello, and L.P. Rozas. 2000. Salt marsh linkages to productivity of Penaeid shrimps and blue crabs in the northern Gulf of Mexico. In Concepts and controversies in tidal marsh ecology, ed. M.P. Weinstein and D.A. Kreeger, 293–314. Boston, Massachusetts: Kluwer Academic Publishers.",{"EN":206},"Estuaries in the northern Gulf of Mexico (GOM) provide habitat for many ecologically, commercially, and recreationally important fish and crustacean species (i.e., nekton), but patterns of nekton abundance and community assemblages across habitat types, salinity zones, and seasons have not been described region-wide. Recognizing the wealth of information collected from previous and ongoing field sampling efforts, we developed a meta-analytical approach to aggregate nekton density data from separate studies (using different gear types) that can be used to answer key research questions. We then applied this meta-analytical approach to separate nekton datasets from studies conducted in the Gulf of Mexico to summarize patterns in nekton density across and within several estuarine habitat types, including marsh, oyster reefs, submerged aquatic vegetation (SAV), and open-water non-vegetated bottom (NVB). The results of the meta-analysis highlighted several important patterns of nekton use associated with these habitat types. Nekton densities were higher in structured estuarine habitats (i.e., marsh, oyster reefs, SAV) than in open-water NVB habitat. Marsh and SAV community assemblages were relatively similar to each other, but different from those associated with open-water NVB and oyster habitats. Densities of commercially and recreationally important crustacean and fish species were highest in saline marshes, thus demonstrating the importance of this habitat in the northern GOM. The results of our meta-analysis are generally consistent with previous site-specific studies in the region (many of which were included in the meta-analysis) and provide further evidence for these patterns at a regional scale. This meta-analytical approach is easy to implement for diverse research and management purposes, and provides the opportunity to advance understanding of the value and role of coastal habitats to nekton communities.",{"EN":208},"Meta-analysis of Nekton Utilization of Coastal Habitats in the Northern Gulf of Mexico",{"VOID":210},"10.1007\u002Fs12237-019-00633-y","PUBLICATION","VERIFIED","Auto Verify","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs12237-019-00633-y",[216,232,247,282,298,314,340,363],{"id":217,"sortIndex":133,"researcher":20,"roles":218,"affiliations":220,"properties":229},"4f68509f-c0dc-4095-8b9c-5be76496e30a",[219],"AUTHOR",[221],{"id":20,"sortIndex":21,"affiliation":222,"properties":20},{"id":223,"createTime":224,"updateTime":224,"relativeEntities":225,"slug":20,"properties":226,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"7d3bed72-3f9a-4924-9304-add65a3cf143","2023-12-11T15:15:31.275+00:00",[],{"title":227},{"VI":228},"MCC Statistical Consulting, LLC, Gainesville, USA",{"title":230},{"VI":231},"Mary C. 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Effect of starvation on growth, biochemical, hematological and non-specific immune parameters in two different size groups of grey mullet, Mugil cephalus (Linnaeus, 1758). Acta Ecologica Sinica. Elsevier B.V 36: 205–211. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.chnaes.2016.04.008.\nAnderson, Donald, M., Elizabeth, Fensin, Christopher J. Gobler, Alicia E. Hoeglund, Katherine A. Hubbard, David M. Kulis, Jan H. Landsberg, et al. 2021. Marine harmful algal blooms (HABs) in the United States: History, current status and future trends. Harmful Algae. Elsevier B.V 102: 101975. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.hal.2021.101975.\nArockia, Vasanthi, Lourduraj, Peranandam, Revathi, Jayaprakash, Mini, and Natesan Munuswamy. 2013. Integrated use of histological and ultrastructural biomarkers in Mugil cephalus for assessing heavy metal pollution in Ennore estuary, Chennai. Chemosphere. Elsevier Ltd 91: 1156–1164. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.chemosphere.2013.01.021.\nAzazy, G.E.A., H.A. Hebicha, and A.M. Nasr-Allah. 2012. Estimated costs and returns for commercial cage production of fingerlings and table-size mullet (Mugil cephalus) in Dakhlia Governorate. Egypt. Egyptian Journal of Aquatic Research 2: 1–14.\nBates, Stephen, S., Daniel G. Beach, Luc A. Comeau, Nicola, Haigh, Nancy I. Lewis, Andrea, Locke, Jennifer L. Martin, et al. 2020. Marine harmful algal blooms and phycotoxins of concern to Canada. Canadian Technical Report of Fisheries and Aquatic Sciences. Moncton: Fisheries and Oceans Canada 3384.\nBernet, D, H Schmidt-Posthaus, T Wahli, and P Burkhardt-Holm. 2004. Evaluation of two monitoring approaches to assess effects of waste water disposal on histological alterations in fish. Hydrobiologia 524: 53–66. https:\u002F\u002Fdoi.org\u002F10.1023\u002FB:HYDR.0000036196.84682.27.\nBernet, D, H Schmidt, W Meier, P Burkhardt-Holm, and T Wahli. 1999. Histopathology in fish: proposal for a protocol to assess aquatic pollution. Journal of Fish Diseases 22: 25–34. https:\u002F\u002Fdoi.org\u002F10.1046\u002Fj.1365-2761.1999.00134.x.\nBlack, E.A., J.N.C. Whyth, J.W. Bagshaw, and N.G. Ginther. 1991. The effects of Heterosigma akashiwo on juvenile Oncorhynchus tshawytscha and its implications for fish culture. Journal of Applied Ichthyology 7: 168–175. https:\u002F\u002Fdoi.org\u002F10.1111\u002Fj.1439-0426.1991.tb00523.x.\nBornman, Eugin, Paul D. Cowley, Janine B. Adams, and Nadine A. Strydom. 2021. Daytime intra-estuary movements and harmful algal bloom avoidance by Mugil cephalus ( family Mugilidae ). Estuarine, Coastal and Shelf Science. Elsevier Ltd 260: 107492. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.ecss.2021.107492.\nChang, F Hoe, Colin Anderson, and Nelson C. Boustead. 1990. First record of a Heterosigma (Raphidophyceae) bloom with associated mortality of cage - reared salmon in Big Glory Bay, New Zealand. New Zealand Journal of Marine and Freshwater Research 24: 461–469. https:\u002F\u002Fdoi.org\u002F10.1080\u002F00288330.1990.9516437.\nDe las Heras, V., Juan Antonio Martos-Sitcha, Manuel Yúfera, Juan Miguel Mancera, and Gonzalo Martínez-Rodríguez. 2015. Influence of stocking density on growth, metabolism and stress of thick- lipped grey mullet (Chelon labrosus) juveniles. Aquaculture. Elsevier 448: 29–37. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.aquaculture.2015.05.033.\nDiaz, Julia M., Sydney Plummer, Carmelo Tomas, and Catharina Alves-de-souza. 2018. Production of extracellular superoxide and hydrogen peroxide by five marine species of harmful bloom-forming algae. Journal of Plankton Research 40: 667–677. https:\u002F\u002Fdoi.org\u002F10.1093\u002Fplankt\u002Ffby043.\nDolah, Frances M. Van, Daniel Roelke, and Richard M. Greene. 2001. Health and Ecological Impacts of Harmful Algal Blooms: Risk Assessment Needs. Human and Ecological Risk Assessment 7: 1329–1345\nEspmark, Åsa, Maria, Kirsti, Hjelde, and Grete Baeverfjord. 2010. Development of gas bubble disease in juvenile Atlantic salmon exposed to water supersaturated with oxygen. Aquaculture. Elsevier B.V 306: 198–204. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.aquaculture.2010.05.001.\nFazio, F., C. Faggio, G. Piccione, R. Bonfiglio, and F. Marino. 2014. Effect of rearing density on the blood and tissues of mullet (Mugil cephalus L.). Marine and Freshwater Behaviour and Physiology. Taylor & Francis 47: 389–399. https:\u002F\u002Fdoi.org\u002F10.1080\u002F10236244.2014.955351.\nFredrickson, Kerri A., Suzanne L. Strom, Ryan Crim, and Kathryn J. Coyne. 2011. Interstrain variability in physiology and genetics of Heterosigma Akashiwo (Raphidophyceae ) from the west coast of North America. Journal of Phycology 47: 25–35. https:\u002F\u002Fdoi.org\u002F10.1111\u002Fj.1529-8817.2010.00942.x.\nHaigh, Rowan, Debby Ianson, Carrie A. Holt, and Holly E. Neate. 2015. Effects of Ocean Acidification on Temperate Coastal Marine Ecosystems and Fisheries in the Northeast Pacific. PLoS One 10: 1–46. https:\u002F\u002Fdoi.org\u002F10.1371\u002Fjournal.pone.0117533.\nHallegraeff, G.M. 1993. A review of harmful algal blooms and their apparent global increase. Phycologia 32: 79–99. https:\u002F\u002Fdoi.org\u002F10.2216\u002Fi0031-8884-32-2-79.1.\nHara, Yoshiaki, and Mitsuo Chihara. 