Comparison of Aquatic Invertebrates in Pool and Riffle Habitats of Blackburn Fork Comparison of Aquatic Invertebrates in Pool and Riffle Habitats of Blackburn.

Slides:



Advertisements
Similar presentations
AUTAUGA CREEK BENTHIC INVERTEBRATE COMMUNITY ASSESSMENT, 2009 Will S. Mooty USGS.
Advertisements

David McCormick & Simon Harrison
Biological Response of Two North Central PA Streams After Flood of September 2011 Fred Rogers CWI, Supervisor Dr. Mel Zimmerman Introduction: Within Pennsylvania,
Tennessee Technological University
ECOLOGICAL RESPONSES TO NUTRIENTS Utah Division of Water Quality Snake Creek, Heber Valley, 2014.
Trait-based Analyses for Fishes and Invertebrates in Streams Mark Pyron Stoeckerecological.com.
Melissa Churchel 1, Jim Hanula 2, Wayne Berisford 1 and Jim Vose 2 1 Department of Entomology University of Georgia 2 USDA Forest Service Southern Research.
Testing for Ammonia in Cumberland County Lakes Mary Paradis TTU Undergraduate Cookeville,TN.
Lec 12: Rapid Bioassessment Protocols (RBP’s)
An analysis of the aquatic insect communities of McMichael Creek, PA under open and closed canopies Christopher Hartzler, James Hartzler, Bradley Rehnberg.
Watershed System Physical Properties Stream flow (cfs) Stream Channel Pattern Substrate Chemical Properties pH Dissolved Oxygen Temperature Nutrients Turbidity.
Roadway pollutant effects on abundance of Odonate nymphs in a wetland of the Eastern Highland Rim, Tennessee Jason Payne, Undergraduate Student (Marine.
Roadway pollutant effects on abundance of Odonate nymphs in a wetland of the Eastern Highland Rim, Tennessee Jason Payne, Undergraduate Student (Marine.
Do installed steam logjams increase macroinvertebrate richness and abundance? Seyeon Kim and Ong Xiong with faculty mentor Dr. Todd Wellnitz Biology Department.
Conclusion -Velocity affects the temperature, pH and DO of a stream; the greater the velocity, the greater the water quality -The positive correlation.
Final stuff: n Lab practical –Coleoptera, Hemiptera n Final exam: Fri May 2:15 –Assessment with Invertebrates n Lecture material (IDEM protocol) n.
Bioassessment 1.0. Stream Visual Assessment Protocol 1. Turbidity 2. Plant growth 3. Channel Condition 4. Channel Flow Alteration 5. Percent Embeddedness.
Metric (Family Level) Standard Best Value (95 th or 5 th percentile) Worst Possible Value Expected Response to Degradation Total Taxa180 EPT Taxa120 %EPT91.90.
Physical Factors: Current, Substrate, Temperature, and Oxygen Unit 1: Module 4, Lecture 3.
An Assessment of the Benthic Community Structure: Implications on the Water Quality of Lake Palacpaquen, San Pablo City, Philippines Perez, Terresita.,
Improvement of Meadow Stream Health due to Livestock Distribution Efforts K.W. Tate, T.A. Becchetii, C. Battaglia, N.K. McDougald, D.F. Lile, H.A. George,
Name of presenter Date of presentation.  To help preserve and protect Wisconsin’s over 15,000 lakes and 86,000 miles of rivers.
STREAM ECOSYSTEMS.
Comparing aquatic macroinvertebrates communities between native and invasive plant species in Mill Creek Shelly Wesner Department of Biological Sciences,
Functional Diversity and Substrate Composition Shape Primary Productivity and Decomposition Patterns in an Aquatic Ecosystem Methods Background The impact.
Coastal development impacts on biological communities in the Chesapeake Bay Examples from the Atlantic Slope Consortium R
NC Division of Water Quality Water Quality Assessments and Local Watershed Plans.
Biological Assessment REFORM Summer School, Wageningen (NL), 28 June 2015 Christian Wolter Leibniz-Institute of Freshwater Ecology and Inland Fisheries.
A Comparative Stream Study of Two First Order Streams in Nixon Park, York PA Susan Price Department of Biological Sciences, York College Introduction Macroinvertebrates.
Correlations Between Stream Order and Diversity of Fishes in the Blackburn Fork Drainage, Tn. Michael H. Graf Undergraduate Student Fisheries Biology Concentration,
Nesting Abundance and Clutch Size of the Eastern Bluebird. Chris Carson Undergraduate Student, Dept. of Biology Tennessee Technological University, Cookeville,
Final stuff: n Lab practical: Apr 29 n Final exam: due Fri May 2:15.
The Effects of Lysol on Living Bacteria Final Platform Presentation Ashley Pruitt Undergraduate Student Health Science Biology concentration Department.
