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Effects of fish density, identity, a...

Hargrave, Chad Wesley.

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Effects of fish density, identity, and species richness on stream ecosystems.

Record Type:	Electronic resources : Monograph/item
Title/Author:	Effects of fish density, identity, and species richness on stream ecosystems./
Author:	Hargrave, Chad Wesley.
Description:	141 p.
Notes:	Source: Dissertation Abstracts International, Volume: 66-02, Section: B, page: 0674.
Contained By:	Dissertation Abstracts International66-02B.
Subject:	Biology, Ecology. -
Online resource:	http://pqdd.sinica.edu.tw/twdaoapp/servlet/advanced?query=3163015
ISBN:	0496968688

Effects of fish density, identity, and species richness on stream ecosystems.
Hargrave, Chad Wesley.

Effects of fish density, identity, and species richness on stream ecosystems. - 141 p.

Source: Dissertation Abstracts International, Volume: 66-02, Section: B, page: 0674.

Thesis (Ph.D.)--The University of Oklahoma, 2005.

Stream ecosystem properties and functions are important because they provide services such as water purification, oxygen production, and carbon fixation that help sustain life. Aquatic organisms can affect these properties and functions through different pathways linked to a species trophic and functional characteristics. It is necessary to understand how these ecosystem effects vary among taxa because as aquatic biota change as a result of random, natural, or anthropogenic influences, ecosystems properties and functions are likely to be affected.

ISBN: 0496968688Subjects--Topical Terms:

1017726
Biology, Ecology.

Effects of fish density, identity, and species richness on stream ecosystems.
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100 1 $a Hargrave, Chad Wesley. $3 1937778
245 1 0 $a Effects of fish density, identity, and species richness on stream ecosystems.
300 $a 141 p.
500 $a Source: Dissertation Abstracts International, Volume: 66-02, Section: B, page: 0674.
500 $a Adviser: William J. Matthews.
502 $a Thesis (Ph.D.)--The University of Oklahoma, 2005.
520 $a Stream ecosystem properties and functions are important because they provide services such as water purification, oxygen production, and carbon fixation that help sustain life. Aquatic organisms can affect these properties and functions through different pathways linked to a species trophic and functional characteristics. It is necessary to understand how these ecosystem effects vary among taxa because as aquatic biota change as a result of random, natural, or anthropogenic influences, ecosystems properties and functions are likely to be affected.
520 $a Fishes are important consumers in stream ecosystems, having important regulatory roles for many ecosystem properties and functions. In this dissertation, I addressed the effects of fishes on stream ecosystems from three perspectives. I asked (1) if fish ecosystem effects were dependent on local fish density, (2) if fish effects were caused by different species-specific food web pathways, and (3) if co-occurring fish species had facilitative effects on ecosystems when in more specious assemblages.
520 $a This research suggests that the population size, the identity of species in the assemblage, as well as the number of species making up the assemblage can be important factors affecting stream ecosystem properties and functions. Chapters 1--3 were conducted in artificial stream mesocosms, and may have limited applicability to natural stream ecosystems where a variety of abiotic factors can influence ecosystems. In Chapter 4, I tested the ecosystem effects of three fish species from different functional groups on PPR, benthic algae biomass (as chlorophyll-a), and benthic invertebrate density in a natural stream ecosystem using field enclosures. Treatments were Blackstripe Topminnow (Fundulus notatus), a surface insectivore; Longear Sunfish (Lepomis megalotis), a watercolumn insectivore; Orangethroat Darter (Etheostoma spectabile), a benthic invertivore; and a fishless control. Primary productivity was greater in all enclosures with fish than in enclosures without fish. Relative to control enclosures, benthic algae biomass was not different in Blackstripe Topminnow treatments, but was greater in Longear Sunfish treatments on both sample days, and was greater in Orangethroat Darter treatments on day 15. Benthic invertebrate abundance was not affected by any of the fish treatments. These data agree with results from previous mesocosm experiments. Thus, despite the limited realism of stream mesocosms, patterns observed in mesocosm experiments are likely to occur in natural stream ecosystems. (Abstract shortened by UMI.)
590 $a School code: 0169.
650 4 $a Biology, Ecology. $3 1017726
650 4 $a Agriculture, Fisheries and Aquaculture. $3 1020913
690 $a 0329
690 $a 0792
710 2 0 $a The University of Oklahoma. $3 1021915
773 0 $t Dissertation Abstracts International $g 66-02B.
790 1 0 $a Matthews, William J., $e advisor
790 $a 0169
791 $a Ph.D.
792 $a 2005
856 4 0 $u http://pqdd.sinica.edu.tw/twdaoapp/servlet/advanced?query=3163015