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U.S. Department of the Interior
U.S. Geological Survey
Michigan Water Science Center

 

In cooperation with the U.S. Department of Agriculture, Natural Resources Conservation Service and the Lenawee Conservation District

Chemical and Microbiological Water Quality of Subsurface Agricultural Drains during a Field Trial of Liquid Dairy Manure Effluent Application Rate and Varying Tillage Practices, Upper Tiffin Watershed, Southeastern Michigan

U.S. Geological Survey Open-File Report 2008–1189

By Sheridan Kidd Haack and Joseph W. Duris

ONLINE ONLY

 


This report is available below as a 38–page PDF for viewing and printing.


Abstract

A field trial was done in the Upper Tiffin River Watershed, in southeastern Michigan, to determine the influence of liquid dairy manure effluent (LDME) management practices on the quality of agricultural subsurface–drain water. Samples from subsurface drains were analyzed for nutrients, fecal–coliform and Escherichia coli (E. coli) bacteria, antibiotics, chemicals typically detected in wastewater, and the occurrence of genes indicating the presence of shiga–toxin–producing E. coli, or of bovine–specific Bacteroidetes bacteria. Samples were collected from November 2, 2006, to March 20, 2007, from eight subsurface drains under field plots that received no LDME and no tillage (controls) or received 4,000 or 8,000 gallons per acre (gal/acre) of LDME and either no tillage or two different types of tillage. The two types of tillage tested were (1) ground–driven, rotary, subsurface cultivation and (2) rolling–tine aeration. Samples were collected before LDME application and at 4 hours, and 1, 2, 6, 7, and 14 days post–application.

 

Nutrient concentrations were high in subsurface–drain water throughout the field–trial period and could not be attributed to the field–trial LDME application. Of the 59 drain–water samples, including those collected before LDME application and control samples for each date, 56 had concentrations greater than the U.S. Environmental Protection Agency (USEPA), Ecoregion VI recommended surface–water criterion for total phosphorus, and all samples had concentrations greater than the recommended total nitrogen criterion. Nitrate + nitrite nitrogen concentration exceeded 20 milligrams per liter for every sample and contributed most to the total nitrogen concentrations. Substantial increases in drain–water concentrations of organic and ammonia nitrogen and total phosphorus were found for all treatments, including controls, at 14 days post–application after 0.84 inch of rainfall over 2 days.

 

E. coli concentrations exceeded the USEPA recreational–water–quality single–sample criterion of 235 colony forming units per 100 milliliters in only 3 of 56 samples. Of these three samples, two were collected within 1 day post–LDME application from the treatment receiving 8,000 gal/acre LDME with no tillage (NT8000). The third sample was from the rolling–tine aerator treatment with 4,000 gal/acre LDME application rate after the first significant rainfall.

 

Two wastewater chemicals and two bacterial genes (eaeA and stx1) detected in the LDME, but absent in field blank or pre–application samples, were detected in the 4–hour or 1–day post–application NT8000 samples. No LDME–associated chemicals were detected in later samples from the NT8000 treatment, and none were detected in samples from other treatments after the first significant rainfall.

 

Results of this field trial were somewhat equivocal with respect to the influence of LDME concentration and tillage practices on subsurface–drain water quality, both immediately after LDME application and in the longer term, after significant rainfall. Interpretation of study findings is limited by the fact that treatments were not replicated, and flow rate or discharge from the subsurface drains was not measured. Nevertheless, study results provide useful information about nutrient and bacteria concentrations in subsurface drains during the non–growing season. In addition, study results demonstrate some potential for the use of chemical and microbiological indicators of LDME transport to subsurface drains.

 


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Covers 1 and 4 (front and back) (56 KB) - 2 pages (8.5” by 11” paper)

Whole report (475 KB) - 38 pages (8.5” by 11” paper)

 


 

Suggested Citation:

Haack, S.K., and Duris, Joseph W., 2008, Chemical and microbiological water quality of subsurface agricultural drains during a field trial of liquid dairy manure effluent application rate and varying tillage practices, Upper Tiffin Watershed, southeastern Michigan: U.S. Geological Survey Open-File Report 2008–1189, 38 p. Date Posted: July 30, 2008: [https://pubs.water.usgs.gov/ofr20081189/]

 


Contents

Abstract

Introduction

Purpose and Scope

Management Practices

Chemical and Microbiological Indicators of LDME Transport to Subsurface Drains

Conditions at the Study Area

Sampling and Analytical Methods

Sampling Procedures

Chemical Analyses

Microbiological Analyses

Bacteria Enumeration and Preservation

Microbiological Indicators of LDME Transport to Subsurface Drains

Immunological Test for O157 Antigen

DNA Extraction

Polymerase Chain Reaction (PCR)

Multiplex PCR for Shiga-Toxin-Producing E. coli

PCR for Bovine Bacteroidetes Gene

Quality Assurance/Quality Control

Results of Chemical and Microbiological Analyses

Specific Conductance and pH

Bacteria Concentrations

Nutrient Concentrations

Chemical Indicators of LDME Transport to Subsurface Drains

Microbiological Indicators of LDME Transport to Subsurface Drains

Study Limitations

Summary and Conclusions

References Cited

Appendix

 

Figures

   1. Map showing location of Upper Tiffin Watershed Conservation Effects Assessment Project area.

 

Tables

   1. Treatment definitions and abbreviations.

   2. Rainfall during the course of the field trial.

   3. Methods of nutrient analysis and reporting limits.

   4. Water–quality field data and bacteria concentrations for LDME on date of application and for all tile–water samples.

   5. Nutrient concentrations in LDME, field blank, and tile–water samples.

   6. U.S. Environmental Protection Agency Ambient Water-Quality Criteria and 25th percentiles for nutrients in Ecoregion VI
       (Corn Belt) and Level III Ecoregion 57 (Huron/Erie Lake Plain).

   7. Results of antibiotic and wastewater chemical analyses for LDME, pre–application sample, and NT8000 treatment
       (Tile 6) over time.

   8. Results of wastewater–chemical analyses for field blank and for all treatments after the first significant rainfall event.

   9. Results of analyses for microbiological indicators in subsurface drain water for NT8000 treatment before and after
       addition of liquid dairy manure effluent.

 10. Results of analyses for microbiological indicators in LDME and all treatments before LDME application and at 6 days
       post–application.

1–1. Wastewater–method compound names, U.S. Geological Survey National Water Quality Laboratory reporting limits,
       and possible compound uses or sources.

1–2. Antibiotic analytes by liquid chromatography/mass spectrometry.

 


For additional information, contact:

U.S. Geological Survey
Michigan Water Science Center
6520 Mercantile Way, Suite 5
Lansing, MI 48911–5991
GS-W-MIlns_DC@usgs.gov

 

or for more information about USGS activities in Michigan, visit the USGS Michigan Water Science Center home page.



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