 Sustainability Master Plan  Effect of Runoff on Stream  Negative Effect on Lake Carnegie  Final Pre-Restoration Assessment  Why this first order.
Benthic Macroinvertebrate Assemblages in Flint River, Indian Creek and Flint Creek Watersheds in North Alabama- Preliminary Study R. Ward, L. White, A.
Effects of Acid Mine Drainage (AMD) on Nesting Tree Swallows.
Benthic Macroinvertebrate Sampling. Sampling -WHAT All available invertebrate taxa in the entire 200 foot stream reach -WHERE All available habitats in.
Biological Assessment Developed by Ken Cooke Kentucky Division of Water Watershed Watch Program Coordinator Modified by Mike Kemp Professor of Environmental.
Large River Fish ~ 10,000 species > 2,000 species in Amazon (not all unique) Ancient freshwater fishes are river fishes.
STREAM QUALITY in SOUGAHATCHEE CREEK. LEECH CRANE FLY MIDGE STONEFLY CADDISFLY MAYFLY GOOD WATER QUALITY (EPT~10-23) POOR WATER QUALITY (EPT~0-5)
WATER QUALITY, SPECIES DIVERSITY, AND QUANTITY IN A STREAM HABITAT Jason R. L. Holcomb Tennessee Technological University, Cookeville, Tennessee Introduction.
Ecomorphological Comparison of the Two Cyprinid Fishes Varicorhinus barbatulus and Candidia barbatus in Hapen Creek of the Northern Taiwan Ling-Chuan Chuang.
National Monitoring Conference May 7-11, 2006
Water Quality, Species Diversity, And Quantity In A Stream Habitat Jason Holcomb Undergraduate Wildlife Biology Department Tennessee Technological University.
Background As number of species varies with volume (Taylor, 1997, and others), how is assemblage stability affected when isolated pools shrink during summer?
Stream Health: biotic integrity variation in Owasco Lake watershed Susan F. Cushman Hobart and William Smith Colleges 2007 Finger Lakes Research Conference.
Water Quality of Mullins Creek/ Determined by Aquatic Diversity Josh Thomasson Biology-Environmental Concentration Tennessee Techological University Cookeville,
Middle Fork Project AQ 3 – Macroinvertebrate and Aquatic Mollusk Technical Study Report Overview May 5, 2008.
Ecological Principles of Diversity 1. Principle of Limiting Similarity - There is a limit to the similarity of coexisting competitors; they cannot occupy.
Aquatic Diversity of Macro Invertebrates in Mullins Creek Josh Thomasson Biology-Environmental Concentration Tennessee Techological University Cookeville,
Aquatic Invertebrates in Pool and Riffle Habitats of Blackburn Fork Michael Railling Wildlife and Fisheries Science Tennessee Tech.
Impact of tree species foliage on aquatic macroinvertebrate communities. Andrew Nevin Department of Biological Sciences, York College of Pennsylvania Introduction.
Record notes in your notebook  Record at least 5 facts/ideas in your notebook.  Write down and answer the following questions:  What are“benthic macroinvertebrates”?
National Water Quality Monitoring Conference Session E4 April 29, 2014 Jonathan Witt & Britta Bierwagen, ORD/USEPA Jen Stamp & Anna Hamilton, Tetra Tech,
Michael Sorge Wisconsin Dept. of Natural Resources.
Ecological Principles of Diversity 1. Principle of Limiting Similarity - There is a limit to the similarity of coexisting competitors; they cannot occupy.
Effects on Dissolved Oxygen during Generation at Center Hill Dam Jared Durrett Undergraduate Biology Department Tennessee Technological University Cookeville,
Effects of Stream Restoration: A Comparative Study of Pine Run in Felton, Pennsylvania Luke Mummert, Department of Biological Sciences, York College of.
A presentation by: Christine Adams, Louise Tunnah, Jen Dwyer, Steven Sutcliffe, Jenn O’Blenes, and Jill Briand.
Watershed Health Indicators
J. M. C. K Jayawardhana1, W. D. T. M Gunawardhana 1, E. P
Discover Life in West Virginia ( )
Using Benthic Macroinvertebrate Populations to Assess Campus
Water Testing Project for the North Fork River
Butternut Creek Biomonitoring
Hypotheses (motivate these in your introduction, discuss them in your discussion in the context of the results) There are patterns of association between.
Using Bugs and GIS to Assess and Manage Watershed Health
The Index of Biotic Integrity (the BI or IBI)
Hypotheses (motivate these in your introduction, discuss them in your discussion in the context of the results) There are patterns of association between.
The Effects of Pond Characteristics on Communities of Large Invertebrates Alexander R Salazar1,2, Debora Goedert3,4, Craig D Layne3, Kathryn L Cottingham3,
Presentation transcript:

Comparison of Aquatic Invertebrates in Pool and Riffle Habitats of Blackburn Fork Comparison of Aquatic Invertebrates in Pool and Riffle Habitats of Blackburn Fork Michael Railling Department of Biology Undergraduate Student Tennessee Technological University Cookeville, TN USA

Introduction/Background The Blackburn Fork is a productive 4th order stream in Jackson and Putnam counties (Baker 1994). On 9/14/03 a sampling effort was conducted along a 100 meter stretch of Blackburn Fork to compare macroinvertebrate community structures between pool and riffle habitats. This is the background used for the research. ► Stream macroinvertebrate assemblage varies at both regional and local scales (Heino et al. 2003). ► Lower water quality is directly associated to diversity (Heino et al. 2003). ► Abundance of the macroinvertebrates can be affected by many factors but habitat is the prime factor (Waters and Giovanni 2002). ► Some may prefer the larger cobble and faster currents of a riffle and other may prefer the slower and bedrock substrate found in a pool (Cushing and Allan 2001). ► Pools generally have higher dissolved oxygen levels and a more neutral pH. Water Qualities In pH and dissolved oxygen can have a significant effect on the biota (Boto and Bunt 1981).

Objective/Hypothesis Statement ► Hypothesis: Are aquatic macroinvertebrate assemblages the same in pool and riffle habitats in Blackburn Fork? ► Objective: To show that different taxa are found pool and riffle habitats using taxa richness and percent EPT’s and percent Chironomidae.

Methods and Materials ► 6 Hester-Dendy samplers were used qualitatively, 3 in pools and 3 in riffles. Hester-Dendy ► Two samplers from each habitat were scrubbed and seperated. ► Invertebrates were identified to genus. Invertebrates were identified to genus. Invertebrates were identified to genus. ► Results were scored using data forms to show the taxa richness, percent EPT’s, and percent Chironomidae (Tennessee Department of Environment and Conservation 2002).

Results and Discussion ► In all 17 taxa were found in riffles and 11 were found in pools (Table 1). Two of the taxa, Antocha and Nigronia serricornis were found in higher numbers in the riffle habitats. The presence of these genra is directly associated with higher dissolved oxygen concentrations (Weigel et al. 2003). Table 1Table 1 ► Seventeen EPT’s were found in the riffle habitats for a total of 3.78% (Table 2, Figure 2) Table 2, Figure 2Table 2, Figure 2 ► The pool habitat had 26 EPT’s for a total of 3.97% (Table 2, Figure 1). Table 2, Figure 1Table 2, Figure 1 ► A total of 416 Chironomids were found in riffles; making up 92.44% of the total composition (Table 2, Figure 2). Table 2, Figure 2Table 2, Figure 2 ► Table 2 and Figure 1 show that 627 Chironomids were found in the pool sites making up percent of the total composition. ► I agree with Marshall (2001) that taxa richness directly corresponds with water quality, however I disagree that percent EPT corresponds with the water quality in my research. ► My results back Marshall (2001) that Chironomidae are more abundant in poor water qualities.

Summary ► 3 samples were taken from pools and 3 from riffles riffles within a 100 meter stretch ► The lower water quality pools had higher percentage of Chironomidae, higher percentage of EPT’s, but had less richness. ► The higher water quality riffles had higher richness, less Chironomidae, but had lower percentage of EPT’s.