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165:, if present, account for a minority of the total area cover. High water levels are one of the important factors that prevent invasion by woody plants; in other cases, fire is important. In areas with low frequencies of fire, or reduced water level fluctuations, or higher fertility, plant diversity will decline.
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The most important factors in creating and maintaining wet meadows are therefore natural water level fluctuations and recurring fire. In some cases, small areas of wet meadow are artificially created. Due to the concern with damage that excessive stormwater runoff can cause to nearby lakes and
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opportunity for school-age children. In Europe, wet meadows are sometimes managed by hay-cutting and grazing. Intensified agricultural practices (too frequent mowing, use of mineral fertilizers, manure and insecticides), may lead to declines in the abundance of organisms and species diversity.
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Peet, R. K. and Allard, D. J. (1993). Longleaf pine vegetation of the southern
Atlantic and eastern Gulf Coast regions: a preliminary classification. In The Longleaf Pine Ecosystem: Ecology, Restoration and Management, ed. S. M. Hermann, pp. 45–81. Tallahassee, FL: Tall Timbers Research
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Peet, R. K. and Allard, D. J. (1993). Longleaf pine vegetation of the southern
Atlantic and eastern Gulf Coast regions: a preliminary classification. In The Longleaf Pine Ecosystem: Ecology, Restoration and Management, ed. S. M. Hermann, pp. 45–81. Tallahassee, FL: Tall Timbers Research
189:
streams, artificial wetlands can be created to capture stormwater. Often this produce marshes, but in some cases wet meadows may be produced. The idea is to capture and store rainwater onsite and use it as a resource to grow attractive native plants that thrive in such conditions. The
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Mountford, J. O., Lakhani, K. H., and
Kirkham, F. W. 1993. Experimental assessment of the effects of nitrogen addition under hay-cutting and aftermath grazing on the vegetation of meadows on a Somerset peat moor. Journal of Applied Ecology 30:
181:. The also survive along rivers and lakeshores where water levels are allowed to change within and among years. But their area has been dramatically reduced. In some areas, wet meadows are partially drained and farmed and therefore lack the
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Keddy, P. A. and Fraser, L. H. (2002). The management of wetlands for biological diversity: four principles. In Modern Trends in
Applied Aquatic Ecology, eds. R. S. Ambasht and N. K. Ambasht, pp. 21–42. New York:
91:. Wet meadows often have large numbers of wetland plant species, which frequently survive as buried seeds during dry periods, and then regenerate after flooding. Wet meadows therefore do not usually support
83:, a wet meadow does not have standing water present except for brief to moderate periods during the growing season. Instead, the ground in a wet meadow fluctuates between brief periods of
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Wilcox, D.A, Thompson, T.A., Booth, R.K. and
Nicholas, J.R. 2007. Lake-level variability and water availability in the Great Lakes. USGS Circular 1311. 25 p.
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life such as fish. They typically have a high diversity of plant species, and may attract large numbers of birds, small mammals and insects including
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Hammer, D. A. (ed.) (1989). Constructed
Wetlands for Wastewater Treatment: Municipal, Industrial and Agricultural. Chelsea, MI: Lewis Publishers.
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described here. In other cases, the construction of dams has interfered with the natural fluctuation of water levels that generates wet meadows.
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Fraser, L. H. and Keddy, P. A. (eds.) 2005. The World’s
Largest Wetlands: Ecology and Conservation. Cambridge, UK: Cambridge University Press.
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for part or all of the growing season which prevents the growth of trees and brush. Debate exists whether a wet meadow is a type of
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388:"Effect of nature protection and management of grassland on biodiversity – Case from big flooded river valley (NE Poland)"
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Whigham, D.F., D. Dykyjova, and S. Hejny. 1993. Wetlands of the World, Vol. 1, Dordrecht, the
Netherlands: Kluwer.
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Wet meadows were once common in wetland types around the world. They remain an important community type in wet
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Knozowski, Paweł; Nowakowski, Jacek J.; Stawicka, Anna Maria; Górski, Andrzej; Dulisz, Beata (2023-11-10).
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or a completely separate type of wetland. Wet prairies and wet
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289:(2nd ed.). Cambridge: Cambridge University Press.