1987. Morphology, ultrastructure and taxonomy of the raphidophycean alga Heterosigma akashiwo. The Botanical Magazine, Tokyo 100: 151–163.\nHeisler, J., P.M. Glibert, J.M. Burkholder, D.M. Anderson, W. Cochlan, W.C. Dennison, Q. Dortch, et al. 2008. Eutrophication and harmful algal blooms : A scientific consensus. Harmful Algae 8: 3–13. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.hal.2008.08.006.\nHigashi, Aiko, Satoshi Nagai, Paulo S. Salomon, and Shoko Ueki. 2017. A unique, highly variable mitochondrial gene with coding capacity of Heterosigma akashiwo, class Raphidophyceae. Journal of Applied Phycology 29: 2961–2969. https:\u002F\u002Fdoi.org\u002F10.1007\u002Fs10811-017-1142-2.\nHorner, R.A. 1998. Harmful Algal Blooms in Puget Sound: general Perspective. 4th Puget Sound Research Conference, Seattle, WA, March 12-13, 1998.\nHued, Andrea Cecilia, Sabrina Oberhofer, María De Los, and Ángeles. Bistoni. 2012. Exposure to a commercial glyphosate formulation (Roundup®) alters normal gill and liver histology and affects male sexual activity of Jenynsia multidentata (Anablepidae, cyprinodontiformes). Archives of Environmental Contamination and Toxicology 62: 107–117. https:\u002F\u002Fdoi.org\u002F10.1007\u002Fs00244-011-9686-7.\nICES. 2012. Report of the ICES - IOC Working Group on Harmful Algal Bloom Dynamics (WGHABD). Oban, Scotland.\nJeong, H. J. 2011. Mixotrophy in red tide algae raphidophytes. Journal of Eukaryotic Microbiology 58: 215–222. https:\u002F\u002Fdoi.org\u002F10.1111\u002Fj.1550-7408.2011.00550.x.\nKarim, Ehsanul M. Zaher, Mohammed, Ashraful, Haque, M.S., Kuli, Khan, and M.J. Rahman. 2011. Optimization of stocking density for growth and production of striped mullet, Mugil cephalus L. in pond culture system. Bangladesh Journal of Fish Research 103–114.\nKhan, S., O. Arakawa, and Y. Onoue. 1997. Neurotoxins in a toxic red tide of Heterosigma akashiwo (Raphidophyceae) in Kagoshima Bay, Japan. Aquaculture Research 9–14. https:\u002F\u002Fdoi.org\u002F10.1046\u002Fj.1365-2109.1997.t01-1-00823.x.\nLandsberg, Jan H. 2002. The effects of harmful algal blooms on aquatic organisms. Reviews in Fisheries Science. https:\u002F\u002Fdoi.org\u002F10.1080\u002F20026491051695.\nLemley, D. A., J. B. Adams, and G. M. Rishworth. 2018a. Unwinding a tangled web: a fine-scale approach towards understanding the drivers of harmful algal bloom species in a eutrophic South African estuary. Estuaries and Coasts. Springer New York LLC 41: 1356–1369. https:\u002F\u002Fdoi.org\u002F10.1007\u002Fs12237-018-0380-0.\nLemley, D. A., J. B. Adams, and N. A. Strydom. 2018b. Triggers of phytoplankton bloom dynamics in permanently eutrophic waters of a South African estuary. African Journal of Aquatic Science. NISC Pty Ltd 43: 229–240. https:\u002F\u002Fdoi.org\u002F10.2989\u002F16085914.2018.1478794.\nLemley, D. A., J. B. Adams, and S. Taljaard. 2017. Comparative assessment of two agriculturallyinfluenced estuaries: Similar pressure, different response. Marine Pollution Bulletin 117. Elsevier Ltd: 136–147. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.marpolbul.2017.01.059.\nMartínez-Porchas, Marcel, Luis Rafael Martínez-Córdova, and Rogelio Ramos-Enriquez. 2009. Cortisol and Glucose: Reliable indicators of fish stress? Pan-American Journal of Aquatic Sciences 4: 158–178.\nMartínez, Rosa, Emma Orive, Aitor Laza-Martínez, and Sergio Seoane. 2010. Growth response of six strains of Heterosigma akashiwo to varying temperature, salinity and irradiance conditions. Journal of Plankton Research 32: 529–538. https:\u002F\u002Fdoi.org\u002F10.1093\u002Fplankt\u002Ffbp135.\nNero, V., A. Farwell, L.E.J. Lee, T. Van Meer, M.D. MacKinnon, and D.G. Dixon. 2006. The effects of salinity on naphthenic acid toxicity to yellow perch: Gill and liver histopathology. Ecotoxicology and Environmental Safety 65: 252–264. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.ecoenv.2005.07.009.\nNusch, E.A. 1980. Comparison of different methods for chlorophyll and phaeopigment determination. Arch. 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Plasma cortisol and glucose concentrations in the striped mullet (Mugil cephalus L.) subjected to intense handling stress. Chinese Journal of Oceanology and Limnology 10: 40–43.\nWells, Mark L., Vera L. Trainer, Theodore J. Smayda, Bengt SO Karlson, Charles G. Trick, Raphael M. Kudela, Akira Ishikawa et al. 2015. Harmful algal blooms and climate change : Learning from the past and present to forecast the future. Harmful Algae. Elsevier B.V 49: 68–93. https:\u002F\u002Fdoi.org\u002F10.1016\u002Fj.hal.2015.07.009.\nWhitfield, A.K., J. Panfili, and J.D. Durand. 2012. A global review of the cosmopolitan flathead mullet Mugil cephalus Linnaeus 1758 (Teleostei: Mugilidae), with emphasis on the biology, genetics, ecology and fisheries aspects of this apparent species complex. Reviews in Fish Biology and Fisheries 22: 641–681. https:\u002F\u002Fdoi.org\u002F10.1007\u002Fs11160-012-9263-9.\nWolf, Jeffrey C., Wes A. Baumgartner, Vicki S. Blazer, Alvin C. Camus, Jeffery A. Engelhardt, John W. Fournie, Salvatore Frasca, et al. 2015. Nonlesions, Misdiagnoses, Missed diagnoses, and other interpretive challenges in fish histopathology studies: A guide for investigators, authors, reviewers, and readers. Toxicologic Pathology 43: 297–325. https:\u002F\u002Fdoi.org\u002F10.1177\u002F0192623314540229.\nZuur, Alain F., Elena N. Ieno, Neil J. Walker, Anatoly A. Saveliev, and Graham M. Smith. 2009. Mixed effects modelling for nested data. In Mixed effects models and extensions in ecology with R, 101–142. Springer, New York, NY. https:\u002F\u002Fdoi.org\u002F10.1007\u002F978-0-387-87458-6_5.",{"EN":423},"Harmful algal bloom events (HABs) of the raphidophyte, Heterosigma akashiwo, have increased in frequency and severity in some South African estuaries and have been observed in conjunction with substantial fish kills. The impact of H. akashiwo on wild fish populations is still unclear, despite being responsible for massive economic losses in the aquaculture industry globally. Thus, histopathological techniques were used to assess the impacts of H. akashiwo HABs on three species of Mugilidae (Chelon richardsonii, Mugil cephalus and Chelon dumerili) during an in situ cage study (stocking density of \u003C 0.75 kg m−3) in the agriculturally influenced Sundays Estuary, which has predictable spring\u002Fsummer blooming periods of H. akashiwo. It was hypothesised that fishes kept in mesocosms situated in the bloom area of the estuary would have higher blood plasma cortisol and glucose levels and have more deleterious gill alterations than fishes kept adjacent to the bloom area. Blood plasma cortisol, glucose and gill histological and morphological indices were similar between the HAB and control treatments but differed between bloom phases. The proportion of secondary lamellae available for gas exchange (PAGE index) was lower during trials that were in a hypereutrophic bloom phase (> 60 Chl-a µg.L−1) compared to the accumulation and decay phases. Gill histological alterations (HIGill index) were also more pronounced during the same trials. This study emphasises the need for further research including a toxicology study on the H. akashiwo strain, now common in some South African estuaries, to gain knowledge on the mechanisms by which H. akashiwo causes fish kills in order to protect the ecosystem services that estuaries provide.",{"EN":425},"Algal Blooms of Heterosigma akashiwo and Mugilidae Gill Alterations",{"VOID":427},"10.1007\u002Fs12237-021-01038-6","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs12237-021-01038-6",[430,445,457],{"id":431,"sortIndex":170,"researcher":20,"roles":432,"affiliations":433,"properties":442},"cc5dc131-3526-4374-a250-7da68f0e32d0",[219],[434],{"id":20,"sortIndex":21,"affiliation":435,"properties":20},{"id":436,"createTime":437,"updateTime":437,"relativeEntities":438,"slug":20,"properties":439,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"62b56bba-7cf8-428d-8a07-9587f9cf07b3","2024-01-02T05:26:34.289+00:00",[],{"title":440},{"VI":441},"Department of Zoology, Nelson Mandela University, Port Elizabeth, South Africa",{"title":443},{"VI":444},"Nadine