Academic literature on the topic 'Wetland restoration'

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Journal articles on the topic "Wetland restoration"

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Zhang, Aiying, Zhixia Ying, Xunyu Hu, and Mingjian Yu. "Phylogenetic Diversity of Wetland Plants across China." Plants 10, no. 9 (September 6, 2021): 1850. http://dx.doi.org/10.3390/plants10091850.

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Accelerating and severe wetland loss has made wetland restoration increasingly important. Current wetland restorations do not take into consideration the ecological adaptability of wetland plants at large scales, which likely affects their long-term restoration success. We explored the ecological adaptability, including plant life forms and phylogenetic diversity, of plants across 28 wetlands in China. We found that perennial herbs were more common than annual herbs, with the proportion of perennial herbs accounting for 40–50%, 45–65%, 45–70%, 50–60%, and 60–80% of species in coastal wetlands, human-made wetlands, lake wetlands, river wetlands, and marsh wetlands, respectively. A ranking of phylogenetic diversity indices (PDIs) showed an order of marsh < river < coastal < lake < human-made, meaning that human-made wetlands had the highest phylogenetic diversity and marsh wetlands had the lowest phylogenetic diversity. The nearest taxon index (NTI) was positive in 23 out of 28 wetlands, indicating that species were phylogenetically clustered in wetland habitats. Dominant species tended to be distantly related to non-dominant species, as were alien invasive species and native species. Our study indicated that annual herbs and perennial herbs were found in different proportions in different types of wetlands and that species were phylogenetically clustered in wetland habitats. To improve wetland restoration, we suggest screening for native annual herbs and perennial herbs in proportions that occur naturally and the consideration of the phylogenetic similarity to dominant native species.
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Xu, Nan, Haiyan Li, Chunyu Luo, Hongqiang Zhang, and Yi Qu. "Exploring Spatial Relationship between Restoration Suitability and Rivers for Sustainable Wetland Utilization." International Journal of Environmental Research and Public Health 19, no. 13 (July 1, 2022): 8083. http://dx.doi.org/10.3390/ijerph19138083.

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Wetlands are important ecosystems for biodiversity preservation and environmental regulation. However, the integrity of wetland ecosystems has been seriously compromised and damaged due to the reckless and indiscriminate exploitation of wetland resources during economic development by human society. Hence, wetland restoration has now attracted wide attention. Understanding wetland restoration suitability and its relationship with river grade and river distance is an important step in further implementing wetland restoration and ensuring an orderly wetland development and utilization. In this study, wetland restoration suitability is evaluated combining natural and human factors. Taking its result as an important basis, the spatial distribution characteristics of different levels of wetland restoration suitability are discussed for the studied region; the percentage distribution of different levels of wetland restoration suitability is analyzed for 10 km long buffer zones of rivers of different grades, and the association between the distribution of different levels of wetland restoration suitability and the river distance (2, 4, 6, 8, and 10 km) is also analyzed for different buffer zones of rivers in different grades. Our findings show that the spatial distribution of wetland restoration suitability is closely associated with the grade of rivers and the distance of the wetland patches from the river. The higher the river grade, the higher the percentage of the wetland with high restoration suitability within the same river distance. The percentage of wetlands with high restoration suitability has shown a notably decreasing trend as the river distance increases for the areas beside rivers of all grades, while the percentage of a wetland area with relatively high restoration suitability tends to increase as the river distance increases for the areas beside rivers of grade I and II and does not have a noticeable trend to change as the river distance changes for the area beside rivers of other grades. Results of this can provide technical support for wetland restoration suitability evaluation for plain areas, a spatial reference for wetland restoration prioritizing, and an orderly wetland development and utilization in future studies and planning.
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Xie, Wen Xia, Zhen Xu, and Kun Jie Zhu. "Review of Key Technique Research on the Field of Vegetation Restoration in Beach Wetlands." Advanced Materials Research 709 (June 2013): 948–51. http://dx.doi.org/10.4028/www.scientific.net/amr.709.948.

