Floristic development patterns in a restored Elk River estuarine marsh, Grays Harbor, Washington

被引:44
作者
Thom, RM
Zeigler, R
Borde, AB
机构
[1] Battelle Marine Sci Lab, Sequim, WA 98382 USA
[2] Washington State Dept Fish & Wildlife, Olympia, WA 98501 USA
关键词
dike breach; Grays Harbor estuary; Pacific Northwest wetlands; salt marsh restoration;
D O I
10.1046/j.1526-100X.2002.01038.x
中图分类号
Q14 [生态学(生物生态学)];
学科分类号
071012 ; 0713 ;
摘要
We describe the changes in the floral assemblage in a salt marsh after reconnection to estuarine tidal inundation. The Elk River marsh in Grays Harbor, Washington was opened to tidal flushing in 1987 after being diked for approximately 70 years. The freshwater pasture assemblage dominated by Phalarais arundinacea (reed canary grass) converted to low salt marsh vegetation within 5 years, with the major flux in species occurring between years 1 and 4. The system continued to develop through the 11-year post-breach monitoring period, although change after year 6 was slower than in previous years. The assemblage resembles a low salt marsh community dominated by Distichlis spicata (salt grass) and Salicornia virginica (pickleweed). Because of subsidence of the system during the period of breaching, the restored system remains substantially different from the Deschamsia cespitosa (tufted hairgrass)-dominated reference marsh. Use of a similarity index to compare between years and also between reference and restored marshes in the same year revealed that similarity in floral composition between year 0 and subsequent years decreased with time. However, there was a period of dramatic dissimilarity during years 1 to 3 when the system was rapidly changing from a freshwater to estuarine condition. Similarity values between the reference and restored system generally increased with time. Somewhat surprisingly the reference marsh showed considerable between-year variation in similarity, which indicated substantial year-to-year variability in species composition. Based on accretion rate data from previous studies we predict that full recovery of the system would take between 75 and 150 years.
引用
收藏
页码:487 / 496
页数:10
相关论文
共 30 条
[1]  
[Anonymous], 96R23 IWR US ARM COR
[2]   IMPACT OF A COMBINED SEWER OVERFLOW ON THE ABUNDANCE, DISTRIBUTION AND COMMUNITY STRUCTURE OF SUBTIDAL BENTHOS [J].
ARMSTRONG, JW ;
THOM, RM ;
CHEW, KK .
MARINE ENVIRONMENTAL RESEARCH, 1980, 4 (01) :3-23
[3]   EVIDENCE FOR GREAT HOLOCENE EARTHQUAKES ALONG THE OUTER COAST OF WASHINGTON-STATE [J].
ATWATER, BF .
SCIENCE, 1987, 236 (4804) :942-944
[4]   Modeling habitat change in salt marshes after tidal restoration [J].
Boumans, RMJ ;
Burdick, DM ;
Dionne, M .
RESTORATION ECOLOGY, 2002, 10 (03) :543-555
[5]   AN ORDINATION OF THE UPLAND FOREST COMMUNITIES OF SOUTHERN WISCONSIN [J].
BRAY, JR ;
CURTIS, JT .
ECOLOGICAL MONOGRAPHS, 1957, 27 (04) :326-349
[6]  
Callaway JC, 2001, MAR SCI SER, P89
[7]  
Cooke S.S., 1997, FIELD GUIDE COMMON W
[8]   Physical and functional responses to experimental marsh surface elevation manipulation in Coos Bay's South Slough [J].
Cornu, CE ;
Sadro, S .
RESTORATION ECOLOGY, 2002, 10 (03) :474-486
[9]   Drainage and elevation as factors in the restoration of salt marsh in Britain [J].
Crooks, S ;
Schutten, J ;
Sheern, GD ;
Pye, K ;
Davy, AJ .
RESTORATION ECOLOGY, 2002, 10 (03) :591-602
[10]   Restoration of the Sieperda tidal marsh in the Scheldt estuary, the Netherlands [J].
Eertman, RHM ;
Kornman, BA ;
Stikvoort, E ;
Verbeek, H .
RESTORATION ECOLOGY, 2002, 10 (03) :438-449