A. Strydom",{"id":446,"sortIndex":21,"researcher":20,"roles":447,"affiliations":448,"properties":454},"4daa577d-9e7e-47c5-bde6-ba06353118e9",[219],[449],{"id":20,"sortIndex":21,"affiliation":450,"properties":20},{"id":436,"createTime":437,"updateTime":437,"relativeEntities":451,"slug":20,"properties":452,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},[],{"title":453},{"VI":441},{"title":455},{"VI":456},"Eugin Bornman",{"id":458,"sortIndex":133,"researcher":20,"roles":459,"affiliations":460,"properties":469},"947eecec-c97e-4c42-a873-f669fbbe0f8c",[219],[461],{"id":20,"sortIndex":21,"affiliation":462,"properties":20},{"id":463,"createTime":464,"updateTime":464,"relativeEntities":465,"slug":20,"properties":466,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"3a51b2ad-efe0-4ba2-b620-11d82b359b7e","2023-12-27T00:18:25.297+00:00",[],{"title":467},{"VI":468},"DST\u002FNRF Research Chair in Shallow Water Ecosystems, Institute for Coastal and Marine Research, Nelson Mandela University, Port Elizabeth, South Africa",{"title":470},{"VI":471},"Janine B. Adams",{"url":428,"publisher":473,"properties":501},{"id":6,"createTime":7,"updateTime":8,"relativeEntities":474,"slug":10,"properties":475,"entityType":18,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21,"subjectFields":479,"manageAffiliations":480,"indexDatabases":481,"url":20,"thumbnailPath":20,"statistic":496,"gsStatistic":20,"type":20,"analyzePriority":20},[],{"issn":476,"eissn":477,"title":478},{"VOID":13},{"VOID":15},{"EN":17},[],[],[482,489],{"id":72,"indexDatabase":483,"url":87,"indexYears":20,"academicFieldIds":488,"indexDatabaseRanking":20},{"id":74,"createTime":75,"updateTime":76,"relativeEntities":484,"label":485,"description":486,"key":83,"publicationTags":487,"standard":20},[],{"EN":79,"VI":79},{"VI":81,"EN":82},[85,86],[89,90],{"id":92,"indexDatabase":490,"url":105,"indexYears":106,"academicFieldIds":495,"indexDatabaseRanking":111},{"id":94,"createTime":95,"updateTime":96,"relativeEntities":491,"label":492,"description":493,"key":102,"publicationTags":494,"standard":20},[],{"EN":99,"VI":99},{"EN":99,"VI":101},[104],[108,109,110],{"impactFactor":21,"impactFactorByYear":497,"i10Index":126,"i10IndexLast5Year":127,"totalPublication":128,"totalPublicationByYear":498,"totalCitation":150,"totalCitationByYear":499,"totalCitationPerPublication":171,"totalCitationPerPublicationByYear":500,"hindexLast5Year":191,"hindex":191},{"2012":114,"2013":115,"2014":116,"2015":117,"2016":118,"2017":119,"2018":120,"2019":121,"2020":122,"2021":123,"2022":124,"2023":125},{"1960":67,"1973":130,"1981":67,"1985":131,"1993":132,"1995":133,"2006":134,"2007":135,"2008":136,"2009":137,"2010":138,"2011":139,"2012":140,"2013":141,"2014":142,"2015":143,"2016":143,"2017":144,"2018":145,"2019":146,"2020":147,"2021":148,"2022":136,"2023":144,"2024":149},{"2006":152,"2007":153,"2008":154,"2009":155,"2010":156,"2011":157,"2012":158,"2013":159,"2014":160,"2015":161,"2016":162,"2017":163,"2018":164,"2019":165,"2020":166,"2021":167,"2022":168,"2023":169,"2024":170},{"2006":173,"2007":174,"2008":175,"2009":176,"2010":177,"2011":178,"2012":179,"2013":180,"2014":181,"2015":182,"2016":183,"2017":184,"2018":185,"2019":186,"2020":187,"2021":188,"2022":187,"2023":189,"2024":190},{"volume":502,"pages":504},{"VOID":503},"45",{"VOID":505},"1674-1687","2022-01-03",2022,{"id":509,"createTime":510,"updateTime":511,"relativeEntities":512,"slug":513,"properties":514,"entityType":211,"verifyStatus":212,"verifyTime":511,"verifyNote":213,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21,"primaryUrl":523,"fullTextUrl":20,"authors":524,"publicationType":375,"publisherRelationship":561,"citationCount":20,"citationInfo":20,"publishDate":595,"publishYear":596,"citationAnalyzeStatus":19,"lastCitationAnalyze":20,"indexDatabases":20,"openAccess":20,"references":20,"isForceReanalyzing":412},"e6c1c07b-fdba-4aba-8140-b353a046aa90","2024-02-06T07:50:40.302+00:00","2024-06-26T23:56:20.841+00:00",[],"Using-Isotopic-Measures-of-Connectivity-and-Ecosystem-Capacity-to-Compare-Restoring-and-Natural-Marshes-in-the-Skokomish-River-Estuary-WA-USA",{"references":515,"abstract":517,"title":519,"doi":521},{"VOID":516},"Able, K.W., T.M. 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Perennial pepperweed (Lepidiurn latifolium): properties of invaded tidal marshes. Invasive Plant Science and Management 3: 130–138.\nRickert, C. 2011. Microlepidoptera in salt marshes—life history, effects of grazing, and their suitability as ecological indicators. Faunistisch-Oekologische Mitteilungen: 5-125.\nRiginos, C., and C. Cunningham. 2005. Local adaptation and species segregation in two mussel (Mytilus edulis x Mytilus trossulus) hybrid zones. Molecular Ecology 14: 381–400.\nRomanuk, T.N., and C.D. Levings. 2005. Stable isotope analysis of trophic position and terrestrial vs. marine carbon sources for juvenile Pacific salmonids in nearshore marine habitats. Fisheries Management and Ecology 12: 113–121.\nRuckelshaus, M.H., R.C. Wissmar, and C.A. Simenstad. 1993. The importance of autotroph distribution to mussel growth in a well-mixed, temperate estuary. Estuaries 16: 898–912.\nRussel-Hunter, W.D. 1970. Aquatic productivity: an introduction to some basic aspects of biological oceanography and limnology. London: Collier-MacMillan.\nSchafer, L.N., M.E. Platell, F. Valesini, and I.C. Potter. 2002. Comparisons between the influence of habitat type, season and body size on the dietary compositions of fish species in nearshore marine waters. Journal of Experimental Marine Biology and Ecology 278: 67–92.\nSemmens, B.X., E.J. Ward, J.W. Moore, and C.T. Darimont. 2009. Quantifying inter- and intra-population niche variability using hierarchical bayesian stable isotope mixing models. Plos One 4: 9.\nSheaves, M. 2009. Consequences of ecological connectivity: the coastal ecosystem mosaic. Marine Ecology-Progress Series 391: 107–115.\nSimenstad, C.A., and J.R. Cordell. 2000. Ecological assessment criteria for restoring anadromous salmonid habitat in Pacific Northwest estuaries. Ecological Engineering 15: 283–302.\nSimenstad, C.A., and R.M. Thom. 1996. Functional equivalency trajectories of the restored Gog-Le-Hi-Te estuarine wetland. Ecological Applications 6: 38–56.\nSimenstad, C.A., and R.C. Wissmar. 1985. 13C evidence of the origins and fates of organic carbon in estuarine and nearshore food webs. Marine Ecology-Progress Series 22: 141–152.\nSimenstad, C.A., D. Reed, and M. Ford. 2006. When is restoration not? Incorporating landscape-scale processes to restore self-sustaining ecosystems in coastal wetland restoration. Ecological Engineering 26: 27–39.\nSobczak, W.V., J.E. Cloern, A.D. Jassby, and A.B.. Muller-Solger. 2002. Bioavailability of organic matter in a highly disturbed estuary: the role of detrital and algal resources. Proceedings from the National Academy of Sciences of the United States of America 99: 8101–8105.\nSobczak, W.V., J.E. Cloern, A.D. Jassby, B.E. Cole, T.S. Schraga, and A. Arnsberg. 2005. Detritus fuels ecosystem metabolism but not metazoan food webs in San Francisco Estuary's freshwater delta. Estuaries 28: 124–137.\nSukhotin, A., and H. Portner. 1999. Habitat as a factor involved in the physiological response to environmental anaerobiosis of White Sea Mytilus edulis. Marine Ecology Progress Series 184: 149–160.\nTenore, K. 1983. What controls the availability to animals of detritus derived from vascular plants: Organic nitrogen enrichment or caloric availability? Marine Ecology Progress Series 10: 307–309.\nTorzilli, A., M. Sikaroodi, D. Chalkley, and P. Gillevet. 2006. A comparison of fungal communities from four salt marsh plants using automated ribosomal intergenic spacer analysis (ARISA). Mycologia 98: 690–698.\nTuxen, K., L. Schile, D. Stralberg, S. Siegel, T. Parker, M. Vasey, J. Callaway, and M. Kelly. 2011. Mapping changes in tidal wetland vegetation composition and pattern across a salinity gradient using high spatial resolution imagery. Wetlands Ecology and Management 19: 141–157.\nVinagre, C., J. Salgado, H.N. Cabral, and M.J. Costa. 2011. Food web structure and habitat connectivity in fish estuarine nurseries—impact of river flow. Estuaries and Coasts 34: 663–674.\nWarren, R.S., P.E. Fell, R. Rozsa, A.H. Brawley, A.C. Orsted, E.T. Olson, V. Swamy, and W.A. Niering. 2002. Salt marsh restoration in Connecticut: 20 years of science and management. Restoration Ecology 10: 497–513.\nWeinstein, M.P., S.Y. Litvin, K.L. Bosley, C.M. Fuller, and S.C. Wainright. 