Using Benthic Macroinvertebrate Populations to Assess Campus

Slides:



Advertisements
Similar presentations
Background The monitoring of our natural environment is becoming an increasingly important matter. With the human population reaching 7 billion, more and.
Advertisements

Biological Assessment Developed by Ken Cooke Kentucky Division of Water Watershed Watch Program Coordinator Modified by Mike Kemp Professor of Environmental.
Watershed Watch Protocols Level I. Goals for this module Understand how biomonitoring is used to evaluate the health of a stream Understand how biomonitoring.
Benthic Macroinvertebrates
Clearwater River Habitat/Bioassessment
A Comparative Study of Water Quality and Aquatic Macroinvertebrate Diversity in the Rio Grande and its Ditches By Lian Liu Mentor: Ayesha Burdett.
Lec 12: Rapid Bioassessment Protocols (RBP’s)
Introduction Larvae of the caddisfly Leucotrichia live in silk cases attached to hard surfaces in streams (McAuliffe 1982). They construct cases in summer,
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.
The relationship between riparian areas and biological diversity A comparison of streams in eastern Colorado and southwestern Virginia By Ann Widmer
Aquatic invertebrates and water quality monitoring in the Little Luckiamute River Aquatic invertebrates and water quality monitoring in the Little Luckiamute.
An Assessment of the Benthic Community Structure: Implications on the Water Quality of Lake Palacpaquen, San Pablo City, Philippines Perez, Terresita.,
Benthic Macroinvertebrate Survey Honors Biology
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.
Printed by My results indicate that:  Periphyton and macroinvertebrate abundance had a positive relationship to light intensity.
A Comparative Stream Study of Two First Order Streams in Nixon Park, York PA Susan Price Department of Biological Sciences, York College Introduction Macroinvertebrates.
Final stuff: n Lab practical: Apr 29 n Final exam: due Fri May 2:15.
National Aquatic Resource Surveys Wadeable Streams Assessment Overview November, 2007.
 Sustainability Master Plan  Effect of Runoff on Stream  Negative Effect on Lake Carnegie  Final Pre-Restoration Assessment  Why this first order.
Biological Assessment Developed by Ken Cooke Kentucky Division of Water Watershed Watch Program Coordinator Modified by Mike Kemp Professor of Environmental.
Indirect Effects of Current Velocity on Algal Abundance Through Interactions with Ceratopsyche Larvae Sarina Rutter with faculty mentor Todd Wellnitz Department.
Rapid Bioassessment Protocols for low gradient streams) for species richness, composition and pollution tolerance, as well as a composite benthic macroinvertebrate.
Loudoun Wildlife Conservancy Stream Monitoring Kickoff March 4, 2012 Rust Library Leesburg, VA.
Sampling Biodiversity Using macroinvertebrates
Why Assess Biological Water Quality? Role in government decision making Role in government decision making Decide which areas need help first Decide which.
Impact of Native Tree Species Foliage on Aquatic Invertebrate Communities Branden Birth Department of Biological Sciences, York College of Pennsylvania.
Water Assessment Data Lab Assignment # 5 Land Use The first thing you notice when field sampling is the area around your site. What type of land use.
Janet Garcia Ayesha Burdett
Lab: Benthic Bugs and Bioassessment
The Effects of Lake Productivity and Campsite Usage on Crayfish Abundance Within the Boundary Waters Canoe Area Sarah Schieffer, Nicole Bauer, Brandon.
Macroinvertebrates Little Creatures that tell us If our natural waterways are healthy.
The Arizona Rivers Project Southwestern Academy June 2009 Fun with Macroinvertebrates.
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”?
C.4: Conservation of biodiversity
Look Closely for Water Quality Activity by Alison Smith, SRP.
TITLE OF YOUR POSTER GOES HERE Student Names go here Science And Math Institute, Tacoma, Washington Abstract Introduction MethodsMethods Continued Discussion.
Effects of Stream Restoration: A Comparative Study of Pine Run in Felton, Pennsylvania Luke Mummert, Department of Biological Sciences, York College of.
Objective Two classic theories attempt to explain how natural communities assemble: Gleason’s Individualistic model and Clements’ Organismic model. To.
Climate Change Impacts on Estuarine Larval Fish Composition Jamie F. Caridad and Kenneth W. Able Institute of Marine and Coastal Sciences. Rutgers University.
Acknowledgements: We would like to give a special thanks to Lois Helland for allowing us access to Lowes Creek, Shane Opatz for his photographs, and LTS.
2013 Testing a new invertebrate-based river biomonitoring scheme for tropical rivers in Africa Isabel Moore, Kevin Murphy IBAHCM, University of Glasgow,
Biodiversity of Macroinvertebrates at Argyle Lake
The Effect of Substrate Size on Macroinvertebrate Distribution in Little Niagara Allison Ban-Herr, Morgan Freeburg, Alexandra Hillstrom and Katlynn Kralewski.
Todd Wellnitz1 and William Hintz2
Claudette Kellar Research Summit August 2016
Aquatic Macroinvertebrate Composition Over an Elevation Gradient
Distribution of Earthworms and Other Invertebrates on the Upper and Lower Terraces of Putnam Park Jenna Barlow, Cory Dick, Brian Johnson, Wil Raasch, Terrance.
5.2 Detection and Monitoring of Pollution
Fun with Macroinvertebrates
Assessing PA’s Lake Erie Tributaries
WATER QUALITY Vol 3: Biological Characteristics
Biological Assessment of Pond Health
Intro to Stream Monitoring
a Biological Study of Macroinvertebrates in the Leibert Creek
Warmup What can biodiversity indicate about an ecosystem? (reference page 67 notebook)
Nathan Servey, Brennan Dow, Brittany Burant and Mason Loden
Butternut Creek Biomonitoring
Using Bugs and GIS to Assess and Manage Watershed Health
Macroinvertebrates are animals without a backbone that can be seen with the naked eye. These bottom-dwelling animals include crustaceans and worms but.
MacroinverteWHATS? Macroinvertebrates!.
Trends in Invertebrate Feeding Strategies
Macroinvertebrates.
The Index of Biotic Integrity (the BI or IBI)
Benthic Invertebrate Distribution in
The Four Phases Phase 1: Teach Phase 2: Collect Phase 3: Report
Jenna Marcotte1, Emily Picchiello1, John Halloran1
Presentation transcript:

Using Benthic Macroinvertebrate Populations to Assess Campus Impacts on Little Niagara Creek Biology  University of Wisconsin-Eau Claire Danielle Mares and Brian Johnson ( Dr. Todd Wellnitz, mentor) Results Introduction Are students destroying Little Niagara Creek? This stream is a great resource for the UWEC science classes and is used for many field labs and research projects. But is this heavy use damaging the stream and the populations of benthic macroinvertebrates that live there? Biological diversity is critical for the healthy functioning of all ecosystems, and richness and diversity of stream organisms, particularly macroinvertebrates, are important indicators of a stream’s overall health (Voshell & Bartlett 2002). By sampling macroinvertebrates in Little Niagara at sites before, within, and after campus, we aimed to analyze the health and state of this stream, and ultimately, the effects of campus usage on this valuable UWEC resource.   Discussion Our results suggest that student and class activities on campus do not have adverse affects on Little Niagara stream health. This is good news for the UWEC science departments! The lower richness seen after campus may be a consequence of the lack of riparian vegetation found there. Before and within campus, the stream is surrounded by tall grasses that lean into the water and provide habitat for Broadwinged Damselflies. After campus, the banks are bare, lack grasses, and the streambed has no aquatic plants. These differences correspond to the changes in species richness, suggesting habitat, not campus usage, is largely responsible for the composition of Little Niagara’s macroinvertebrate populations. Although species richness within the campus is quite high, sow bugs, a species tolerant to pollution, dominated the assemblage. Also, the abundance of several species within the campus section was quite low, indicating lower evenness in the assemblage. This lack of evenness and dominance of a pollution-tolerant species suggests that the stream is not functioning at an optimal level and could be improved. Before Campus 15 10 5 Before campus Within After Species Richness Sow bugs (11%) Net-spinner caddisfly (7%) Broadwinged damselflies (56%) Species richness differed among the three stream locations (F = 10.17; P = 0.012). It was highest before and within campus, and lowest after campus. Within Campus Broadwinged Damselfly Students sampling a section of Little Niagara Creek for a biology class. Methods: D-frame kick nets were used to sample sections of Little Niagara Creek before, within and after campus. Three, 2-minute samples were taken in each section. Collected macroinvertebrates were preserved in 70% ethanol and then sorted, identified and counted in the lab. Statistical analyses were conducted using one-way ANOVAs to test the effect of stream location on species richness and organism abundance. After Campus Sow Bug Water spider (6%) The abundant aquatic plants on the streambed within campus. Blackfly Larvae (6%) 50 10 Before campus Within After Number of individuals Broadwinged damselflies Sow bugs 20 30 40 References Voshell, J. and Bartlett, A. (2002). A Guide to Common Freshwater Invertebrates of North America. McDonald & Woodward Publishing Company. 456 p. Invertebrate Images: Sow bug: http://www.bing.com/images Broadwinged Damselfly: http://aquaticinsectsofcentralvirginia.blogspot.com Acknowledgements Dr. Matthew Evans for consultation and mentoring The Blugold Fellowship Program for supporting this research. Learning & Technology for printing this poster. Sow bugs (81%) The three sampling sites on Little Niagara Creek (Goggle Earth image) After Campus Before Community composition of benthic macroinvertebrates in Little Niagara Creek. Each species is indicated by a different color, and the size of the wedge represents the percent abundance. The three most abundant species at each site are listed. Different species dominated at each location. Before campus, Broadwinged damselflies made up 56% of all individuals collected, but within and after campus, Sow bugs were most abundant at 46% and 83%, respectively.