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The study wetland vegetation restoration technology system and representative beach wetland restoration projects at home and abroad are summarized. Technology system of wetland vegetation restoration mainly includes engineering technology and biological technology. Ecological restoration research of coastal wetland in China mainly concentrated in the Yellow River Delta, the southeast coastal mangrove wetlands, coastal beaches of Jiangsu and the coastal wetlands in Shanghai Fengxian District. Finally, the issues existed in current research field were pointed out. The research fields need to be strengthened for the detailed field investigation and laboratory analysis of soil, vegetation, hydrology, meteorology, etc. According to the actual situation of wetland beaches, wetland site type will be divided. Suitable salt-tolerant plant varieties should be filtered and the mudflat wetland vegetation recovery key technologies should be explored.
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Crumpton, W. G. "Using wetlands for water quality improvement in agricultural watersheds; the importance of a watershed scale approach." Water Science and Technology 44, no. 11-12 (December 1, 2001): 559–64. http://dx.doi.org/10.2166/wst.2001.0880.

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Agricultural applications of fertilizers and pesticides have increased dramatically since the middle 1960s, and agrochemical contamination of surface and groundwater has become a serious environmental concern. Since the mid-1980s, a variety of state and federal programs have been used to promote wetland restoration, and these continuing efforts provide a unique opportunity for water quality improvement in agricultural watersheds. However, wetland restorations have been motivated primarily by concern over waterfowl habitat loss, and model simulations suggest that commonly used site selection criteria for wetland restorations may be inadequate for water quality purposes. This does not lessen the promise of wetlands for water quality improvement in agricultural watersheds, but rather emphasizes the need for watershed scale approaches to wetland siting and design. Water quality is best viewed from a watershed perspective, and watershed scale endpoints should be explicitly considered in site selection for wetland restoration.
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Carberry, Brendan, Tom A. Langen, and Michael R. Twiss. "Surface Water Quality Differs between Functionally Similar Restored and Natural Wetlands of the Saint Lawrence River Valley in New York." Land 10, no. 7 (June 27, 2021): 676. http://dx.doi.org/10.3390/land10070676.

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We tested the hypothesis that upland wetland restorations provide the same quality of wetland, in terms of ecosystem services and biodiversity, as natural wetlands in the St. Lawrence River Valley. Water quality (pH, alkalinity, colored dissolved organic matter, phytoplankton community composition, chlorophyll-a, fecal coliform, total phosphorus, dissolved nitrate, turbidity, specific conductivity) in 17 natural and 45 restored wetlands was compared to determine whether wetland restoration provided similar physicochemical conditions as natural wetlands in the Saint Lawrence River Valley of northeastern New York State. Natural wetlands were more acidic, which was hypothesized to result from the avoidance of naturally acidic regions by farmers seeking to drain wetlands for crop and pasture use. Natural wetlands had significantly greater fecal coliform concentrations. Restored wetlands had significantly greater specific conductivity and related ions, and this is attributed to the creation of wetlands upon marine clay deposits. Other water quality indicators did not differ between restored and natural wetlands. These findings confirm other research at these same wetlands showing no substantial differences between restored and natural wetlands in major biotic indicators. Thus, we conclude that wetland restoration does result in wetlands that are functionally the same as the natural wetlands they were designed to replicate.
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Cao, Rui, Jingyu Wang, Xue Tian, Yuanchun Zou, Ming Jiang, Han Yu, Chunli Zhao, and Xiran Zhou. "Post-Restoration Monitoring of Wetland Restored from Farmland Indicated That Its Effectiveness Barely Measured Up." Water 16, no. 3 (January 26, 2024): 410. http://dx.doi.org/10.3390/w16030410.

