Evaluating a Large-Scale Eelgrass Restoration Project in the Chesapeake Bay

被引:22
作者
Tanner, Christopher [1 ]
Hunter, Sarah [1 ]
Reel, Justin [2 ]
Parham, Thomas [3 ]
Naylor, Mike [3 ]
Karrh, Lee [3 ]
Busch, Kathryn [3 ]
Golden, Rebecca R. [3 ]
Lewandowski, Mark [3 ]
Rybicki, Nancy [4 ]
Schenk, Edward [4 ]
机构
[1] St Marys Coll Maryland, St Marys City, MD 20686 USA
[2] RKK Engineers, Baltimore, MD 21217 USA
[3] Maryland Dept Nat Resources, Annapolis, MD 21401 USA
[4] US Geol Survey, Natl Ctr 430, Reston, VA 20192 USA
关键词
eelgrass; epiphytes; restoration; SAV habitat requirements; site selection; water quality; Zostera marina; ZOSTERA-MARINA L; SUBMERSED AQUATIC VEGETATION; WATER-QUALITY; PHOTOSYNTHETIC RESPONSES; AMMONIUM UPTAKE; CLIMATE-CHANGE; WAVE EXPOSURE; GROWTH; MACROPHYTES; LIGHT;
D O I
10.1111/j.1526-100X.2010.00694.x
中图分类号
Q14 [生态学(生物生态学)];
学科分类号
071012 ; 0713 ;
摘要
Approximately 90,000 shoots of eelgrass (Zostera marina) were planted over 3 years (2003-2005) at Piney Point (PP) in the lower Potomac River estuary in the Chesapeake Bay (mid-Atlantic coast of North America) following 3 years of habitat evaluation using a Preliminary Transplant Suitability Index (PTSI) and test plantings. Initial survival was high for the 2003 and 2004 plantings; however, most of the eelgrass died during the summer following the fall planting. Habitat quality and restoration success were monitored for the 2005 plantings and compared to a nearby restoration site (St. George Island [SGI]). Eelgrass planted at PP in the fall of 2005 declined through the summer of 2006 with some recovery in the spring of 2007, but was gone by the end of the summer of 2007. The summer decline from late July to mid-August of 2006 coincided with water temperatures greater than 30 degrees C, hypoxic oxygen (0-3 mg/L) concentrations, and low percent light at leaf level (PLL < 15%). Epiphyte loads were much heavier at PP than at SGI, despite similar water quality. We suggest that this was the result of higher wave exposure at PP. All of these factors are likely to have contributed to the mortality of the 2005 plantings. Submerged aquatic vegetation habitat quality based on the PTSI, median PLL during the growing season, and test plantings did not explain the decline of the plantings. Restoration site selection criteria should be expanded to include the effects of wave exposure on self-shading and epiphyte loads, and the potential for both short-term exposures to stressful conditions and long-term changes in habitat quality.
引用
收藏
页码:538 / 548
页数:11
相关论文
共 62 条
[1]  
Batuik R.P.W Bergstrom., 2000, CHESAPEAKE BAY SUBME
[2]  
Calumpong HP, 2001, GLOBAL SEAGRASS RESEARCH METHODS, P425, DOI 10.1016/B978-044450891-1/50023-2
[3]  
Campbell ML, 2002, B MAR SCI, V71, P1405
[4]   ROLE OF WEATHER AND WATER-QUALITY IN POPULATION-DYNAMICS OF SUBMERSED MACROPHYTES IN THE TIDAL POTOMAC RIVER [J].
CARTER, V ;
RYBICKI, NB ;
LANDWEHR, JM ;
TURTORA, M .
ESTUARIES, 1994, 17 (02) :417-426
[5]  
Carter V, 1985, 2234A US GEOL SURV
[6]  
*CHES BAY PROGR, 1999, WAT QUAL DAT BAS
[7]   Ammonium uptake by seagrass epiphytes: Isolation of the effects of water velocity using an isotope label [J].
Cornelisen, CD ;
Thomas, FIM .
LIMNOLOGY AND OCEANOGRAPHY, 2002, 47 (04) :1223-1229
[8]   Restoring eelgrass, Zostera marina L., habitat using a new transplanting technique: The horizontal rhizome method [J].
Davis, RC ;
Short, FT .
AQUATIC BOTANY, 1997, 59 (1-2) :1-15
[9]   ASSESSING WATER-QUALITY WITH SUBMERSED AQUATIC VEGETATION [J].
DENNISON, WC ;
ORTH, RJ ;
MOORE, KA ;
STEVENSON, JC ;
CARTER, V ;
KOLLAR, S ;
BERGSTROM, PW ;
BATIUK, RA .
BIOSCIENCE, 1993, 43 (02) :86-94
[10]   Biodiversity and the functioning of seagrass ecosystems [J].
Duffy, J. Emmett .
MARINE ECOLOGY PROGRESS SERIES, 2006, 311 :233-250