Relationship between size of vegetative buffers and transport of fecal coliform bacteria from pasturelands treated with dairy cow manure T. Sullivan,

Slides:



Advertisements
Similar presentations
Hydrology Rainfall - Runoff Modeling (I)
Advertisements

Pollutant Removal Effectiveness of Vegetated Biofilters, Exfiltration Trenches and Vegetated Filter Strips for Linear Project Applications April 13, 2011.
Prepared by WMC Consulting Engineers Inc. John A. Wengell.
Post Construction Runoff Control & BMPs J. C. Hayes, Ph.D., P.E. & D. Hitchcock, Ph.D. South Carolina Stormwater Forum May 8, 2007 Columbia, SC.
Jeanette A. Thurston-Enriquez
Runoff Estimation, and Surface Erosion and Control Ali Fares, PhD NREM 600, Evaluation of Natural Resources Management.
Runoff Processes Reading: Applied Hydrology Sections 5.6 to 5.8 and Chapter 6 for Tuesday of next week.
AMS 25th Conference on Hydrology
Unit 4 Climate Part 2 Factors affecting water movement.
Stormwater Management
Schuykill River Watershed. ebrateDetail.cfm?wsid=29.
Continuous Hydrologic Simulation of Johnson Creek Basin and Assuming Watershed Stationarity Rick Shimota, P.E. Hans Hadley, P.E., P.G. The Oregon Water.
Hydrologic Abstractions
Infiltration Infiltration is the process by which water penetrates from ground surface into the soil. Infiltration rate is governed by: rainfall rate hydraulic.
G.S. Karlovits, J.C. Adam, Washington State University 2010 AGU Fall Meeting, San Francisco, CA.
Predicting Nitrogen Fertilizer Response in Douglas-fir Plantations Kim Littke Rob Harrison.
Vegetative Treatment Area Performance and Design Recommendations Joshua W. Faulkner Biological and Environmental Engineering Cornell University.
Forest Hydrology Issue: Interaction of forests, fish, and climate One of the dominant pathways by which land cover change affects freshwater fish habitat.
Engineering Hydrology (ECIV 4323)
Biological and Environmental Engineering Soil & Water Research Group Hydrological pathways in a glaciated watershed in the Catskill Mountains Adrian Harpold.
Effects of Including Hysteresis when Simulating Infiltration Swen Magnuson AgE 558 April 13, 2001.
In a 16 mile corridor along I-82, from Granger to Grandview, 76 dairy facilities ranging from 2000 to head, began their operation.
Determining the effectiveness of best management practices to reduce nutrient loading from cattle grazed pastures in Utah Nicki Devanny Utah State University,
Kristie J. Franz Department of Geological & Atmospheric Sciences Iowa State University
BACTERIAL CONCENTRATIONS IN BULL CREEK AUSTIN, TEXAS Patrick Sejkora.
DIMITRI LAZARIDIS AND PHILIP APPLETON SUCCESSFUL GOLF COURSE DRAINAGE.
The University of MississippiNational Center for Computational Hydroscience and Engineering Rainfall runoff modeling in agricultural watershed using 2D.
Watershed Management Water Budget, Hydrograph Analysis
Towards a Better Design of Micro-Catchment Water Harvesting Schemes.
Chowan River TMDL Development and Source Assessment Blackwater River Area October 25, 2004.
Discussion of Proposed MS4 Permit Design Standards Language.
ADSORPTION OF FECAL COLIFORMS, ESCHERICHIA COLI IN DIFFERENT SOILS IN SARAWAK Ling Teck Yee, Goh Soon Hian and Kasing Apun Faculty of Resource Science.
Seifu A Tilahun School of Civil & Water Resources Engineering,BDU Storm Runoff and soil erosion processes on the Ethiopian highland.