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In the context of wetland restoration, the reconstruction of an ecosystem’s structure typically manifests within a relatively short timeframe, while the restoration of its function often necessitates an extended period of time following the implementation of restoration measures. Consequently, it becomes imperative to engage in the comprehensive, long-term dynamic monitoring of restored wetlands to capture timely information regarding the ecological health status of wetland restoration. In this paper, we aimed to precisely assess the ecosystem health of a typical wetland that had been converted from farmland to wetland in Fujin National Wetland Park in 2022. We selected 18 ecological, social, and economic indicators to establish a wetland ecological health evaluation model, and then used the method of an analytic hierarchy process (AHP) to calculate the weights for each indicator and acquire the ecological health index (EHI) score. The results of our study revealed that the ecosystem health index was 3.68, indicating that the FNWP wetland ecosystem was in “good” condition; this result was mainly affected by wetland water quality (0.382). The ecological health assessment of restored wetlands can monitor wetland ecological resources and provide a scientific basis for the management and protection of restored wetlands.
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Kameri Ochoko, John, Suzan Luyiga, and Bernad Barasa. "The Mediating Role of Management Functions (Planning, Implementation, and Control) in Influencing the Restoration of Limoto Wetland." American Journal of Environment Studies 6, no. 2 (May 17, 2023): 1–18. http://dx.doi.org/10.47672/ajes.1465.

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Purpose: The purpose of this study was to analyze the gap between wetland management functions and the extent of wise use and sustainable harnessing of livelihood opportunities through restoration programs. This study contributes to the comprehension of wetland management functions concerning wetland restoration through the promotion of sustainable livelihoods. Methodology: A cross-sectional research design was adopted. Both quantitative and qualitative data were collected using Focus Group Discussions (FGD) and interviews. FGD was conducted with five groups of beneficiaries of livelihood options. Interviews were carried out with seven key informants who were thought to be knowledgeable about the wetland restoration alternative livelihood options. These included local council chairmen from communities near the wetland, village opinion leaders, district natural resources officers, IUCN Representatives, NEMA officials, and the wetland department. Findings: Results showed a positive but insignificant relationship between planning function and restoration activities. Furthermore, results also indicated a negative significant relationship between implementation and restoration activities. Finally, findings revealed that there was a relationship between the control function and restoration activities. It was found out that Wetland restoration is a process that helps to transform the wetland area that has been impacted by human or natural activity into an area that can sustain native habitats. Wetlands cover 6% of global and 13% of Uganda's land cover. Over the past forty-five years, wetlands have lost 30% and 36% of land cover globally and in Uganda respectively. Unique Contribution to Theory, Practice, and Policy: Many wetlands, particularly those in rural Uganda are, however, getting degraded through mainly conversion of land use to agriculture, exploitation, and settlements despite the existing resource management regime. The study recommends inclusive management functions to achieve a successful wetland restoration.
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Ge, Xiu Li, Ren Qing Wang, and Jian Liu. "The Comparison of the Community Features between the Constructed Wetland and the Natural Wetland in Nansi Lake." Advanced Materials Research 518-523 (May 2012): 5238–43. http://dx.doi.org/10.4028/www.scientific.net/amr.518-523.5238.

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Thirteen typical plant communities were investigated in Xinxuehe constructed wetland restored for five years and in Gaolou natural wetland restored naturally for eight years. Both wetlands are located in Nansi Lake area. The species composition, coverage, aboveground biomass and biodiversity indices were compared between the communities from the constructed wetland and the natural wetland. The results showed that the constructed wetland and the natural wetland had similar emergent species and typical species of their own, however neither coverage nor aboveground biomass showed significant differences. In the meanwhile, we found that the biodiversity of natural wetland is relatively higher than the constructed wetland. For the wetland restoration and the water quality quick improving, it is suitable to use artificial ways to promote the restoration of wetlands which converted from the farmland in Nansi Lake area; in the other hand, the natural wetland restoration is more valuable for the biodiversity conservation in the long run.
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Zhao, Dandan, Daiji Wan, Jian Yang, Jiping Liu, Zhicheng Yong, and Chongya Ma. "Effects of restoration years on soil nitrogen and phosphorus in inland salt marshes." PeerJ 12 (January 16, 2024): e16766. http://dx.doi.org/10.7717/peerj.16766.