2000. The role of tidal salt marsh as an energy source for marine transient and resident finfishes: A stable isotope approach. Transactions Of The American Fisheries Society 129: 797–810.\nWeinstein, M.P., S.Y. Litvin, and V.G. Guida. 2005. Considerations of habitat linkages, estuarine landscapes, and the trophic spectrum in wetland restoration design. Journal of Coastal Research: 51–63.\nWiddows, J., P. Fieth, and C. Worrall. 1979. Relationships between seston, available food and feeding activity in the common mussel Mytilus edulis. Marine Biology 50: 195–207.\nWozniak, A.S., C.T. Roman, S.C. Wainright, R.A. McKinney, and M. James-Pirri. 2006. Monitoring food web changes in tide-restored salt marshes: a carbon stable isotope approach. Estuaries and Coasts 29: 568–578.\nWu, Y.T., C.H. Wang, X.D. Zhang, B. Zhao, L.F. Jiang, J.K. Chen, and B. Li. 2009. Effects of saltmarsh invasion by Spartina alterniflora on arthropod community structure and diets. Biological Invasions 11: 635–649.",{"EN":518},"Estuarine detritus-based food webs typically rely on diverse sources and timing of organic matter (OM) delivery. Access to detritus requires adequate hydraulic connectivity for consumer migration into productive locations and the transfer of allochthonous detritus into consumer habitats. These processes are particularly important to the patterns and rates of community development in restoring estuarine marshes where OM sources and connectivity might vary as a function of landscape setting. This study quantifies trophic dynamics in restoring and natural marsh ecosystems in the Skokomish estuary, Washington, USA, using Pacific blue mussels (Mytilus trossulus), stable isotopes, and a Bayesian multiple source mixing model to estimate available suspended food resources. The restoring marshes represent different ages since restoration implementation—14 and 3 years—as well as different restoration approaches—a levee breach and a full levee removal. Sestonic OM was less available and of lower quality in the two restoring marshes than in the natural marsh site. Mussel diets tracked seasonal trends in OM availability: Phytoplankton consumption was highest in spring, marsh detritus consumption was highest in winter (but consistently comprised at least 30 % of OM assimilated by mussels), and macroalgae consumption was highest in September. Trophic equivalency with mussels inhabiting the natural marsh appears to be restoring more rapidly in the younger restoration site, perhaps because increased hydrologic connectivity achieved through full levee removal promotes greater OM exchange compared to the single levee breach restoration approach. We conclude that increasing ecosystem capacity for detritus production by restoring emergent marsh ecosystems can bolster support for detritus-based food webs and suggest that restoration actions enhancing connectivity may achieve functional equivalency more rapidly than restoration projects exhibiting limited connectivity to the surrounding landscape.",{"EN":520},"Using Isotopic Measures of Connectivity and Ecosystem Capacity to Compare Restoring and Natural Marshes in the Skokomish River Estuary, WA, USA",{"VOID":522},"10.1007\u002Fs12237-014-9831-4","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs12237-014-9831-4",[525,546],{"id":526,"sortIndex":133,"researcher":20,"roles":527,"affiliations":528,"properties":543},"8df02a2d-9257-4383-acc6-38c018ee45b9",[219],[529],{"id":530,"sortIndex":21,"affiliation":531,"properties":540},"fdef82bc-9393-4bcc-a81e-4e3c76c0b210",{"id":532,"createTime":533,"updateTime":534,"relativeEntities":535,"slug":536,"properties":537,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"15cc17a9-0784-49d0-824f-12cef8c6e906","2024-04-20T01:21:47.164+00:00","2024-12-05T15:57:13.400+00:00",[],"University-of-Washington-SEATTLE-USA",{"title":538},{"EN":539},"University of Washington SEATTLE USA",{"title":541},{"VI":542},"University of Washington, Seattle, USA",{"title":544},{"VI":545},"Charles A. Simenstad",{"id":547,"sortIndex":21,"researcher":20,"roles":548,"affiliations":549,"properties":558},"b2c98e72-55e5-42b7-8fcb-30714b4afd82",[219],[550],{"id":551,"sortIndex":21,"affiliation":552,"properties":556},"6260a8cb-197a-412a-9875-4e07a8d73d9c",{"id":532,"createTime":533,"updateTime":534,"relativeEntities":553,"slug":536,"properties":554,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},[],{"title":555},{"EN":539},{"title":557},{"VI":542},{"title":559},{"VI":560},"Emily Howe",{"url":523,"publisher":562,"properties":590},{"id":6,"createTime":7,"updateTime":8,"relativeEntities":563,"slug":10,"properties":564,"entityType":18,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21,"subjectFields":568,"manageAffiliations":569,"indexDatabases":570,"url":20,"thumbnailPath":20,"statistic":585,"gsStatistic":20,"type":20,"analyzePriority":20},[],{"issn":565,"eissn":566,"title":567},{"VOID":13},{"VOID":15},{"EN":17},[],[],[571,578],{"id":72,"indexDatabase":572,"url":87,"indexYears":20,"academicFieldIds":577,"indexDatabaseRanking":20},{"id":74,"createTime":75,"updateTime":76,"relativeEntities":573,"label":574,"description":575,"key":83,"publicationTags":576,"standard":20},[],{"EN":79,"VI":79},{"VI":81,"EN":82},[85,86],[89,90],{"id":92,"indexDatabase":579,"url":105,"indexYears":106,"academicFieldIds":584,"indexDatabaseRanking":111},{"id":94,"createTime":95,"updateTime":96,"relativeEntities":580,"label":581,"description":582,"key":102,"publicationTags":583,"standard":20},[],{"EN":99,"VI":99},{"EN":99,"VI":101},[104],[108,109,110],{"impactFactor":21,"impactFactorByYear":586,"i10Index":126,"i10IndexLast5Year":127,"totalPublication":128,"totalPublicationByYear":587,"totalCitation":150,"totalCitationByYear":588,"totalCitationPerPublication":171,"totalCitationPerPublicationByYear":589,"hindexLast5Year":191,"hindex":191},{"2012":114,"2013":115,"2014":116,"2015":117,"2016":118,"2017":119,"2018":120,"2019":121,"2020":122,"2021":123,"2022":124,"2023":125},{"1960":67,"1973":130,"1981":67,"1985":131,"1993":132,"1995":133,"2006":134,"2007":135,"2008":136,"2009":137,"2010":138,"2011":139,"2012":140,"2013":141,"2014":142,"2015":143,"2016":143,"2017":144,"2018":145,"2019":146,"2020":147,"2021":148,"2022":136,"2023":144,"2024":149},{"2006":152,"2007":153,"2008":154,"2009":155,"2010":156,"2011":157,"2012":158,"2013":159,"2014":160,"2015":161,"2016":162,"2017":163,"2018":164,"2019":165,"2020":166,"2021":167,"2022":168,"2023":169,"2024":170},{"2006":173,"2007":174,"2008":175,"2009":176,"2010":177,"2011":178,"2012":179,"2013":180,"2014":181,"2015":182,"2016":183,"2017":184,"2018":185,"2019":186,"2020":187,"2021":188,"2022":187,"2023":189,"2024":190},{"volume":591,"pages":593},{"VOID":592},"38",{"VOID":594},"639-658","2014-05-30",2014,{"id":598,"createTime":599,"updateTime":599,"relativeEntities":600,"slug":20,"properties":601,"entityType":211,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21,"primaryUrl":610,"fullTextUrl":20,"authors":611,"publicationType":375,"publisherRelationship":640,"citationCount":20,"citationInfo":20,"publishDate":674,"publishYear":675,"citationAnalyzeStatus":19,"lastCitationAnalyze":20,"indexDatabases":20,"openAccess":20,"references":20,"isForceReanalyzing":412},"659445e3-2ee1-493c-bacc-872cd3be386f","2023-12-25T23:55:35.916+00:00",[],{"references":602,"abstract":604,"title":606,"doi":608},{"VOID":603},"Adam, P. 1990. 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Ph.D. Dissertation, University of California Riverside and San Diego State University, San Diego, California.\nZedler, J. B. 1977. Salt marsh community structure in the Tijuana Estuary, California. Estuarine and Coastal Marine Science 5: 39–53.\nZedler, J. B. 1980. Algal mat productivity: Comparisons in a salt marsh. Estuaries 3: 122–131.\nZedler, J. B., J. C. Callaway, J. S. Desmond, G. Vivian-Smith, G. D. Williams, G. Sullivan, A. E. Brewster, and B. K. Bradshaw. 1999. Californian salt-marsh vegetation: An improved model of spatial pattern. Ecosystems 2: 19–35.\nZedler, J. B., J. C. Callaway, and G. Sullivan. 2001. Declining biodiversity: Why species matter and their functions might be restored in California tidal marshes. BioScience 51: 1005–1017.\nZedler, J. B., H. N. Morzaria-Luna, and K. Ward. 2003. The challenge of restoring vegetation on tidal, hypersaline substrates. Plant and Soil 253: 259–273.