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Recovery of trophic function in a restored Pacific coastal wetland (with C. Currin) California Sea Grant (3/01-2/03)

ABSTRACT:

Response of benthic communities to changing flushing regimes in a Southern California lagoon
The Southern California coast is dotted with coastal lagoons and embayments. Typically, geographically small with episodic freshwater input linked to rain events, these lagoons also receive significant inputs of energy, nutrients and organisms from the sea. Occasionally, lagoons close for extended periods or during specific reproductive seasons, possibly causing key species with life cycles dependent on ocean flushing and transport to disappear. Because plant cover is a main source of spatial heterogeneity in Pacific coast wetlands, changes in plant community can influence the abundance and diversity of benthic invertebrates. The objective of this research was to determine responses of the seagrass, Ruppia maritima L. and associated benthic communities to changing ocean flushing conditions in San Dieguito Lagoon.
San Dieguito Lagoon contains approximately 260 acres of wetland habitat that forms the lower part of the San Dieguito River valley. This lagoon opens and closes regularly based on rainfall amounts and flood scour. In October of 2002, San Dieguito River inlet was breached after an extended 8-month closure. The lower salinity, higher temperature water that resulted post-breach coincided with changes in abiotic sediment properties, with changes in plant distribution, and with changes in the benthic invertebrate community. Pre-breach, tidal flats were dominated by R. maritima but were largely unvegetated after opening the inlet. With the significant decrease in R. maritima cover, porewater salinity increased, porewater temperature decreased, and sediment redox values became more positive. Multivariate analysis indicates differences between pre- and post-breach seagrass fauna composition, partially due to increases in opportunistic species, such as Capitella capitata complex. After breaching the inlet, the seagrass infauna communities also exhibited an increase in diversity and evenness. Understanding the benthic community alterations due to changes in plant cover and in flushing regime will increase knowledge of complex wetland interactions and aid conservation of Southern California lagoon ecosystems.

OBJECTIVES: The project is designed to (1) develop methods (protocols and criteria) for evaluation of trophic function in salt marshes, (2) assess rates and trajectories of recovery of trophic structure and function in created wetlands of southern California and (3) identify key factors controlling trophic function in coastal wetlands. Hypotheses will be tested that examine the relative importance (interaction strength) of different primary producers as food chain support in coastal wetlands (with emphasis on benthic microalgae and Spartina), the role of landscape-level and local-scale factors in determining this importance, and the extent to which created marshes attain the architecture and trophic complexity of natural systems. A related goal is determining whether primary producer availability influences infaunal recovery within created or restored wetlands. The overall scientific objectives are improved understanding of which primary producers fuel secondary and higher order production in California salt marshes (so they can be targeted in restoration design), identification of factors that promote development of food webs characteristic of natural marshes, and development of techniques to evaluate trophic structure and function.

METHODOLOGY: Research will involve a series of mensurative experiments (using natural heterogeneity) and manipulative experiments conducted within the restored and natural salt marshes of Mission Bay California. Trophic function, defined through evaluation of food web architecture, interaction strengths, and complexity, will be determined using (i) using identification of invertebrate and fish gut contents (light microscopy, SEM and HPLC analysis of gut pigments), (ii) stable isotopic analyses (d13C, 15N and 34S) of primary organic matter sources and consumers, (iii) infaunal food preference and assimilation experiments conducted in the laboratory and (iv) in situ tracking of trophic pathways via isotopically labeled benthic food sources. Manipulation of light (shading experiments), plant cover (clipping), and sediment parameters (transplants and organic amendments) will be carried out to identify factors controlling benthic microalgal availability and composition, and the role of benthic microalgae in promoting faunal colonization and typical trophic linkages within created marshes. Near the end of the study, food web architecture in other southern California created marshes (Tijuana River Estuary [2 yr old] and San Diego Bay [18 y old] will be compared with that in Mission Bay

RATIONALE: Loss of coastal salt marsh habitat is a widespread problem in southern California that continues in the face of conservation efforts. Marsh restoration and creation have become standard mitigation measures to compensate for marsh loss in California and elsewhere, despite some uncertainty about their effectiveness. There is broad recognition that effective marsh restoration must achieve recovery of function in addition to structural attributes, but functional measures have been especially elusive. A major function of California salt marshes is trophic support for shellfish, fish and birds.Trophic functions (food web architecture, interaction strengths, complexity), which have received little attention in restored wetlands, will be the focus of this proposal.

ACCOMPLISHMENTS: We will identify primary producers key to salt marsh trophic support functions and identify marsh design criteria that promote development of trophic pathways characteristic of natural marshes. A protocol will be developed for target species which describes sampling, analysis and interpretation of marsh trophic function and for comparison to reference sites. This protocol will be suitable for use by those monitoring restoration projects or change (e.g., degradation) in natural systems. In addition, recommendations will be generated for wetlands design and construction, to promote rapid development of trophic function in created marshes. These will take the form of publications and manuals, available for use by businesses and agencies responsible for the design, construction, monitoring and oversight of wetlands restoration programs.
 

Muddy region of the Crown Point Mitigation Site, Mission Bay, CA; Marsh age: 6 yrs


Sandy region of the Crown Point Mitigation Site, Mission Bay CA; Marsh age: 6 years



Levin, L. A., IOD, Scripps Inst. Ocean., La Jolla, CA, USA, llevin@ucsd.edu
Currin, C., Nat. Ocean Service, NOAA, Beaufort, NC, Carolyn.Currin@noaa.gov
Neira, C. IOD, Scripps Inst. Ocean., La Jolla, CA, USA, cneira@coast.ucsd.edu
McMillan, P., IOD, Scripps Inst. Ocean., La Jolla, CA, USA, pmcmillan@ucsd.edu
Mendoza, G., IOD, Scripps Inst. Ocean., La Jolla, CA, USA, guillmendoza@hotmail.com
Whitcraft, C., IOD, Scripps Inst. Ocean., La Jolla, CA, USA, cwhitcra@ucsd.edu
Gonzalez, J., IOD, Scripps Inst. Ocean., La Jolla, CA, USA, jpgonzal@ucsd.edu
Carman, K., Dept. of Biol. Sci, LSU, Baton Rouge, LA, USA, zocarm@lsu.edu

IMPROVED UNDERSTANDING OF LARGE-SCALE TROPHIC SUCCESSION THROUGH SMALL-SCALE ISOTOPIC ENRICHMENT EXPERIMENTS

Of the many factors regulating succession in benthic marine communities, food has commanded relatively little attention. In California tidal wetlands, disturbance, restoration and plant invasions induce shifts from microalgal-dominated to plant-covered sediments. By enriching algae or bacteria with C-13 and Spartina or cyanobacteria with N-15, we are able to identify those infaunal taxa that preferentially feed on each food source, or C and N derived from these. Experimental results combined with time-series community data reveal that large-scale shifts in community structure in restored salt marshes (from insect to annelid-dominated assemblages) and Spartina-invaded tidal wetlands (from surface to subsurface feeders) are likely to be caused by changes in food availability.

2003 Am. Society of Limnology and Oceanography Meeting

 

Related Downloads:
 

Download Talley and Levin2001
Download Levin and Talley 2002

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