Response of aquatic vegetation communities and other wetland cover types to floodplain restoration at Emiquon Preserve

Hydrobiologia ◽  
2016 ◽  
Vol 804 (1) ◽  
pp. 59-71 ◽  
Author(s):  
Christopher S. Hine ◽  
Heath M. Hagy ◽  
Michelle M. Horath ◽  
Aaron P. Yetter ◽  
Randolph V. Smith ◽  
...  
1985 ◽  
Vol 36 (3) ◽  
pp. 311 ◽  
Author(s):  
AR Fletcher ◽  
AK Morison ◽  
DJ Hume

Densities of carp, ranges of turbidity, and details of communities of aquatic vegetation from 1979 to 1982 are given for several waterbodies in the Goulburn River valley including the Broken River, near Shepparton, Victoria. The turbidity values at all sites were high, typical of Australian inland waterbodies. There was no association between high carp densities and high turbidity, and populations of carp did not appear to increase turbidity. Observed turbidity increases at each site appeared to be related to hydrological changes. Fluctuation of water levels was also an important factor determining the extent of aquatic vegetation communities. However, circumstantial evidence is presented that shallow-rooted and soft-leaved aquatic vegetation such as Potamogeton spp. have been reduced by carp.


2021 ◽  
Vol 33 (2) ◽  
pp. 507-517
Author(s):  
Yang Jingzhicheng ◽  
◽  
Luo Juhua ◽  
Lu Lirong ◽  
Sun Zhe ◽  
...  

Estuaries ◽  
2000 ◽  
Vol 23 (1) ◽  
pp. 115 ◽  
Author(s):  
Kenneth A. Moore ◽  
David J. Wilcox ◽  
Robert J. Orth

2019 ◽  
Vol 10 (1) ◽  
pp. 277-294
Author(s):  
Brian A. Tangen ◽  
Raymond G. Finocchiaro ◽  
Wesley E. Newton ◽  
Charles F. Dahl

Abstract Observed degradation of aquatic systems at Big Stone National Wildlife Refuge, located in west-central Minnesota, have been associated with sediment-laden inflows from riverine systems. To support management, a study was conducted during 2013–2014 with overall goals of characterizing the aquatic invertebrate and vegetation communities of the Big Stone National Wildlife Refuge and exploring relations between these communities and various water-quality parameters. Sample sites were located along an observed vegetation gradient and assigned to three predetermined habitat zones for comparison purposes: upstream, transition, and downstream. Of the 12 species of aquatic vegetation that were identified, invasive narrowleaf cattail Typha angustifolia dominated the upstream zone (observed at >90% of sample locations), coontail Ceratophyllum demersum and narrowleaf cattail were most common in the transition zone (collected or observed at 100 and 83% of sample locations, respectively), and coontail and narrowleaf pondweed Potamogeton strictifolius were most common in the downstream zone (collected at 100 and 64% of sample locations, respectively). Measured values for the water-quality parameters varied among dates, reflecting the continually fluctuating nature of riverine systems. Based on general observations across sample dates, turbidity and dissolved oxygen concentrations were greatest in the upstream zone sample sites, while oxidation-reduction potential was greatest in the downstream zone sites. There were 115 unique aquatic invertebrate taxa identified to varying levels of taxonomic resolution. Results suggested that there were overall differences in invertebrate biomass among the sample dates, but that there were no strong trends among the sample zones. Aquatic invertebrates and vegetation communities, along with the water-quality parameters, varied temporally and showed irregular relations among the sample zones. These general observations emphasize the importance of temporally and spatially intensive sampling to account for natural variation. Moreover, short- and long-term streamflow and water-level information obtained for this study demonstrated substantial variability that must be considered when conducting biotic inventories and monitoring water quality, as well as when using such data to assess management options. Periodic monitoring of wetlands and associated streamflows, along with sediment loads and water quality of inflows, should allow Big Stone National Wildlife Refuge staff to identify habitat degradation and potential contributing factors, and to develop strategies to achieve specific management objectives and goals.


2009 ◽  
Vol 27 (2) ◽  
pp. 136-139 ◽  
Author(s):  
E. G. Booth ◽  
S. P. Loheide ◽  
R. D. Hansis

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