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Last modified
7/14/2009 5:02:35 PM
Creation date
5/20/2009 10:55:18 AM
Metadata
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Template:
UCREFRP
UCREFRP Catalog Number
9371
Author
Levee Removal Evaluation Group.
Title
Green River levee Removal and Floodplain Connectivity Evaluation.
USFW Year
1998.
USFW - Doc Type
CAP-6 LR,
Copyright Material
NO
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<br />1 <br /> <br /> <br /> <br /> <br />I <br /> <br /> <br />1 <br />1 <br />1 <br />1 <br />1 <br />1 <br /> <br />1 <br /> <br />1 <br />APPROACH <br />The purpose of this study is to determine whether the removal of floodplain levees will <br />benefit endangered fishes in the middle Green River. A design to test whether nutrients, <br />vegetation, invertebrate biomass, and/or fish respond to levee removal and floodplain inundation <br />was developed for selected sites and reaches in the Green River. The study design was stratified <br />to test for differences in nutrients, vegetation, invertebrate biomass, and fish abundance in natural <br />floodplains versus breached areas among sites that hold water following recession of flood <br />waters and those that do not, within areas that were determined to have high and low nonnative <br />fish densities (according to unpublished data by Todd Crowl, Utah State University). Study sites <br />were assigned using the following hierarchical categories. <br />1) Low nonnative fish densities versus high nonnative fish reaches <br />2) Sites that hold water following flood flow recession (depressions) versus sites that do <br />not (terraces) <br />3) Natural versus breached (application) sites <br />During the first year of the levee removal study, six sites were evaluated including three <br />terrace and three depression sites (Table 1.1). In 1997, two sites were added (two depressions <br />were added, one in the low nonnative density reach and one in the high nonnative density reach), <br />and in 1998 one depression (low nonnative density) and one terrace (low nonnative density) were <br />added. As will be discussed in later chapters, sites did not always function as terraces or <br />depressions. <br />The analytical approach described in the initial scope of work involved sampling within <br />individual floodplain sites and riverine environments adjacent to the floodplain both during <br />inundation and after river flows receded to baseflow conditions. Although sampling within the <br />floodplains was effective in determining the response of inundation inside study floodplains <br />(hypotheses 1-3), riverine collections did not represent a response to the adjacent floodplain <br />(hypothesis 4). Following the first year of the study it was evident that fish abundance and <br />distribution in the river adjacent to study floodplains were influenced more by the surrounding <br />environment than the relatively small floodplain connected at the site. Irving and Burdick (1995) <br />identified approximately 5,050 acres of middle Green River floodplain inundated in May 1993, <br />whereas between 100 and 200 floodplain acres were added in 1997 (depending on flows) and <br />between 950 and 1,600 acres were added in 1998. In an effort to adjust our sampling design <br />accordingly, the design of the riverine collections in 1997 and 1998 was modified to randomly <br />sample a given distance of river within six longitudinal reaches in the river. In this manner, the <br />riverine samples represented a longitudinal gradient of the river rather than an immediate <br />response to the adjacent floodplain study site. Thus, analysis of fish abundance and distribution <br />in the river reflects responses to the river reaches in general and not solely to the influence of tl <br />study floodplains. B <br />Following the analysis of fish abundance and distribution data, it will be critical to <br />determine the criteria in which floodplain enhancement is considered beneficial or deient <br />a? <br />4
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