\nZedler, J. B., and J. M. West. 2007. Declining diversity in natural and restored salt marshes: A 30-year study of Tijuana Estuary. Restoration Ecology in press. DOI 10.1111\u002Fj.1526-100X.2007.00268.x.",{"EN":605},"Annual plants that coexist among perennial dominants might persist in microsites that are stressful to their competitors. In Californian salt marshes, where cover of annual and perennial Salicornia species are negatively correlated, we hypothesized that waterlogged depressions support the annual (Salicornia bigelovii) but not the region’s dominant perennial (Salicornia virginica). In a large restoration site, S. virginica cover was low in naturally formed pools, and our 10-cm depressions decreased its cover by approximately 30% compared to the controls. S. bigelovii grew taller and produced more flowers in waterlogged sites with low soil redox potential, and it completed its life cycle in the 5-cm-deep depressions that we created. Experimentally reducing S. virginica canopy cover in shallow depressions also increased the survival of the annual. In the greenhouse, rhizosphere oxidation was indicated as a mechanism for tolerating waterlogging, as S. bigelovii elevated the soil redox potential by 50 mV more than S. virginica did. Also, in the greenhouse, S. bigelovii seedlings actually suppressed the growth of S. virginica seedlings under increased flooding. We conclude that waterlogged microsites help sustain S. bigelovii in Californian salt marshes and that this increasingly rare plant could be managed by adding shallow depressions to restoration sites.",{"EN":607},"How Waterlogged Microsites Help an Annual Plant Persist Among Salt Marsh Perennials",{"VOID":609},"10.1007\u002Fs12237-007-9019-2","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs12237-007-9019-2",[612,628],{"id":613,"sortIndex":21,"researcher":20,"roles":614,"affiliations":615,"properties":625},"cc2f6193-c631-468d-af04-3c247326977e",[219],[616],{"id":20,"sortIndex":21,"affiliation":617,"properties":20},{"id":618,"createTime":619,"updateTime":619,"relativeEntities":620,"slug":621,"properties":622,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"a607a03d-d029-46b8-9d3a-efeb617ce7c7","2024-04-15T18:07:47.588+00:00",[],"Botany-Department-and-Arboretum-University-of-Wisconsin-Madison-USA",{"title":623},{"EN":624},"Botany Department and Arboretum, University of Wisconsin, Madison, USA",{"title":626},{"VI":627},"Alison K. Varty",{"id":629,"sortIndex":133,"researcher":20,"roles":630,"affiliations":631,"properties":637},"86ad3333-a3ef-46ea-ac5f-e93fae133aa8",[219],[632],{"id":20,"sortIndex":21,"affiliation":633,"properties":20},{"id":618,"createTime":619,"updateTime":619,"relativeEntities":634,"slug":621,"properties":635,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},[],{"title":636},{"EN":624},{"title":638},{"VI":639},"Joy B. 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In the Austral Spring of 2014, we assessed how differences in infaunal communities between paired sedimentary sites with and without seawalls vary with tidal elevation and environmental conditions (i.e. sediment variables, benthic cover), at five locations within Brisbane Waters, New South Wales, Australia. Contrary to the prediction that differences in infaunal communities between sites with and without seawalls would be greatest at high intertidal elevation at which seawalls are built, we found greater differences at mid intertidal elevations. At muddy locations, characterised by high faunal abundance and richness, the abundance of mid intertidal infauna was less at sites with than without seawalls. By contrast, at sandy locations, which were characterised by low infaunal abundance and richness, the reverse pattern was seen. Although the structure of infaunal communities was correlated with sediment characteristics, sites with and without seawalls did not display consistent patterns of difference in sediment grain size or organic carbon content across locations. The greater difference in infaunal communities between sites with and without seawalls at mid than high or low intertidal elevations likely reflects an interaction between the proximity of habitat to seawalls and biological traits of the resident infaunal species that influence their susceptibility to perturbation.",{"EN":686},"Differences in Soft-Sediment Infaunal Communities Between Shorelines with and Without Seawalls",{"VOID":688},"10.1007\u002Fs12237-019-00527-z","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs12237-019-00527-z",[691,708],{"id":692,"sortIndex":133,"researcher":20,"roles":693,"affiliations":694,"properties":705},"80584505-0314-4c2f-9769-75a377a1a3d7",[219],[695],{"id":20,"sortIndex":21,"affiliation":696,"properties":20},{"id":697,"createTime":698,"updateTime":699,"relativeEntities":700,"slug":701,"properties":702,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"c3ba7ddd-8307-4496-800e-7e53532cc822","2023-12-27T23:58:53.240+00:00","2024-09-21T10:24:54.335+00:00",[],"Department-of-Biological-Sciences-Macquarie-University-Sydney-Australia",{"title":703},{"VI":704},"Department of Biological Sciences, Macquarie University, Sydney, Australia",{"title":706},{"VI":707},"Melanie J. Bishop",{"id":709,"sortIndex":21,"researcher":20,"roles":710,"affiliations":711,"properties":717},"0f850876-e93e-4345-8a0d-2fca542a655f",[219],[712],{"id":20,"sortIndex":21,"affiliation":713,"properties":20},{"id":697,"createTime":698,"updateTime":699,"relativeEntities":714,"slug":701,"properties":715,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},[],{"title":716},{"VI":704},{"title":718},{"VI":719},"Lincoln P. 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Van den Berg. 1999. Metal-sulfide complexation in seawater. Marine Chemistry 63: 331–352. doi:10.1016\u002FS0304-4203(98)00056-5.\nAndreae, M.O., and R.J. Ferek. 1992. Photochemical production of carbonyl sulfide in seawater and its emission to the atmosphere. Global Biogeochemical Cycles 6: 175–183. doi:10.1029\u002F91GB02809.\nBarcellos da Rosa, M., W. Behnke, and C. Zetzsch. 2003. Study of the heterogeneous reaction of O3 with CH3SCH3 using the wetted-wall flowtube technique. Atmospheric Chemistry and Physics 3: 1665–1673.\nBell, R.A., and J.R. Kramer. 1999. Structural chemistry and geochemistry of silver–sulfur compounds: critical review. Environmental Toxicology and Chemistry 18: 9–22. doi:10.1897\u002F1551-5028(1999)018\u003C0009:SCAGOS>2.3.CO;2.\nBoffi, A., M. Rizzi, F. Monacelli, and P. Ascenzi. 2000. Determination of H2S solubility via the reaction with ferric hemoglobin I from the bivalve mollusk Lucina pectina. Biochimica et Biophysica Acta 1523: 206–208.\nBuggy, C.J., and J.M. Tobin. 2006. Seasonal and spatial distributions of tributylin in surface sediment of the Tolka estuary, Dublin, Ireland. Environmental Pollution 143: 294–303. doi:10.1016\u002Fj.envpol.2005.11.025.\nChiffoleau, J.F., D. Cossa, D. Auger, and I. Truquet. 1994. Trace metal distribution, partition and fluxes in the Seine estuary in low discharge regime. Marine Chemistry 47: 145–158. doi:10.1016\u002F0304-4203(94)90105-8.\nChiffoleau, J.F., D. Auger, E. Chartier, P. Michel, I. Truquet, A. Ficht, J.L. Gonzalez, and L.A. Romana. 2001. Spatio-temporal changes in cadmium contamination in the Seine estuary (France). Estuaries 24: 1029–1040. doi:10.2307\u002F1353015.\nChiffoleau, J.F., D. Auger, N. Roux, E. Rozuel, and A. Santini. 2005. Distribution of silver in mussels and oysters along the French coasts: data from the national monitoring program. Marine Pollution Bulletin 50: 1713–1744. doi:10.1016\u002Fj.marpolbul.2005.09.009.\nCutter, G.A., and C.F. Krahforst. 1988. Sulfide in surface waters of the Western Atlantic Ocean. Geophysical Research Letters 1512: 1393–1396. doi:10.1029\u002FGL015i012p01393.\nCutter, G.A., and J. Radford-Knoery. 1993. Carbonyl sulfide in two estuaries and shelf waters of the western North Atlantic Ocean. Marine Chemistry 43: 225–233.\nDanielsson, L.-G., B. Magnusson, S. Westerlund, and K. Zhang. 1982. Trace metal determinations in estuarine waters by electrothermal atomic absorption spectrometry after extraction of dithiocarbamate complexes into freon. Analytica Chimica Acta 144: 183–188. doi:10.1016\u002FS0003-2670(01)95531-X.\nDyrssen, D., and K. Kremling. 1990. Increasing hydrogen sulfide concentration and trace metal behavior in the anoxic Baltic waters. Marine Chemistry 30: 193–204. doi:10.1016\u002F0304-4203(90)90070-S.\nElliot, S., E. Lu, and S. Rowland. 