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Importance of Wetland Soils for Ecosystem Services

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www.ispecongre.org

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IMPORTANCE OF WETLAND SOILS FOR ECOSYSTEM SERVICES Mesut BUDAK

Hikmet Tokat

ekosistemlerde nadiren

--1 organik karbon (OC)

Tg OC yr-1

-2

Anahtar Kelimeler: Hidroloji

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Wetlands are among the biologically most productive ecosystems. Provision of nutrient, contribution to water and carbon cycles, soil formation, pollination of plants, control of diseases and pests, hydrology of the region, socio-economic structure and cultural values are important aspects of wetlands, in addition to the hosting of rarely found plants and animals in other ecosystems. Wetlands have a higher biological activity than many other ecosystems, therefore most contaminants in waste water are converted into biodegradable by-products or basic nutrients. Due to the importance of the ecosystem services provided by wetlands to human being, we have examined the current literature on wetlands to summarize importance in terms of ecosystem services. Previous studies have demonstrated that wetlands provide many ecosystem services to human beings and are the most productive ecosystems for the production of organic matter after tropical forests. High biomass productivity and very slow decomposition of organic matter in wetlands enable organic wastes to be stored as peat. The deposition of huge amount of organic matter makes wetlands an important carbon pool on earth surface. Increased carbon content in wetlands is believed to have an important contribution to the mitigation of global climate change. The study conducted in Austria

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organic carbon (OC). The annual carbon sequestration in wetland is reported as 0.75 Tg OC

yr-1 which is equivalent to annual US $ 28.02 million. One-year carbon sequestration in a

wetland of southwest Florida was reported approximately 98 g C m-2. The studies strongly

emphasized the importance of wetlands for provision of ecosystem services and importance of conservation of wetlands to sustain the benefits provided to human being.

Keywords: Marshland, Wetland, Ecosystem Services, Carbon Sequestration, Hydrology 1.

endirmek ve

tedarik etme

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besin zinciri ve

Mitsch and Gooselink, 2015).

Mitsch and Gooselink, 2015)

Mitsch ve Gooselink, 2015).

Mitsch and Gooselink 2015; Adame and Fry, 2016).

edilmektedir (Cui et

300 bin hektar sulak alan kuruma ve kirlenme gibi nedenler

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sulak alanlar,

1.) 2.) sulak alanlardaki vejetasyonu destekler ve 3.)

sulak alan hidrolojisine sahiptir (Skaggs et al., 1994). Sulak alanlar, besinlerin ve di

3.

Mittsch et al., 2015; Adame and Fry, 2015;

Wallace, 2008) besin

(Kadlec and Wallace, 2008).

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anlarda tutulan karbon -1 -1 -2 -1 EM) ile --1) ve mera (49.77 ton C ha-1 -1 (Tablo 1) (Anonim, 2018).

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Sonraki alan Orman

Mera

Yapay Alanlar

miktarda C depolasa da bir

4 2 2'den 23 olan CH4 al., 2

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4. -85 km2 gen bu onun tam atta ra, bir Kercher, 2005). 2 2'nin bu mevcut sula

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Adame, M. F., & Fry, B. 2016. Source and stability of soil carbon in mangrove and freshwater wetlands of the Mexican Pacific coast. Wetlands ecology and management, 24(2), 129-137.

Adhikari, S., Bajracharaya, R. M., Sitaula, B. K. 2009. A review of carbon dynamics and sequestration in wetlands. Journal of Wetlands Ecology, 42-46.

-Bridgham, S. D., Megonigal, J. P., Keller, J. K., Bliss, N. B., Trettin, C. 2006. The carbon balance of North American wetlands. Wetlands, 26(4), 889-916.

Brown, D. R., Johnston, S. G., Santos, I. R., Holloway, C. J., Sanders, C. J. 2019. Significant organic carbon accumulation in two coastal acid sulfate soil wetlands. Geophysical Research Letters.

Chen, H., Zou, J., Cui, J., Nie, M., Fang, C. 2018. Wetland drying increases the temperature sensitivity of soil respiration. Soil Biology and Biochemistry, 120, 24-27.

Cui, B., Yang, Q., Yang, Z., Zhang, K. 2009. Evaluating the ecological performance of wetland restoration in the Yellow River Delta, China. Ecological Engineering, 35(7), 1090-1103.

Dodds, W. K., Perkin, J. S., Gerken, J. E. 2013. Human impact on freshwater ecosystem services: a global perspective, Environmental science & technology, 47(16), 9061-9068. Hambright, K. D., Zohary, T. 1999. The Hula Valley (northern Israel) wetlands rehabilitation project. In An International Perspective on Wetland Rehabilitation (pp. 173-180). Springer, Dordrecht.

