RMBL Non-Spatial Metadata Owner and Metadata Title:   Lauren Curtis  <div> <meta content="text/html; charset=utf-8" http-equiv="Content-Type"> <meta content="Word.Document" name="ProgId"> <meta content="Microsoft Word 11" name="Generator"> <meta content="Microsoft Word 11" name="Originator"> <link href="file:///C:%5CUsers%5CLauren%5CAppData%5CLocal%5CTemp%5Cmsohtml1%5C24%5Cclip_filelist.xml" rel="File-List"> <style><!-- /* Style Definitions */ p.MsoNormal, li.MsoNormal, div.MsoNormal {mso-style-parent:""; margin:0in; margin-bottom:.0001pt; mso-pagination:widow-orphan; font-size:12.0pt; font-family:"Times New Roman"; mso-fareast-font-family:"Times New Roman";} @page Section1 {size:8.5in 11.0in; margin:1.0in 1.25in 1.0in 1.25in; mso-header-margin:.5in; mso-footer-margin:.5in; mso-paper-source:0;} div.Section1 {page:Section1;} --></style> <p style="margin-right: -0.25in;" class="MsoNormal">Didymo Removal 2009</p>  </div>



RMBL non-spatial metadata record ID #466
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Project Contact Information
Head PI /OwnerLauren Curtis Affiliation: Student
Project Title: 

Didymo Removal 2009

 
Data Collector:  Lauren Curtis Email: lcurtis1@ksc.mailcruiser.com
Metadata Collector:  Lauren Curtis Email: lcurtis1@ksc.mailcruiser.com

Project Classification Information
Level: population Theme:  Research Subject: other
Project:  Experimental Location:  Gothic Townsite
Organism 1:  Didymosphenia geminata Organism 2:  Didymosphenia geminata

Project Information
Project keywords: Didymoshenia geminata
Project purpose:  The purpose of the Didymosphenia geminata removal experiment is to determine if the presence of the algae has an effect on the abundance and composition of invertebrates in the East River along the Gothic townsite. The overall goal is to determine what kind of influence and invasion of D. geminata has on the aquatic community.
Project methodology:  
We removed the algae, Didymosphenia geminata, from the stream bottom of 8 plots in the East River, in order to manipulate the environment and determine if the presence of D. geminata has an effect on the abundance and composition of the invertebrate environment. The plots were placed at two sites in the East River. Plots one through four resided 30 meters above Vera falls, and plots five through eight were placed several hundred meters downstream. In order to prevent bias, the plots were chosen when in mid June when the river’s water level was high, (roughly 40 centimeters) and the stream bottom was difficult to see. The plots at each site were placed two meters away from each other, beginning downstream and moving upstream. Each plot measured 0.5 m x 0.5 m and had an adjacent control where no D. geminata was removed during the experiment. The control plots were placed 1 meter away from the corresponding experimental plot where the velocity and depth of the water were similar between the two plots. The upper corners of each plot were marked two steel bars placed 0.5 meters away from each other. During removals the plots were defined using a 0.5 m x 0.5 m grid which was placed over the steel bars and submerged to outline removal area. We used glass viewing box to identify where in the quadrat D. geminata was present and metal forceps to eradicate the algae from the substrates of the removal plots. To control for disturbance, we placed the quadrat over the adjacent control (non D. geminata removal) plot and touched each of the rocks within the designated area with the same forceps without removing any D. geminata. We visited the sites regularly (every 2 to 4 days) to remove any D. geminata growth in the experimental plots. The removals took place from July 3rd to July 27th, just over three weeks.  We used a volume index to determine the amount of D. geminata growth in each of the plot over the three weeks. To do this, we placed the 0.5 x 0.5 meter quadrat over the plot. The quadrat is divided into 25 10 x 10 cm squares. We visually determined the amount of D. geminata inside each individual square at each plot along with the depth of the algae (mm) in the particular square. The volume index was calculated by multiplying the percent cover by the depth for each of o the 16 plots. The plots were first scored on July 3rd (prior to removal) and continued to be scored every 7 to 10 days until July 27th. On July 28th we sampled the center of each of the 16 plots for benthic invertebrates using a 31 cm by 31 cm Hoffman sampler with 375 micrometer mesh and electrobug sampling methods (Taylor et al. 2001). We separated the invertebrates by plot and taxa in the field and preserved the samples in water. We used a dissecting microscope to identify and count the invertebrate. Most of the taxa were classified to genus or species using Ward et al. (2002) and Peckarsky et al. (1985), except for chironomid larvae which we identified to family. The differences in abundance between plots were tested using a Hotelling’s T2 test.  Species diversity metrics (e.g., richness, evenness, and dominance) will be rarefied using EcoSim, pooling across all 16 plots and differences assessed using generated 95% confidence intervals from EcoSim software (Gotelli and Enstminger 2004).  

Project abstract:  
Data variables arrangement: columns
Data variables description: Rows represent the information collected from each .5 x .5 meter plot on a specific day

Project Audit
Have these data been audited? No
Who audited these data? 
Are the metadata and associated data file of sufficient quality to repeat the study?  

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