1989. Rates and mechanisms for the hydrolysis of OCS in natural waters. Environmental Science & Technology 23: 458–461. doi:10.1021\u002Fes00181a011.\nFlock, O.R., and M.O. Andreae. 1996. Photochemical and non-photochemical formation and destruction of OCS and MeSH in ocean waters. Marine Chemistry 54: 11–26. doi:10.1016\u002F0304-4203(96)00027-8.\nIrving, H., and R.J.P. Williams. 1953. The stability of transition-metal complexes. Journal of the Chemical Society 637: 3192–3220. doi:10.1039\u002Fjr9530003192.\nKettle, A.J., T.S. Rhee, M. Von Hobe, A. Poulton, J. Aiken, and M.O. Andreae. 2001. Assessing the flux of volatile sulfur gases from the ocean to the atmosphere. Journal of Geophysical Research 106: 12193–12209. doi:10.1029\u002F2000JD900630.\nKiene, R.P., and B.F. Taylor. 1988. Biotransformation of organosulfur compounds in sediments via 3-mercaptopropionates. Nature 332: 148–150. doi:10.1038\u002F332148a0.\nKiene, R.P., L.J. Linn, and J.A. Bruton. 2000. New and important roles for DMSP in marine microbial communities. Journal of Sea Research 43: 209–224.\nLaglera, L.M., and C.M.G. Van den Berg. 2003. Copper complexation by thiols compounds in estuarine waters. Marine Chemistry 82: 71–89. doi:10.1016\u002FS0304-4203(03)00053-7.\nLemaire, E., G. Abril, R. De Wit, and H. Etcheber. 2002. Distribution of phytoplankton pigments in nine European estuaries and implications for an estuarine typology. Biogeochemistry 59: 52–23. doi:10.1023\u002FA:1015572508179.\nLiss, P.S., A.D. Hatton, G. Malin, P.D. Nightingale, and S.M. Turner. 1997. Marine sulphur emissions. Philosophical Transactions of the Royal Society B: Biological Sciences. 352: 159–169. doi:10.1098\u002Frstb.1997.0011.\nLuoma, S.N., Y.B. Ho, and G.W. Bryan. 1995. Fate, bioavailability and toxicity of silver in estuarine environments. Marine Pollution Bulletin 31: 44–54.\nLuther, G.W., and E. Tsamakis. 1989. Concentration and form of dissolved sulfide in the oxic water column of the ocean. Marine Chemistry 27: 165–177. doi:10.1016\u002F0304-4203(89)90046-7.\nLuther, G.W., D. Rickard, S.M. Theberge, and A. Olroyd. 1996. Determination of metal (bi)sulfide stability constants of Mn2+, Fe2+, Co2+, Ni2+, Cu2+ and Zn2+ by voltammetric methods. Environmental Science & Technology 30: 671–679. doi:10.1021\u002Fes950417i.\nRozan, T.F., B. Gaboury, and G.W. Luther. 1999. Measuring metal sulfide complexes in oxic river waters with square wave voltammetry. Environmental Science & Technology 33: 3021–3026. doi:10.1021\u002Fes981206r.\nRuzic, I. 1996. Trace metal complexation at heterogeneous binding sites in aquatic systems. Marine Chemistry 53: 1–15. doi:10.1016\u002F0304-4203(96)00008-4.\nSciare, J., N. Mihalopoulos, and B.C. Nguyen. 2002. Spatial and temporal variability of dissolved sulfur compounds in European estuaries. Biogeochemistry 59: 121–141. doi:10.1023\u002FA:1015539725017.\nSimo, R., S.D. Archer, C. Pedros-Alios, L. Gilpin, and C.E. Stelfox-Widdicombe. 2002. Coupled dynamics of dimethylsulfoniopropionate and dimethylsulfide cycling and the microbial food web in surface waters of the North Atlantic. Limnology and Oceanography 47: 53–61.\nSmith, R.C., and K.S. Baker. 1979. Penetration of uv-b and biologically effective dose-rates in natural waters. Photochemistry and Photobiology 29: 311–323. doi:10.1111\u002Fj.1751-1097.1979.tb07054.x.\nStumm, W., and J. Morgan. 1981. Aquatic chemistry. An introduction emphasizing chemical equilibria in natural waters. New York: Wiley780 pages.\nTanzer, D., and K.G. Heumann. 1992. Gas chromatographic trace-level determination of volatile organic sulfides and selenides and of methyl iodide in Atlantic surface water. International Journal of Environmental Analytical Chemistry 481: 17–31. doi:10.1080\u002F03067319208027039.\nThouvenin, B., B. Boutier, J.F. Chiffoleau, J.L. Gonzalez, L.A. Romana, D. Auger, B. Averty, E. Chartier, S. Crochet, and I. Truquet. 2004. Contribution à l’étude de la dynamique et de la spéciation des contaminants. Rapport d’activité 2003. Programme Seine Aval 2. Thème Analyse des risques chimiques et microbiologiques.\nThouvenin, B., B. Boutier, J.F. Chiffoleau, J.L. Gonzalez, D. Cossa, D. Auger, B. Averty, E. Rozuel-Chartier, D. Menard, A. Santini, and M. Olivier. 2005. Contribution à l’étude de la dynamique et de la spéciation des contaminants. Rapport d’activité 2004. Programme Seine Aval 2. Thème Morphodynamique, cycle des vases et contaminants associés.\nTurner, S.M., G. Malin, P.S. Liss, D.S. Harbour, and P.M. Holligan. 1988. The seasonal variation of dimethyl sulfide et dimethylsulfoniopropionate concentrations in nearshore waters. Limnology and Oceanography 33: 364–375.\nUlshöfer, V.S., and M.O. Andreae. 1998. Carbonyl sulfide (COS) in the surface ocean and the atmospheric COS budget. Aquatic Geochemistry 3: 283–303. doi:10.1023\u002FA:1009668400667.\nVan den Berg, C.M.G. 1993. Complex formation and the chemistry of selected trace elements in estuaries. Estuaries 16: 512–520. doi:10.2307\u002F1352598.\nWalker, C.F., M.J. Harvey, S.J. Bury, and F.H. Chang. 2000. Biological and physical controls on dissolved dimethyl sulfide over the north-eastern continental shelf of New Zealand. Journal of Sea Research 43: 253–264. doi:10.1016\u002FS1385-1101(00)00017-4.\nWalsh, R.S., G.A. Cutter, W.M. Dunstan, J. Radford-Knoery, and J.T. Elder. 1994. The biogeochemistry of hydrogen sulfide: phytoplankton production in the surface ocean. Limnology and Oceanography 39: 941–948.\nWatts, S.F. 2000. The mass budget of carbonyl sulfide, dimethyl sulfide, carbon disulfide and hydrogen sulfide. Atmospheric Environment 34: 761–779. doi:10.1016\u002FS1352-2310(99)00342-8.\nZepp, R.G., and M.O. Andreae. 1994. Factors affecting the production of OCS in seawater. Geophysical Research Letters 21: 2813–2816. doi:10.1029\u002F94GL03083.\nZhang, L., R.S. Walsh, and G.A. Cutter. 1998. Estuarine cycling of carbonyl sulfide: production and sea–air flux. Marine Chemistry 61: 127–142. doi:10.1016\u002FS0304-4203(98)00015-2.",{"EN":763},"Concentrations of volatile hydrogen sulfide (H2S), carbonyl sulfide (OCS), methane thiol (MeSH), dimethyl sulfide (DMS), and dimethyl disulfide (DMDS) in the Seine estuary (France) were investigated in spring 2005 using samples collected from the first meter beneath the surface. Levels of dissolved metals (Ag, Cd, Cu, Zn, Ni, Co, Pb), suspended particulate matter, and particular organic carbon were also assessed. Maximum concentrations were 0.80 nM for H2S, 0.64 nM for OCS, 3.06 nM for MeSH, 11.06 nM for DMS, and 1.18 nM for DMDS, and different features were observed for the five volatile reduced sulfur compounds (VRSCs). Experiments were conducted to determine silver–VRSC conditional stability constants. 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Randlett, D.C. White, and P.S. Curtis. 1996. Soil microbial communities beneath Populus grandidentata grown under elevated atmospheric CO2. Ecological Applications 6: 257–262.",{"EN":1132},"Many aquatic ecosystems are experiencing a decline in their oxygen (O2) content and this is predicted to continue. Implications of this change on several properties of bacterioplankton (heterotrophic prokaryotes) remain however are poorly known. In this study, oxic samples (∼170 μM O2 = controls) from an oligohaline region of the Scheldt Estuary were purged with N2 to yield low-O2 samples (∼69 μM O2 = treatments); all were amended with 13C-glucose and incubated in dark to examine carbon incorporation and cell size of heterotrophic prokaryotes, and relationships between organic matter (OM) degradation and phosphate (P) availability in waters following O2 loss. Stable isotope (13C) probing of phospholipid fatty acids (PLFA) and flow cytometry were used. In samples that have experienced O2 loss, PLFA biomass became higher, prokaryotic cells had significantly larger size and higher nucleic acid content, but P concentrations was lower, compared to controls. P concentration and OM degradation were positively related in controls, but uncoupled in low-O2 samples. Moreover, the dominant PLFA 16:1ω7c (likely mainly from Gram-negative bacteria) and the nucleic acid content of heterotrophic prokaryotic cells in low-O2 samples explained (62–72 %) differences between controls and low-O2 samples in P amounts. Shortly after incubations began, low-O2 samples had consistently lower bacterial PLFA 13C-enrichments, suggesting involvement of facultatively