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Inland salt marsh wetlands have very important ecological functions in semi-arid areas. However, degradation and soil desertification have impacted these areas, making it necessary to study the impact of wetland restoration years on the soil quality of salt marsh wetland. We used remote sensing methods, field surveys, and inquiries to examine the seasonal profile effects of two-, four-, and six-year restoration periods on total nitrogen (TN), total phosphorus (TP) and the ratio of nitrogen to phosphorus (N:P) in P. australis and S. triqueter wetland natural states. Our results showed that soil TN in P. australis wetland in restored conditions was higher than that in natural conditions. The average soil TP of the S. triqueter wetlands at 0–10 cm, 10–20 cm, 20–30 cm, and 30–40 cm layers was 0.36 g/kg, 0.31 g/kg, 0.21 g/kg, and 0.17 g/kg s in September, respectively. The soil TP of the S. triqueter wetland increased slightly over the entire growing season. The restoration years had a great influence on the soil TP of the S. triqueter wetland from May to July. The soil TN in the P. australis wetland was almost restored to its natural condition in each layer during the six-year restoration period. The soil TP of the S. triqueter wetland was higher in the restored two-year period and showed a decreasing trend with an increased soil depth. Our conclusions can significantly guide the restoration of inland salt marsh wetlands.
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Ma, Chun, Guang Yu Zhang, Xiao Chun Zhang, Bin Zhou, and Wen Xin Jiang. "Water Resource Management for Wetland Restoration Engineering in Tianjin Coastal Area in China." Advanced Materials Research 518-523 (May 2012): 4333–36. http://dx.doi.org/10.4028/www.scientific.net/amr.518-523.4333.

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Wetland is one of the most diverse ecosystem and important habitats. However, degradation and loss of wetlands increased with anthropologic factors. Thus, the research of wetland restoration has become the emphasis and imperative issue. Water plays an important role in ecological evolution of the wetlands, and water requirement is a key step for water resource management of wetland restoration engineering. This research deals with the analysis of water requirement for wetland restoration engineering in a case study in Bohai Bay. The results show that the total water requirement in the study area are (0.18~0.28)×109m3, (0.54~0.81)×109m3, (1.21~1.41)×109m3 to reach the basic objective, moderate objective and perfect objective, respectively.
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Dissertations / Theses on the topic "Wetland restoration"

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Porej, Deni. "Faunal aspects of wetland creation and restoration." Connect to this title online, 2004. http://rave.ohiolink.edu/etdc/view?acc%5Fnum=osu1078327758.

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Thesis (Ph. D)--Ohio State University, 2004.
Title from first page of PDF file. Document formatted into pages; contains xii, 120 p.; also includes graphics. Available online via OhioLINK's ETD Center.
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Porter, Abigail M. "Wetlands in the Urban Landscape: The Process of Wetlands Restoration in Baltimore, Maryland and Paris, France." Ohio University / OhioLINK, 2003. http://rave.ohiolink.edu/etdc/view?acc_num=ohiou1058301973.

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Sherrill, Ursula Rose. "The restoration of wetland functions at the Rio Bosque Wetlands Park in El Paso, Texas, USA." To access this resource online via ProQuest Dissertations and Theses @ UTEP, 2007. http://0-proquest.umi.com.lib.utep.edu/login?COPT=REJTPTU0YmImSU5UPTAmVkVSPTI=&clientId=2515.

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Grundling, Althea Theresa. "Evaluation of remote sensing sensors for monitoring of rehabilitated wetlands." Diss., Prtoria: [s.n.], 2004. http://upetd.up.ac.za/thesis/available/etd-05132005-145705/.

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Magnusson, Gisele Marie. "Economic-ecological relationships in coastal wetland restoration /." View online ; access limited to URI, 2006. http://0-wwwlib.umi.com.helin.uri.edu/dissertations/dlnow/3225321.

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Bevington, Azure E. "Environmental Factors and Typha spp Dominance in Created Wetlands." W&M ScholarWorks, 2007. http://www.vims.edu/library/Theses/Bevington07.pdf.

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Gayaldo, Perry Fleming. "Eelgrass (Zostera marina) restoration techniques /." Thesis, Connect to this title online; UW restricted, 2002. http://hdl.handle.net/1773/5502.

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Newbold, Stephen Carlisle. "Targeting conservation activities : cost-effective wetlands restoration in the Central Valley of California /." For electronic version search Digital dissertations database. Restricted to UC campuses. Access is free to UC campus dissertations, 2002. http://uclibs.org/PID/11984.