Patapsco/Back River SWMM Model Part I - Hydrology Maryland Department of the Environment.
Objective: Have a working knowledge of the relationship between the vegetative cover in a watershed and water yield and water quality.
Sources of streamflow from hillslopes Baseflow streamflow maintained by groundwater contributions Stormflow Augmented by direct precipitation on saturated.
Stormwater Water Quality Treatment Options Alvin Shoblom, P.E. Hydraulics Engineer.
Wetlands Ecology in the Lake Erie Basin. Overview What is a wetland? Case study Types of treatment wetlands Wetlands for water quality Important variables.
Sediment Delivery to the Watonwan River
Drainage Basin. Mississippi River Basin Drainage Basin.
October 12, 2015 Iowa State University Indrajeet Chaubey Purdue University Water Quality.
Surface Water Surface runoff - Precipitation or snowmelt which moves across the land surface ultimately channelizing into streams or rivers or discharging.
Grazing Management Effects on Non-point Source Pollution of Pasture Streams J.R. Russell 1, D.A. Bear 1, K.A. Schwarte 1, and M. Haan 2 1 Iowa State University,
Hydrograph Analysis. Components of river flow Contributions into a river/stream Overland flow – Flow over land surface due to precipitation (runoff)
Some Basic Hydrologic Concepts Weir are used to measure volume of water flowing past a point.
Reduction of Road-Generated Stream Suspended Sediment by a Riparian Buffer — case study from northern Thailand Alan Ziegler University of Hawaii (UHM)
Ron Fleming and Malcolm MacAlpine University of Guelph Ridgetown Campus, Ridgetown, ON, N0P 2C0 Paper No. CSBE
Effects of N Loadings from Dairy Cows to the Susquehanna River Effects of N Loadings from Dairy Cows to the Susquehanna River Austin Weidner CE394K : GIS.
EROSION CONTROL BY LAND MANAGMENT WHAT IS EROSION The detachment and transportation of soil particles from one place to other by running water, wind.
6. Drainage basins and runoff mechanisms Drainage basins Drainage basins The vegetation factor The vegetation factor Sources of runoff Sources of runoff.
Precision Management beyond Fertilizer Application Hailin Zhang.
Maximum Liquid Manure Spreading Rates on Sloping Land Ron Fleming and Malcolm MacAlpine University of Guelph Ridgetown Campus CSBE
Rick Cruse, Greg Brenneman, and Matt Helmers Iowa Water Center and Iowa State University Extension.
RACC High School Training June 26, 2012 Jody Stryker University of Vermont Introduction to Watershed Hydrology.
Let’s Begin! Writing Manure Management Plans!. Manure Management Manual DEP Manure Management Manual can be divided into 3 Parts: Part I Requirements/Guidelines.
a) Water stored in the rocks below ground
Soil erosion by water EROSION Detachment – particle or aggregate loosened from surface Entrainment – initiation of motion by flow TRANSPORT Rill – concentrated.
BUILDING AND RUNNING THE HYDROLOGICAL MODEL
How well does the NARR data simulate recharge to groundwater?
Case Study: Evaluating Retrofit Urban Best Management Practice Performance and Lessons Learned Nick Muenks, Marc Leisenring, Mark Willobee – Geosyntec.
Water Balance in MIKE-SWMM
DO NOW Pick up notes and Review #20..
Analysis of Hydrographs
Scientific or Engineered Landfilling of Waste
Patrick Tara, Jeff Vomacka, Mark Ross
Areas of Environmental Concern in Livestock
Hydrology and drainage
THE WATER CYCLE.
Groundwater Where does the water go?.
Presentation transcript:

Relationship between size of vegetative buffers and transport of fecal coliform bacteria from pasturelands treated with dairy cow manure T. Sullivan, E&S Environmental J.A. Moore, Oregon State University D. Thomas, Oregon State University E. Mallory, Oregon Streamside Service K.U. Snyder, E&S Environmental M. Wustenberg, Kilchis Dairy Herd Services S. Mackey, E&S Environmental T.W. Downing, Oregon State University

Keeping manure out of water Transport a complex function of many interrelated variables Transport a complex function of many interrelated variables 1) Bacterial loading 2) Soil conditions (moisture, air space) 3) Rainfall rate and intensity 4) Microbial die off (time in-between applications) - Castelle et al., 1994, Wenger, 1999, Gerba et al., 1975

Vegetative buffer strips Generally accepted as useful, but effective? Generally accepted as useful, but effective? Studies have not always agreed. Studies have not always agreed. 1) 100% removal with strips 6.1, 12.2 and 18.3 m with simulated rainfall of 7.4 cm. Edwards et al., ) Vegetative strips not adequate in meeting water quality goals (70% reduction in fecal coliform at 10 m) Walker et al., 1990, Coyne et al., 1998

Objectives 1) Examine FCB transport across vegetative filter strips of various sizes and slopes and compare to no buffer 2) Understand cost/benefit of increased buffer size or design

Materials and Methods Site had no manure for three years Site had no manure for three years 22 experimental treatment cells (14 m x 30 m) 22 experimental treatment cells (14 m x 30 m) Each cell had a simulated pasture area that was mowed periodically Each cell had a simulated pasture area that was mowed periodically Designated vegetative buffer strip (0,1,5,8,15,25m) Designated vegetative buffer strip (0,1,5,8,15,25m) Designed to be hydrologically isolated by using ditches all around the cell Designed to be hydrologically isolated by using ditches all around the cell

Materials and Methods Eleven cells were on a gentle slop (3.8%) and eleven were on a moderate slope (7%) Eleven cells were on a gentle slop (3.8%) and eleven were on a moderate slope (7%) Each cell had two samplers (1.2m) installed in the ditch running perpendicular to the cell Each cell had two samplers (1.2m) installed in the ditch running perpendicular to the cell Separated compartments connected to 10 sampling bottles Separated compartments connected to 10 sampling bottles Samplers were designed to catch overland flow and shallow groundwater (15cm) flow from the treatment cell Samplers were designed to catch overland flow and shallow groundwater (15cm) flow from the treatment cell

Materials and Methods Treatment/sampling was planned prior to and during major storm events Treatment/sampling was planned prior to and during major storm events Fresh scrape manure was applied (132.5 L) in a 10.8 m strip across each cell Fresh scrape manure was applied (132.5 L) in a 10.8 m strip across each cell Water samples from each cell were collected at 24 hour intervals, pooled and analyzed for fecal coliform bacteria Water samples from each cell were collected at 24 hour intervals, pooled and analyzed for fecal coliform bacteria Nine storms were sampled over 2 years Nine storms were sampled over 2 years

Materials and Methods Year 1 Year 1 - Two storms sampled - first storm no manure applied Year 2 Year 2 - Seven storms sampled

Precipitation StormPrecipitation (cm) Precipitation Flux to each experimental cell per unit of pasture length (L/m)

Percent runoff by storm Gentle slope Mod. Slope

Bacteria Concentration (gentle slope) Storm 1Average cfu/100ml Median cfu/100ml Control m241 15m m m Zero0164,6275,896

Bacteria Concentration (moderate) Storm 1Average cfu/100ml Median cfu/100ml Control031 25m m m m786 Zero92,008786

Conclusion Only 10% of all treatment cells with buffers had FCB >200 cfu/100ml Only 10% of all treatment cells with buffers had FCB >200 cfu/100ml Any buffer greater than 1 meter reduced FCB by over 99% (average was 26x10 6 cfu/100ml) Any buffer greater than 1 meter reduced FCB by over 99% (average was 26x10 6 cfu/100ml) No differences between cells on different slopes No differences between cells on different slopes Soil type (infiltration capability) may be the most important variable in determining buffer size to effectively reduce FCB runoff Soil type (infiltration capability) may be the most important variable in determining buffer size to effectively reduce FCB runoff

What does this mean? Vegetative buffers (soil?) can be extremely effective at reducing bacteria movement Vegetative buffers (soil?) can be extremely effective at reducing bacteria movement I believe the effectiveness is directly related to soil saturation – or air space I believe the effectiveness is directly related to soil saturation – or air space Site specific guidelines still appear to be the best management approach Site specific guidelines still appear to be the best management approach