anaerobic metabolism in carbon incorporation, and supporting the view that this metabolic pathway is widespread among pelagic bacteria in coastal nutrient-rich ecosystems. Estimates based on 13C-enrichment of PLFAs indicated that grazing by protozoa on some bacteria was stronger in low-O2 samples than in controls, suggesting that the grazing pressure on some heterotrophic prokaryotes may increase at the onset of O2 deficiency in nutrient-rich aquatic systems. These findings also suggest that physiological responses of heterotrophic prokaryotes to O2 loss in such ecosystems include increases in cell activity, high carbon incorporation, and possibly phosphorus retention by cells that may contribute to reduce phosphate availability in waters.",{"EN":1134},"Effects of Oxygen Loss on Carbon Processing and Heterotrophic Prokaryotes from an Estuarine Ecosystem: Results from Stable Isotope Probing and Cytometry Analyses",{"VOID":1136},"10.1007\u002Fs12237-015-0053-1","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs12237-015-0053-1",[1139,1166,1193,1205,1217],{"id":1140,"sortIndex":284,"researcher":20,"roles":1141,"affiliations":1142,"properties":1163},"3c57a8da-e031-449e-8815-40232fc7a2c4",[219],[1143,1155],{"id":1144,"sortIndex":133,"affiliation":1145,"properties":1154},"761f60a2-bca5-423c-9f5e-c55f1ccc5726",{"id":1146,"createTime":1147,"updateTime":1148,"relativeEntities":1149,"slug":1150,"properties":1151,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"9b1dd8a7-3b03-4298-a28f-935794947529","2023-12-19T07:09:44.974+00:00","2024-10-13T23:02:48.688+00:00",[],"Faculty-of-Geosciences-Utrecht-University-Utrecht-The-Netherlands",{"title":1152},{"VI":1153},"Faculty of Geosciences, Utrecht University, Utrecht, The Netherlands",{},{"id":20,"sortIndex":21,"affiliation":1156,"properties":20},{"id":1157,"createTime":1158,"updateTime":1158,"relativeEntities":1159,"slug":20,"properties":1160,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"b608ea76-e3f5-40b8-90ea-fcdbdc94dbe6","2024-02-11T20:02:09.864+00:00",[],{"title":1161},{"VI":1162},"Department of Ecosystem Studies, Netherlands Institute for Sea Research (NIOZ), Yerseke, The Netherlands",{"title":1164},{"VI":1165},"Jack J. Middelburg",{"id":1167,"sortIndex":21,"researcher":20,"roles":1168,"affiliations":1169,"properties":1190},"18c63583-6a67-4ee6-bd30-7e039b4fa870",[219],[1170,1182],{"id":1171,"sortIndex":133,"affiliation":1172,"properties":1181},"b1eed4b2-be98-4c92-ba27-8005b14970c5",{"id":1173,"createTime":1174,"updateTime":1175,"relativeEntities":1176,"slug":1177,"properties":1178,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"59fa209d-fc13-4e05-97cf-851c12289ee9","2023-12-14T05:40:03.590+00:00","2024-09-27T12:17:48.885+00:00",[],"D%C3%A9partement-des-Sciences-Biologiques-Universit%C3%A9-du-Qu%C3%A9bec-%C3%A0-Montr%C3%A9al-Montr%C3%A9al-Canada",{"title":1179},{"VI":1180},"Département des Sciences Biologiques, Université du Québec à Montréal, Montréal, Canada",{},{"id":20,"sortIndex":21,"affiliation":1183,"properties":20},{"id":1184,"createTime":1185,"updateTime":1185,"relativeEntities":1186,"slug":20,"properties":1187,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"b830d533-d7a3-4f17-bef1-cf37bd798b27","2024-02-11T20:02:09.807+00:00",[],{"title":1188},{"VI":1189},"INRA, UMR CARRTEL 042, F-74203, Thonon-Les-Bains, France",{"title":1191},{"VI":1192},"Rémy D. 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Aquatic Botany 8: 209–253.\nVerhoeven, J.T.A., and W.V. Vierssen. 1978. Structure of macrophyte dominated communities in two brackish lagoons on the Island of Corsica, France. Aquatic Botany 5: 77–86.\nWFD European Union. 2000. Directive 2000\u002F60\u002FEC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy. Official Journal of the European Communities L327(43): 1–72.\nZimmermann, U., and E. Steudle. 1971. Effects of potassium concentration and osmotic pressure of sea water on the cell-turgor pressure of Chaetomorpha linum. Marine Biology 11(2): 132–137.",{"EN":1275},"Rice cultivation in the Ebro Delta (Catalonia, Spain) has inverted the natural hydrological cycles of coastal lagoons and decreased water salinities for over 150 years. Adjustments in the water management practices—in terms of source and amount of freshwater inputs—have resulted in changes in the diversity, distribution and productivity of submerged angiosperms. Between the 1970s and late 1980s, a massive decline of the aquatic vegetation occurred in the Encanyissada–Clot and Tancada lagoons, but little information on the status is available after the recovery of macrophytes in the 1990s. Here, we evaluate the influence of salinity regimes resulting from current water management practices on the composition, distribution, seasonal abundance and flowering rates of submersed macrophytes, as well as on the occurrence of epiphyte and drift macroalgae blooms in three coastal lagoons. Our results show that Ruppia cirrhosa is the dominant species in the Encanyissada lagoon (185.97 ± 29.74 g DW m−2 year−1; 12–27 ‰ salinity) and the only plant species found in the Tancada lagoon (53.26 ± 10.94 g DW m2 year−1; 16–28 ‰ salinity). Flowering of R. cirrhosa (up to 1,011 ± 121 flowers m−2) was only observed within the Encanyissada and suggests that mesohaline summer conditions may favor these events. In contrast, low salinities in Clot lagoon (∼3–12 ‰) favor the development of Potamogeton pectinatus (130.53 ± 13.79 g DW m2 year−1) with intersperse R. cirrhosa (8.58 ± 1.71 g DW m−2) and mixed stands of P. pectinatus and Najas marina (up to ∼57 g DW m−2 year−1) in some reduced areas. The peak biomasses observed during the study are 88 to 95 % lower than maximum values reported in the literature at similar salinities, and there is also little or no recovery in some areas compared to last reports more than 20 years ago. The main management actions to restore the natural diversity and productivity of submersed angiosperms, such as the recovering of the seagrass Zostera noltii, should be the increase of salinity during the period of rice cultivation, by reducing freshwater inputs and increasing flushing connections with the bays.",{"EN":1277},"Spatio-Temporal Patterns of Submerged Macrophytes in Three Hydrologically Altered Mediterranean Coastal Lagoons",{"VOID":1279},"10.1007\u002Fs12237-012-9570-3","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs12237-012-9570-3",[1282,1297,1309],{"id":1283,"sortIndex":170,"researcher":20,"roles":1284,"affiliations":1285,"properties":1294},"1669a4ed-dc3b-4fb7-8604-4dbaa969736b",[219],[1286],{"id":20,"sortIndex":21,"affiliation":1287,"properties":20},{"id":1288,"createTime":1289,"updateTime":1289,"relativeEntities":1290,"slug":20,"properties":1291,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"9e2bb79f-d399-435f-8396-b74b047ed46b","2023-12-27T15:55:50.088+00:00",[],{"title":1292},{"VI":1293},"IRTA Aquatic Ecosystems, Sant Carles de la Ràpita, Spain",{"title":1295},{"VI":1296},"Carles Ibáñez",{"id":1298,"sortIndex":21,"researcher":20,"roles":1299,"affiliations":1300,"properties":1306},"18102aae-eda7-4c87-b577-c607fa1cc2c8",[219],[1301],{"id":20,"sortIndex":21,"affiliation":1302,"properties":20},{"id":1288,"createTime":1289,"updateTime":1289,"relativeEntities":1303,"slug":20,"properties":1304,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},[],{"title":1305},{"VI":1293},{"title":1307},{"VI":1308},"Patricia 