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Thesis (Ph. D.)--University of California, Davis, 2002.
Degree granted in Ecology. Includes bibliographical references (leaves189-199). Also available via the World Wide Web. (Restricted to UC campuses)
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Marois, Darryl Evan. "Modeling Wetland Biogeochemistry and Restoration in South Florida." The Ohio State University, 2015. http://rave.ohiolink.edu/etdc/view?acc_num=osu1437578127.

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Huang, Jung-Chen. "Stream Restoration in the Midwest, USA." The Ohio State University, 2010. http://rave.ohiolink.edu/etdc/view?acc_num=osu1267464050.

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Books on the topic "Wetland restoration"

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An, Shuqing, and Limin Wang. Wetland Restoration. Berlin, Heidelberg: Springer Berlin Heidelberg, 2014. http://dx.doi.org/10.1007/978-3-642-54230-5.

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R, Herrera Jose, ed. International wetlands: Ecology, conservation, and restoration. New York: Nova Science Publishers, 2008.

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Roland, Bobbink, ed. Wetlands: Functioning, biodiversity conservation, and restoration. New York: Springer, 2008.

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Middleton, Beth. Wetland restoration, flood pulsing, and disturbance dynamics. New York: Wiley, 1999.

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Rheinhardt, Richard D. An evaluation of the effectiveness of existing North Carolina Department of Transportation wetland mitigation sites : phase 1 report. Raleigh, NC: Center for Transportation and the Environment, NC State University, 2000.

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Conservancy, California State Coastal, United States. Army. Corps of Engineers., and Jones & Stokes Associates., eds. Hamilton wetland restoration plan. [Oakland, Calif: The Conservancy, 1998.

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Albert, Dennis A. Between land and lake: Michigan's Great Lakes coastal wetlands. East Lansing, Mich: Michigan Natural Features Inventory, 2003.

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Interagency Workgroup on Wetland Restoration (U.S.). Una introducción y guía para unsuarios a la restauración, creación y mejoramiento de humedales: Una guía para el público que contiene : antecedentes sobre humedales y restauración, información, sobre planeamiento de proyectos, implementación y monitoreo, lista de recursos, contactos y fuentes de financiamiento. Washington, D.C.]: Administración Nacional de los Océanos y la Atmósfera, Agencia de Protección Ambiental, El Cuerpo de Ingenieros del Ejército, El Servicio de Pesca y Vida Silvestre de los Estados Unidos y El Servicio de Conservación de Recursos Naturales, 2003.

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Frenkel, Robert E. Restoration of the Salmon River salt marshes: Retrospect and prospect. Corvallis, Or: Dept. of Geosciences, Oregon State University, 1990.

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Schneller-McDonald, Karen. Wetland creation and restoration: Description and summary of the literature. Washington, DC: U.S. Dept. of the Interior, Fish and Wildlife Service, 1990.

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Book chapters on the topic "Wetland restoration"

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Zedler, Joy B., and Nick Miller. "Wetland Restoration." In The Wetland Book, 1–12. Dordrecht: Springer Netherlands, 2016. http://dx.doi.org/10.1007/978-94-007-6172-8_59-2.

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Streever, William. "Wetland Restoration." In Encyclopedia of Earth Sciences Series, 1898–904. Cham: Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-319-93806-6_353.

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Streever, William. "Wetland Restoration." In Encyclopedia of Earth Sciences Series, 1–7. Cham: Springer International Publishing, 2018. http://dx.doi.org/10.1007/978-3-319-48657-4_353-2.

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Zedler, Joy B., and Nick Miller. "Wetland Restoration." In The Wetland Book, 165–76. Dordrecht: Springer Netherlands, 2018. http://dx.doi.org/10.1007/978-90-481-9659-3_59.

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Ritchie, William, Katherine Pond, Edward J. Anthony, George Maul, Patricia L. Wiberg, Miles O. Hayes, Andrew D. Short, et al. "Wetland Restoration." In Encyclopedia of Coastal Science, 1081–86. Dordrecht: Springer Netherlands, 2005. http://dx.doi.org/10.1007/1-4020-3880-1_353.

