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7/14/2009 5:02:33 PM
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5/20/2009 10:50:49 AM
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UCREFRP
UCREFRP Catalog Number
8132
Author
Lieberman, D. and T. Burke.
Title
Limnology and Drift of Particulate Organic Matter Through the Lower Colorado River.
USFW Year
1991.
USFW - Doc Type
Denver, CO.
Copyright Material
NO
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flow from the Parker Division annually. By using <br />carefully regulated specific gravity mediums, Sollins <br />et al. (1985 [541) separated streambed and flood plain <br />detritus into fragmented plant materials and organo- <br />mineral particles and found that the latter comprised <br />the bulk of the material. However, in this study, the <br />authors could not determine if the organic matter <br />had already been adsorbed when the particles <br />entered the stream or if the particles had become <br />coated with organics while in the streambed. <br />At Imperial Dam, the sluicing operation indicated that <br />the stirring actions resulted in increased amounts <br />of fine POM in both the canal water and in the river <br />channel below the dam. This action either ground <br />up the larger particles (indicated by a decrease in <br />>25-µm POM) or loosened organic material from <br />mineral particles. A relationship between stirring of <br />the sediments and increased fine POM levels seems <br />apparent. <br />SUMMARY <br />During phase 2, no single factor investigated caused <br />the increase in total POM at downstream stations. <br />Minckley (1979 [10]) stated the relative importance <br />of backwaters to the river system was dispropor- <br />tionate to backwater surface area as indicated by <br />the greater biomass and diversity of benthos and <br />fishes in these habitats. The lower Colorado River <br />is a fairly productive and unique system with many <br />species (albeit exotic) of fish and wildlife. The <25- <br />µm size-fraction POM comprised the greatest <br />proportion of total POM at all stations. The majority <br />of this material was detritus-an important part of <br />the food web. Investigators have reported that <br />detritus provides energy for bacterial and aquatic <br />fauna (Wetzel and Rich, 1973 [25]); Finenko and <br />Zaika, 1970 [551). Minkley (1982 [12]) reported <br />detritus formed the major proportion of stomach <br />contents of threadfin shad, red shiner, mouth- <br />brooder, sailfin molly, and striped mullet in the lower <br />Colorado River, and was common in carp, channel <br />catfish, and yellow bullhead. From this study, <br />evidence supported Minckley's findings (1979 [10]; <br />1982 [12]) that the lower Colorado River is a detrital <br />based trophic system that supports detritivorous <br />fishes. The food habits of introduced forage fishes <br />of the lower Colorado River do not differ substantially <br />from those of the same species within their native <br />ranges. <br />Conclusions derived from this study: <br />1. Phase 1 indicated an increase in the concen- <br />tration of total POM from Davis Dam downstream <br />to Yuma. The mean quantity of total POM in the <br />lower Colorado River was less than 1.50 g/m3; it <br />is quite comparable to results obtained for other 6 <br />and 7 order streams in the Western United States. <br />The <25-µm size-fraction POM comprised the <br />greatest proportion of total POW <br />2. During phase 1, the mean annual POM concen- <br />tration, g/m3, was: <br />- Davis Dam ................. 0.80 <br />- Parker Dam ................ .89 <br />- Headgate Rock Dam ........ .75 <br />- Palo Verde Diversion Dam ... .99 <br />- Cibola ..................... 1.88 <br />- Imperial Dam .............. 2.15 <br />- Yuma ...................... 3.14 <br />At Imperial Dam and Yuma, total POM concentra- <br />tions were not significantly different from one <br />another, but both were significantly different <br />(p<0.05) from all other upstream stations. <br />3. POM was dominated by: <br />• Detrital material and diatoms in the <25-µm size- <br />fraction <br />• Green algae in the >25-µm size-fraction <br />• Macrophyte fragments in the >505-µm size- <br />fraction <br />4. Possible sources for increased POM downsteam <br />were: <br />• In-stream production by autotrophs <br />• Input of material from backwater marshes <br />• Input from agricultural drains <br />• Input from streambed <br />• Input from stream bank erosion <br />5. Reservoirs retained inorganic matter and <br />released a higher percentage of POM than other <br />main channel stations-particularly during spring <br />and summer. <br />• Data indicate that reservoirs neither contributed <br />nor were a sink for POW Increases in POM observed <br />in Parker Dam tailwater diminished downstream <br />which was possibly due to primary and secondary <br />consumers. <br />• Chlorophyll a concentrations were generally <br />greater in Davis Dam and Parker Dam tailwaters than <br />in their respective downstream stations. <br />• In Davis Dam and Parker Dam tailwaters, 121 <br />and 152 phytoplankton species were collected, <br />respectively. <br />• Zooplankton concentrations were greater in Davis <br />Dam and Parker Dam tailwaters than at all other <br />main channel stations. <br />6. POM data were inconclusive regarding the role <br />of backwaters during normal flows. Only during the <br />27
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