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103:in a wet meadow usually includes a wide variety of
287:Wetland ecology : principles and conservation
193:is one such project. It is a group of wet meadow
75:and around the shores of large lakes. Unlike a
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1074:Ramsar Classification System for Wetland Type
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67:Wet meadows may occur because of restricted
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457:Illinois Department of Natural Resources
444:Selected species for wet meadow gardens
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1169:Meadowview Biological Research Station
1101:Greenhouse gas emissions from wetlands
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1164:Irish Peatland Conservation Council
153:), and carnivorous plants such as
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439:How to create a wet meadow garden
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392:Science of the Total Environment
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660:Flooded grasslands and savannas
405:10.1016/j.scitotenv.2023.165280
242:Flooded grasslands and savannas
191:Buhr Park Children's Wet Meadow
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1184:Wildfowl & Wetlands Trust
1174:Society of Wetland Scientists
59:are hydrologically similar.
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35:, California, United States.
1069:National Wetlands Inventory
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1154:Delta Waterfowl Foundation
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1133:Wetland indicator status
33:San Bernardino Mountains
844:Freshwater swamp forest
285:Keddy, Paul A. (2010).
137:, many species of wild
1179:Wetlands International
950:List of wetland plants
454:CDHabitatWetPrairieFen
87:and longer periods of
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824:Salt pannes and pools
449:Children's Wet Meadow
63:Hydrology and ecology
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47:with soils that are
31:A wet meadow in the
1284:Wetlands portal
915:Constructed wetland
500:Types and landforms
199:Ann Arbor, Michigan
1128:Salt marsh die-off
1046:Salt marsh dieback
955:List of fen plants
794:Palustrine wetland
695:Intertidal wetland
690:Interdunal wetland
107:species including
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1330:Fluvial landforms
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1204:Aquatic ecosystem
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1111:Ramsar Convention
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920:Converted wetland
862:Peat swamp forest
725:Inland salt marsh
16:(Redirected from
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1264:Will-o'-the-wisp
1197:Related articles
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889:Whitewater river
839:Coniferous swamp
720:Freshwater marsh
613:Clearwater river
529:Blackwater river
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43:is a type of
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18:Marsh meadows
1229:List of bogs
1084:Conservation
1015:Ombrotrophic
959:
930:Water-meadow
873:
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665:Grass valley
655:Flood-meadow
618:Cypress dome
549:Cataract bog
524:Beach meadow
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252:Water-meadow
247:Flood-meadow
187:
183:biodiversity
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169:Conservation
163:Woody plants
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66:
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1254:Telmatology
1249:River delta
1116:Ramsar site
1106:Marsh organ
1005:Hydric soil
884:Vernal pool
867:Shrub swamp
735:Tidal marsh
564:Plateau bog
554:Coastal bog
544:Blanket bog
203:educational
97:butterflies
1325:Grasslands
1309:Categories
1214:Bog butter
910:Bog garden
903:Artificial
874:Wet meadow
740:High marsh
730:Salt marsh
633:Fen-meadow
601:Alder carr
584:Upland bog
579:String bog
574:Raised bog
398:: 165280.
263:References
195:ecosystems
155:Sarracenia
150:Spiranthes
105:herbaceous
101:Vegetation
89:saturation
85:inundation
41:wet meadow
1036:Hydrosere
1024:Processes
1010:Marsh gas
855:Myristica
745:Low marsh
559:Kermi bog
534:Bofedales
514:Backswamp
414:0048-9697
179:flatwoods
144:Calopogon
128:Parnassia
49:saturated
1315:Wetlands
1294:Category
1224:Bog-wood
1219:Bog iron
1209:Bog body
1031:Halosere
983:Histosol
978:Acrotelm
961:Sphagnum
819:Reed bed
764:Moorland
643:Rich fen
638:Poor fen
493:Wetlands
422:37419354
376:321–332.
347:Station.
319:Station.
210:See also
175:savannas
69:drainage
57:savannas
1320:Meadows
1259:Turbary
1239:Estuary
814:Pothole
804:Pocosin
769:Mudflat
608:Ciénega
591:Callows
507:Natural
357:Kluwer.
159:Drosera
139:orchids
134:Lobelia
117:grasses
93:aquatic
45:wetland
829:Slough
784:Pakihi
774:Muskeg
700:Kettle
670:Guelta
420:
412:
293:
141:(e.g.
122:Rhexia
113:rushes
109:sedges
925:Swale
894:Yaéré
857:swamp
834:Swamp
789:Palsa
779:Oasis
759:Misse
710:Marsh
680:Igapó
675:Hamun
650:Flark
623:Dambo
519:Bayou
81:swamp
77:marsh
53:marsh
1121:List
988:Peat
943:Life
809:Pond
754:Mere
705:Lagg
685:Ings
596:Carr
418:PMID
410:ISSN
291:ISBN
177:and
157:and
147:and
628:Fen
539:Bog
400:doi
396:898
257:Bog
197:in
79:or
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271:^
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99:.
39:A
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