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An, Shuqing, and Limin Wang. "Locational Features of Dalian Lake." In Wetland Restoration, 3–12. Berlin, Heidelberg: Springer Berlin Heidelberg, 2014. http://dx.doi.org/10.1007/978-3-642-54230-5_1.

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An, Shuqing, and Limin Wang. "Benefit Appraisal of the Wetland." In Wetland Restoration, 149–53. Berlin, Heidelberg: Springer Berlin Heidelberg, 2014. http://dx.doi.org/10.1007/978-3-642-54230-5_10.

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An, Shuqing, and Limin Wang. "Regional Evolution of Dalian Lake." In Wetland Restoration, 13–26. Berlin, Heidelberg: Springer Berlin Heidelberg, 2014. http://dx.doi.org/10.1007/978-3-642-54230-5_2.

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An, Shuqing, and Limin Wang. "Characteristics of Hydrologic Environment." In Wetland Restoration, 27–35. Berlin, Heidelberg: Springer Berlin Heidelberg, 2014. http://dx.doi.org/10.1007/978-3-642-54230-5_3.

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An, Shuqing, and Limin Wang. "Analysis on Pollution Source." In Wetland Restoration, 37–42. Berlin, Heidelberg: Springer Berlin Heidelberg, 2014. http://dx.doi.org/10.1007/978-3-642-54230-5_4.

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Conference papers on the topic "Wetland restoration"

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Haupt, Dale M., Christopher J. Bruce, and Brian P. Bledsoe. "Targeting Wetland Restoration Using GIS." In Wetlands Engineering and River Restoration Conference 1998. Reston, VA: American Society of Civil Engineers, 1998. http://dx.doi.org/10.1061/40382(1998)187.

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Hylton, Travis W. "Kawainui Marsh Wetland Restoration." In World Environmental and Water Resources Congress 2008. Reston, VA: American Society of Civil Engineers, 2008. http://dx.doi.org/10.1061/40976(316)310.

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Higgins, John M., D. El-Qousey, A. G. Abul-Azm, and M. Abdelghaffar. "Lake Manzala Engineered Wetland, Egypt." In Wetlands Engineering and River Restoration Conference 2001. Reston, VA: American Society of Civil Engineers, 2001. http://dx.doi.org/10.1061/40581(2001)49.

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DeBoice, John N. "Constructed Wetland Wastewater Treatment Facilities." In Wetlands Engineering and River Restoration Conference 1998. Reston, VA: American Society of Civil Engineers, 1998. http://dx.doi.org/10.1061/40382(1998)11.

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Walker, James R., Ying-Kueng Poon, Christopher K. Webb, and Michael P. Hemphill. "Tidal Wetland Planning and Design." In Wetlands Engineering and River Restoration Conference 1998. Reston, VA: American Society of Civil Engineers, 1998. http://dx.doi.org/10.1061/40382(1998)17.

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Webb, Christopher K. "Wetland Restoration at Bolsa Chica, California." In Wetlands Engineering and River Restoration Conference 2001. Reston, VA: American Society of Civil Engineers, 2001. http://dx.doi.org/10.1061/40581(2001)33.

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Boudreau, Russell H., Michael P. Hemphill, and Weixia Jin. "Engineering Considerations for Coastal Wetland Restoration." In Wetlands Engineering and River Restoration Conference 2001. Reston, VA: American Society of Civil Engineers, 2001. http://dx.doi.org/10.1061/40581(2001)89.

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Somerville, D. Eric, and Wade L. Nutter. "HGM Reference Standards and Wetland Restoration." In Wetlands Engineering and River Restoration Conference 1998. Reston, VA: American Society of Civil Engineers, 1998. http://dx.doi.org/10.1061/40382(1998)182.

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Davis, Mary M., and Jerry Ziewitz. "Evaluation of River Management Impacts on Riparian Wetland Functions Using the Wetland Hydrologic Index." In Wetlands Engineering and River Restoration Conference 1998. Reston, VA: American Society of Civil Engineers, 1998. http://dx.doi.org/10.1061/40382(1998)147.

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Vasilas, L. M., and B. L. Vasilas. "Wetland Restoration and Creation Design to Restore Wetland Functions." In Watershed Management Conference 2005. Reston, VA: American Society of Civil Engineers, 2005. http://dx.doi.org/10.1061/40763(178)6.