Kadlec, R. H., Wallace, S. 2008. Treatment wetlands. CRC press.

Kerstetter, D. L., Hou, J. S., Lin, C. H. 2004. Profiling Taiwanese ecotourists using a behavioral approach. Tourism management, 25(4), 491-498.

Macreadie, P. I., Ollivier, Q. R., Kelleway, J. J., Serrano, O., Carnell, P. E., Lewis, C. J. E., Atwood, T. B., Sanderman, J., Baldock, J., Connolly, R. M., Duarte, C. M., Lavery, P. S., Steven, A., Lovelock, C.E., 2017. Carbon sequestration by Australian tidal marshes. Scientific Reports, 7, 44071.

Mcleod, E., C

Schlesinger, W: H., Silliman, B. R. 2011. A blueprint for blue carbon: toward an improved understanding of the role of vegetated coastal habitats in sequestering CO2. Frontiers in Ecology and the Environment, 9(10), 552-560.

McKinley, E., Ballinger, R. C., Beaumont, N. J. 2018. Saltmarshes, ecosystem services, and an evolving policy landscape: A case study of Wales, UK. Marine Policy, 91, 1-10. Meng, W., He, M., Hu, B., Mo, X., Li, H., Liu, B. and Wang, Z. 2017. Status of wetlands in

China: A review of extent, degradation, issues and recommendations for improvement. Ocean & Coastal Management, 146, pp.50-59.

Millennium Ecosystem Assessment (MEA), 2005. Millennium Ecosystem Assessment: Ecosystems and Human Well-being 5. Island Press Washington, DC.

Mitra, S., Wassman, R., Vlek P. L. G. 2005. An appraisal of global wetland area and its organic carbon stock. Curr. Sci. 88:25 35

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J., Jorgensen, S. E., Brix, H. 2013. Wetlands, carbon, and climate change. Landscape Ecology, 28(4), 583-597.

Mitsch, W. J., Bernal, B., Hernandez, M. E. 2015. Ecosystem services of wetlands.

Mitsch, W. J., Gosselink, J. G. 2015. Wetlands. 5th ed. Hoboken, NJ: John Wiley & Sons, Inc.

Reddy, K. R., DeLaune, R., Craft, C. B. 2010. Nutrients in wetlands: Implications to water quality under changing climatic conditions. Final Report submitted to U. S. Environmental Protection Agency. EPA Contract No. EP-C-09-001.

Ricaurte, L. F., Olaya- -Valencia, J., Lara, D.,

Arroyave-Finlayson, C. M., Palomo, I. 2017. Future impacts of drivers of change on wetland ecosystem services in Colombia. Global environmental change, 44, 158-169.

Richardson, C. J., Hussain, N. A. 2006. Restoring the Garden of Eden: an ecological assessment of the marshes of Iraq. BioScience, 56(6), 477-489.

Sezen, J. 2017

-177.

Sica, Y. V., Quintana, R. D., Radeloff, V. C., Gavier-Pizarro, G. I. 2016. Wetland loss due to Delta, Argentina. Science of the Total Environment, 568, 967-978.

Skaggs, R. W., Amatya, D., Evans, R. O., Parsons, J. E. 1994. Characterization and evaluation of proposed hydrologic criteria for wetlands. J. Soil Water Cons. 49 (5), 501-510.

Tiner, R. W. 2016. Wetland indicators: A guide to wetland formation, identification, delineation, classification, and mapping. CRC press.

Van de Broek, M., Baert, L., Temmerman, S., Govers, G. 2019. Soil organic carbon stocks in a tidal marsh landscape are dominated by human marsh embankment and subsequent marsh progradation. European Journal of Soil Science, 70(2), 338-349.

Villa, J. A., & Mitsch, W. J. 2015. Carbon sequestration in different wetland plant communities in the Big Cypress Swamp region of southwest Florida. International Journal of Biodiversity Science, Ecosystem Services & Management, 11(1), 17-28. Wong, C. P., Jiang, B., Kinzig, A. P., Lee, K. N., Ouyang, Z. 2015. Linking ecosystem

characteristics to final ecosystem services for public policy. Ecology letters, 18(1), 108-118.

Zedler, J. B., Kercher, S. 2005. Wetland resources: status, trends, ecosystem services, and restorability. Annu. Rev. Environ. Resour., 30, 39-74.

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