Fish Habitat: Essential Fish Habitat and Rehabilitation

<em>Abstract</em> .—Defining and quantifying essential fish habitat is difficult, perhaps particularly so in estuaries, which are typically dynamic. Yet we need habitat data to make informed decisions about the management of estuarine habitats and associated fish populations. Our ongoing efforts to resolve issues of fish habitat quality have been centered in the relatively unaltered Jacques Cousteau National Estuarine Research Reserve (the Reserve) in the Mullica River–Great Bay estuary in southern New Jersey, where extensive studies of fishes and their habitats have been conducted during the last decade. Much of our effort to define essential fish habitat has focused on a variety of shallow-water habitats (eelgrass, macroalgae, marsh creeks, unvegetated substrates of different grain sizes) where it is easier to sample in a quantitative manner (e.g., using throw traps and beam trawls) and conduct experimental manipulations (e.g., caging, deploying of artificial habitats). Although our studies in the Reserve have been extensive, they still have been focused on a relatively small component (less than 3%) of the fish fauna of the Reserve, including several species of economic importance. These species include winter flounder <em>Pseudopleuronectes americanus</em> , summer flounder <em>Paralichthys dentatus</em> , tautog <em>Tautoga onitis</em> , and black sea bass <em>Centropristis striata</em> . This work has examined the period from larval ingress and settlement through the first year using a variety of complementary approaches. To date, these studies have included measures of habitat-specific distribution, abundance, residence time, and growth. Attempts to identify both habitat-specific measures of mortality and sources of mortality have proven especially difficult for the migratory fishes typical of Middle Atlantic Bight estuaries. In fact, this mobility, which occurs at seasonal, diel, tidal, and episodic (storms, upwelling, etc.) scales, makes it difficult to assess residence times and confounds attempts to measure habitat quality. The measures of habitat quality that we have used suggest that there are species-specific and habitat-specific responses; however, data sets for multiple years are seldom available to confirm these responses. Efforts to quantify essential fish habitat will be limited in their effectiveness until interannual variability can be assessed.

2007 ◽  
Vol 64 (4) ◽  
pp. 681-691 ◽  
Author(s):  
Steven P Searcy ◽  
David B Eggleston ◽  
Jonathan A Hare

A common assumption throughout the marine ecological and fisheries literature is that growth is a valid indicator of habitat quality and can be used as a criterion for designation of essential fish habitat (EFH). In this study, the validity of growth as an index of habitat quality was tested by examining how variability in otolith growth was related to abiotic and biotic environmental conditions and could be biased by previous growth history, density dependence, and selective mortality. The study was conducted with juvenile Atlantic croaker (Micropogonias undulatus) collected in two North Carolina, USA, estuaries during two seasons of two recruitment years. Water temperature, a component of habitat quality, explained nearly 40% of the variability in juvenile otolith growth. There was also evidence that estimates of growth could be biased by density dependence (slower growth at higher conspecific abundance) and by selective mortality (higher mortality of individuals with relatively slower larval and juvenile otolith growth). Studies using growth-based assessment of habitat quality that fail to identify factors underlying growth rate differences among habitats may reach incorrect decisions regarding quality of different habitats and assignment of EFH.


<em>Abstract.—</em> Freshwater and marine essential fish habitat (EFH) for chinook <em>Oncorhynchus tshawytscha</em> , coho <em>O. kisutch</em> , pink <em>O. gorbuscha</em> , and sockeye <em>O. nerka </em> salmon within Washington, Oregon, California, and Idaho was described and identified using the available literature and databases on salmon distribution and life history. The diversity of freshwater habitats utilized by individual species of salmon coupled with the limitations of existing distribution maps precluded identification of specific stream reaches, wetlands, and other water bodies as EFH for Pacific salmon. A more holistic watershed approach consistent with the ecosystem method recommended by the revised Magnuson-Stevens Fishery Conservation and Management Act was necessary. Therefore, Pacific salmon freshwater EFH was delineated and described as all existing water bodies currently and historically utilized by Pacific salmon within selected watersheds defined by U.S. Geological Survey hydrologic units. Areas above some long-standing artificial barriers to juvenile and adult salmon migration were excluded from designation as Pacific salmon EFH. Delineation of marine EFH was also problematic because of the paucity of scientific studies on offshore Pacific salmon habitat use and distribution. However, available scientific data augmented by information from commercial fisheries indicate that juvenile salmon are found in high concentrations in the nearshore areas of the continental shelf off the Washington, Oregon, and California coasts from late spring through fall. Therefore, Pacific salmon marine EFH was identified as all waters within 60 km of the Washington, Oregon, and California coasts north of Point Conception, California. This initial effort to identify Pacific salmon EFH emphasized the need for accurate, fine-scale geographic information systems data on freshwater and marine salmon distribution and habitat quality and the need for compilation of uniform data sets. Future efforts should focus on developing accurate seasonal salmon distribution data at a 1:24,000 scale to aid in more precise and accurate delineation of Pacific salmon EFH. Furthermore, detailed information on winter distribution of Pacific salmon would be useful in delineating marine EFH.


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