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Reports on the topic "Wetland restoration"

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Berkowitz, Jacob. Quantifying functional increases across a large-scale wetland restoration chronosequence. Engineer Research and Development Center (U.S.), August 2021. http://dx.doi.org/10.21079/11681/41500.

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Over 300,000 ha of forested wetlands have undergone restoration within the Mississippi Alluvial Valley region. Restored forest successional stage varies, providing opportunities to document wetland functional increases across a large-scale restoration chronosequence using the Hydrogeomorphic (HGM) approach. Results from >600 restored study sites spanning a 25-year chronosequence indicate that: 1) wetland functional assessment variables increased toward reference conditions; 2) restored wetlands generally follow expected recovery trajectories; and 3) wetland functions display significant improvements across the restoration chronosequence. A functional lag between restored areas and mature reference wetlands persists in most instances. However, a subset of restored sites have attained mature reference wetland conditions in areas approaching or exceeding tree diameter and canopy closure thresholds. Study results highlight the importance of site selection and the benefits of evaluating a suite of wetland functions in order to identify appropriate restoration success milestones and design monitoring programs. For example, wetland functions associated with detention of precipitation (a largely physical process) rapidly increased under post restoration conditions, while improvements in wetland habitat functions (associated with forest establishment and maturation) required additional time. As the wetland science community transitions towards larger scale restoration efforts, effectively quantifying restoration functional improvements will become increasingly important.
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Yozzo, David J., and John P. Titre. Coastal Wetland Restoration Bibliography. Fort Belvoir, VA: Defense Technical Information Center, August 1997. http://dx.doi.org/10.21236/ada329280.

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Hill, Carlton L. Shoreline Stabilization Design and Wetland Restoration. Fort Belvoir, VA: Defense Technical Information Center, May 2001. http://dx.doi.org/10.21236/ada401154.

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Berkowitz, Jacob, Christine VanZomeren, Nia Hurst, and Kristina Sebastian. An evaluation of soil phosphorus storage capacity (SPSC) at proposed wetland restoration locations in the western Lake Erie Basin. Engineer Research and Development Center (U.S.), September 2021. http://dx.doi.org/10.21079/11681/42108.

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Historical loss of wetlands coupled with excess phosphorus (P) loading at watershed scales have degraded water quality in portions of the western Lake Erie Basin (WLEB). In response, efforts are underway to restore wetlands and decrease P loading to surface waters. Because wetlands have a finite capacity to retain P, researchers have developed techniques to determine whether wetlands function as P sources or sinks. The following technical report evaluates the soil P storage capacity (SPSC) at locations under consideration for wetland restoration in collaboration with the Great Lakes Restoration Initiative (GLRI) and the H2Ohio initiative. Results indicate that the examined soils display a range of P retention capacities, reflecting historic land-use patterns and management regimes. However, the majority of study locations exhibited some capacity to sequester additional P. The analysis supports development of rankings and comparative analyses of areas within a specific land parcel, informing management through design, avoidance, removal, or remediation of potential legacy P sources. Additionally, the approaches described herein support relative comparisons between multiple potential wetland development properties. These results, in conjunction with other data sources, can be used to target, prioritize, justify, and improve decision-making for wetland management activities in the WLEB.
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Menuz, Diane, and Rebekah Downard. Opportunity for Improved Wetland Mitigation in Utah - In-Lieu Fee Mitigation Potential in Utah. Utah Geological Survey, September 2023. http://dx.doi.org/10.34191/ofr-756.