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Caiola",{"url":1280,"publisher":1322,"properties":1350},{"id":6,"createTime":7,"updateTime":8,"relativeEntities":1323,"slug":10,"properties":1324,"entityType":18,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21,"subjectFields":1328,"manageAffiliations":1329,"indexDatabases":1330,"url":20,"thumbnailPath":20,"statistic":1345,"gsStatistic":20,"type":20,"analyzePriority":20},[],{"issn":1325,"eissn":1326,"title":1327},{"VOID":13},{"VOID":15},{"EN":17},[],[],[1331,1338],{"id":72,"indexDatabase":1332,"url":87,"indexYears":20,"academicFieldIds":1337,"indexDatabaseRanking":20},{"id":74,"createTime":75,"updateTime":76,"relativeEntities":1333,"label":1334,"description":1335,"key":83,"publicationTags":1336,"standard":20},[],{"EN":79,"VI":79},{"VI":81,"EN":82},[85,86],[89,90],{"id":92,"indexDatabase":1339,"url":105,"indexYears":106,"academicFieldIds":1344,"indexDatabaseRanking":111},{"id":94,"createTime":95,"updateTime":96,"relativeEntities":1340,"label":1341,"description":1342,"key":102,"publicationTags":1343,"standard":20},[],{"EN":99,"VI":99},{"EN":99,"VI":101},[104],[108,109,110],{"impactFactor":21,"impactFactorByYear":1346,"i10Index":126,"i10IndexLast5Year":127,"totalPublication":128,"totalPublicationByYear":1347,"totalCitation":150,"totalCitationByYear":1348,"totalCitationPerPublication":171,"totalCitationPerPublicationByYear":1349,"hindexLast5Year":191,"hindex":191},{"2012":114,"2013":115,"2014":116,"2015":117,"2016":118,"2017":119,"2018":120,"2019":121,"2020":122,"2021":123,"2022":124,"2023":125},{"1960":67,"1973":130,"1981":67,"1985":131,"1993":132,"1995":133,"2006":134,"2007":135,"2008":136,"2009":137,"2010":138,"2011":139,"2012":140,"2013":141,"2014":142,"2015":143,"2016":143,"2017":144,"2018":145,"2019":146,"2020":147,"2021":148,"2022":136,"2023":144,"2024":149},{"2006":152,"2007":153,"2008":154,"2009":155,"2010":156,"2011":157,"2012":158,"2013":159,"2014":160,"2015":161,"2016":162,"2017":163,"2018":164,"2019":165,"2020":166,"2021":167,"2022":168,"2023":169,"2024":170},{"2006":173,"2007":174,"2008":175,"2009":176,"2010":177,"2011":178,"2012":179,"2013":180,"2014":181,"2015":182,"2016":183,"2017":184,"2018":185,"2019":186,"2020":187,"2021":188,"2022":187,"2023":189,"2024":190},{"volume":1351,"pages":1353},{"VOID":1352},"36",{"VOID":1354},"414-429","2012-11-15",2012,{"id":1358,"createTime":1359,"updateTime":1360,"relativeEntities":1361,"slug":1362,"properties":1363,"entityType":211,"verifyStatus":212,"verifyTime":1360,"verifyNote":213,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21,"primaryUrl":1372,"fullTextUrl":20,"authors":1373,"publicationType":375,"publisherRelationship":1452,"citationCount":20,"citationInfo":20,"publishDate":1486,"publishYear":1487,"citationAnalyzeStatus":19,"lastCitationAnalyze":20,"indexDatabases":20,"openAccess":20,"references":20,"isForceReanalyzing":412},"5d46f230-1091-4d94-ae00-b0a1cc0bd1c0","2023-12-27T05:58:03.559+00:00","2025-02-14T23:49:38.541+00:00",[],"Distribution-of-a-Coastal-Delphinid-Under-the-Impact-of-Long-Term-Habitat-Loss-Indo-Pacific-Humpback-Dolphins-off-Taiwan-s-West-Coast",{"references":1364,"abstract":1366,"title":1368,"doi":1370},{"VOID":1365},"Araújo, 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In Primates and Cetaceans: Field Research and Conservation of Complex Mammalian Societies, eds. J. Yamagiwa, and L. Karczmarski., 249–272. Japan: Springer.\nHuang, S.-L., Y. Hao, Z. Mei, S.T. Turvey, and D. Wang. 2012a. Common pattern of population decline for freshwater cetacean species in deteriorating habitats. Freshwater Biology 57: 1266–1276.\nHuang, S.-L., L. Karczmarski, J. Chen, R. Zhou, W. Lin, H. Zhang, H. Li, and Y. Wu. 2012b. Demography and population trends of the largest population of Indo-Pacific humpback dolphins. Biological Conservation 147: 234–242.\nHuang, S.-L., M.-Y. Chang, Y.-T. Wang, C.-W. Chang, S.-H. Lin, and W.-N. Tzeng. 2013. Diversity loss of fish fauna due to urbanization in river catchments. In The International Conference on Challenges in Aquatic Sciences. Keelug: National Taiwan Ocean University.\nHuang, S.-L., W.-L. Chang, and L. Karczmarski. 2014. Population trend and vulnerability of humpback dolphins Sousa chinensis off the west coast of Taiwan. 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Bulletin of Marine Science 88: 885–902.\nWang, J.Y., S.C. Yang, and S.K. Hung. 2015. Diagnosability and description of a new subspecies of Indo-Pacific humpback dolphin, Sousa chinensis (Osbeck, 1765), from the Taiwan Strait. Zoological Studies 54: 36–51.\nWeir, C.R., and T. Collins. 2016. A review of the geographical distribution and habitat of the Atlantic humpback dolphin (Sousa teuszii). Advances in Marine Biology 72: 79–117.\nWikramanayake, E.D., E. Dinerstein, J.G. Robinson, U. Karanth, A. Rabinowitz, D. Olson, T. Mathew, P. Hedao, M. Conner, G. Hemley, and D. Bolze. 1998. An ecology-based method for defining priorities for large mammal conservation: the tiger as case study. Conservation Biology 12: 865–878.\nYeh, C.-H. 2011. Distribution Prediction and Ranging Pattern of Indo-Pacific Humpback Dolphins (Sousa chinensis) in Taiwan. Master Thesis. National Taiwan University, Taipei, Taiwan.\nYu, H.-Y., T.-H. Lin, W.-L. Chang, and L.-S. Chou. 2010. Using the mark-recapture method to estimate the population size of Sousa chinensis in Taiwan. in Workshop on Population Connectivity and Conservation of Sousa chinensis off Chinese Coast, Nanjing, China.",{"EN":1367},"For the Indo-Pacific humpback dolphin, Sousa chinensis, an obligatory shallow water inshore species, the degradation of coastal habitats can have major consequences for population persistence and distribution. Off Taiwan’s west coast (TWC), these animals are predominantly seen in two areas separated by a stretch of coast with only sporadic sightings, suggesting that either (a) only two sectors of TWC offer sufficiently suitable habitat for the dolphins or (b) a recent environmental change limits the population connectivity. We measured the extent of habitat destruction due to land reclamation off TWC since 1972 using a habitat integrity index (HII) and applied general linear models (GLMs) to compare HII with sightings of dolphins per unit effort (SPUE). While early Landsat data reveal extensive continuity and diversity of coastal habitats, by 2013, a total area of over 222 km2 was lost to land reclamation (23 % of dolphin habitat and 40 % of dolphin foraging habitat). GLM analysis showed a significant relationship between HII and SPUE; the lower HII the lower SPUE, indicating that off TWC, the current discontinuous distribution of humpback dolphins is likely due to a different extent of habitat degradation rather than natural patchiness of their environment. We emphasize that the history of coastal habitat alteration must be considered when interpreting cetacean distribution from survey data and formulating habitat management decisions, especially in areas experiencing extensive anthropogenic coastal change.",{"EN":1369},"Distribution of a Coastal Delphinid Under the Impact of Long-Term Habitat Loss: Indo-Pacific Humpback Dolphins off Taiwan’s West Coast",{"VOID":1371},"10.1007\u002Fs12237-016-0146-5","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs12237-016-0146-5",[1374,1389,1401,1413,1425,1440],{"id":1375,"sortIndex":21,"researcher":20,"roles":1376,"affiliations":1377,"properties":1386},"89d4c2c3-1d25-491f-906d-2004eea0c04a",[219],[1378],{"id":20,"sortIndex":21,"affiliation":1379,"properties":20},{"id":1380,"createTime":1381,"updateTime":1381,"relativeEntities":1382,"slug":20,"properties":1383,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},"d5c0cdbf-f1a6-4bf7-9b21-7f15801025f2","2023-12-27T05:58:03.615+00:00",[],{"title":1384},{"VI":1385},"The Swire Institute of Marine Science and School of Biological Sciences, The University of Hong Kong, Cape d’Aguilar, Hong Kong",{"title":1387},{"VI":1388},"Leszek Karczmarski",{"id":1390,"sortIndex":133,"researcher":20,"roles":1391,"affiliations":1392,"properties":1398},"729b5f18-6749-4c9c-b4b0-dd11f57b2eb9",[219],[1393],{"id":20,"sortIndex":21,"affiliation":1394,"properties":20},{"id":1380,"createTime":1381,"updateTime":1381,"relativeEntities":1395,"slug":20,"properties":1396,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},[],{"title":1397},{"VI":1385},{"title":1399},{"VI":1400},"Shiang-Lin Huang",{"id":1402,"sortIndex":316,"researcher":20,"roles":1403,"affiliations":1404,"properties":1410},"64967338-3b10-4ebc-8f97-35b8ea316e0f",[219],[1405],{"id":20,"sortIndex":21,"affiliation":1406,"properties":20},{"id":1380,"createTime":1381,"updateTime":1381,"relativeEntities":1407,"slug":20,"properties":1408,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},[],{"title":1409},{"VI":1385},{"title":1411},{"VI":1412},"Wei-Lun Chang",{"id":1414,"sortIndex":284,"researcher":20,"roles":1415,"affiliations":1416,"properties":1422},"e1ebeb67-14bb-417f-9428-d67bb6c94849",[219],[1417],{"id":20,"sortIndex":21,"affiliation":1418,"properties":20},{"id":1380,"createTime":1381,"updateTime":1381,"relativeEntities":1419,"slug":20,"properties":1420,"entityType":56,"verifyStatus":19,"verifyTime":20,"verifyNote":20,"syncStatus":19,"languages":20,"translateLanguages":20,"viewCount":21},[],{"title":1421},{"VI":1385},{"title":1423},{"VI":1424},"Stephen C.Y. 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