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Wetlands play a crucial role in watersheds and provide critical ecosystem functions, most notably, water quality improvement, fish and wildlife habitat, flood attenuation, drought mitigation, and carbon sequestration. Wetlands in Utah are regulated primarily by the federal government under the Clean Water Act (CWA), which requires mitigation to replace ecological services that are lost to permitted activities. Utah House Bill 118 (2022) directed the Utah Geological Survey to explore the potential for an In-Lieu Fee (ILF) mitigation program to improve wetland resources in Utah. An ILF program would allow entities seeking CWA permits to pay a fee to mitigate impacts to streams and wetlands rather than having to develop their own mitigation plans. To research the possible consequences of an ILF, we conducted document research and interviews with mitigation practitioners and wetland stakeholders and analyzed ten years of permit data. Interview participants agreed that an ILF would improve the quality of wetland mitigation projects, which currently are often small, isolated, and overrun with weeds. An ILF would also improve coordination between the various entities involved in natural resource protection, permitting, and restoration. Further, permittees would benefit from an ILF because it would streamline the permitting process. Research and input from current practitioners showcased that there were many options for running an ILF program that can work for Utah, which has few permitted wetland impacts compared to other, less arid states. The most effective way to build an ILF in Utah is to support a full-time ILF administrator to establish the program and develop and maintain strong relationships with regulators, restoration specialists, and those seeking permits. Based on historical permit rates, such a position could be funded by program fees after the program is established. The future of a self-sustaining ILF program is uncertain, however, due to the recent Sackett v. Environmental Protection Agency (EPA) Supreme Court decision which limited the types of wetlands that are regulated by the federal government. The expected reduction in wetland permitting creates a more challenging environment in which to operate an ILF program because permit fees will likely no longer support a full-time ILF administrator’s salary. At the same time, ensuring high quality mitigation will be more important than ever because there will be more unpermitted and thus unmitigated wetland impacts, leading to loss in ecological functions. Given these considerations, we recommend establishing a position for a wetland mitigation and restoration coordinator who can explore multiple options to preserve and restore wetlands in Utah, coordinate among agencies, and begin to implement an ILF program at a rate and scale appropriate to the new regulatory conditions. By investing in a wetland mitigation and restoration coordinator, the state can support voluntary restoration measures to increase wetland functions while at the same time improving mitigation outcomes for permittees and projects. Together, these actions will lead to healthier, more resilient wetlands that will protect the quality of life for all Utahns.
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King, D., and C. Bohlen. The cost of wetland creation and restoration. Final report. Office of Scientific and Technical Information (OSTI), August 1995. http://dx.doi.org/10.2172/91931.

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7

Pioneer Natural Resources. Beneficial Use of Drilling Waste - A Wetland Restoration Technology. Office of Scientific and Technical Information (OSTI), August 2000. http://dx.doi.org/10.2172/760020.

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8

Pioneer Natural Resources. Beneficial Use of Drilling Waste - A Wetland Restoration Technology. Office of Scientific and Technical Information (OSTI), July 1999. http://dx.doi.org/10.2172/760021.

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9

Simpson, Matthew, Megan Eldred, Sevvandi Jayakody, and Laura Mackenzie. Scaling up wetland conservation and restoration to deliver the Kunming-Montreal Global Biodiversity Framework: Guidance on including wetlands in National Biodiversity Strategy and Action Plans (NBSAPs) to boost biodiversity and halt wetland loss and degradation. Convention on Wetlands, May 2024. http://dx.doi.org/10.69556/strp.tr12.24.

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Wetland conservation and restoration is an essential component of delivering the Kunming-Montreal Global Biodiversity Framework (KM-GBF) vision of a world living in harmony with nature where “by 2050, biodiversity is valued, conserved, restored and wisely used, maintaining ecosystem services, sustaining a healthy planet and delivering benefits essential for all people.” This document supports the inclusion of ambitious wetland commitments and actions in National Biodiversity Strategies and Action Plans (NBSAPs) as a pivotal way of boosting biodiversity, to achieve the goals of both the Convention on Wetlands and the KM-GBF. This report focuses on the critical role of wetlands in achieving the 23 targets of the KM-GBF by 2030. It provides guidance to Parties to the CBD on how to incorporate the role and importance of wetlands and key actions into their NBSAPs in relation to each target. It also provides Contracting Parties to the Convention on Wetlands, with information on how to support delivery of the KM-GBF and achieve targets within the Fourth Strategic Plan of the Convention on Wetlands and the forthcoming Fifth Strategic Plan.
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Erdman, Charles, Heather Hendrixson, and undefined. Larval Lost River and shortnose sucker response to wetland restoration. The Nature Conservancy, July 2009. http://dx.doi.org/10.3411/col.07291948.

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