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Temporal and Spatial Variability of Groundwater Nitrate in the Southern Willamette Valley, Oregon

Temporal and Spatial Variability of Groundwater Nitrate in the Southern Willamette Valley, Oregon. Glenn Mutti & Roy Haggerty Oregon State University Department of Geosciences. Introduction. Overview of previous spatial and temporal studies Sampling Network Results and Implications

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Temporal and Spatial Variability of Groundwater Nitrate in the Southern Willamette Valley, Oregon

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  1. Temporal and Spatial Variability of Groundwater Nitrate in the Southern Willamette Valley, Oregon Glenn Mutti & Roy Haggerty Oregon State University Department of Geosciences

  2. Introduction • Overview of previous spatial and temporal studies • Sampling Network • Results and Implications • Modeling Nitrogen Dynamics • Conclusions

  3. Spatial Distribution of Nitrate from Previous Studies

  4. Prior Documentation of Temporal Variability (From Faega et al., 2004)

  5. Hypothesis • Seasonal precipitation should impact shallow groundwater nitrate concentrations • Why should it matter? • Distinguish seasonal trends vs. actual trends in monitoring data • Determine optimal sampling periods

  6. Monitoring Network • 19 wells sampled monthly for 15 months • 15 residential wells • 4 monitoring wells • Well log extant • Well Depth ≤ 50 ft • Screening Interval ≤ 15 ft • Pass Coliform bacteria test

  7. Was there Seasonal Variability? • Yes, precipitation influences nitrate values • However, seasonal wetting patterns are critical!

  8. Wetting Up Period Necessary to have NO3- Response • Used water levels to indicate when recharge occurred • Soil needs to wet up before recharge, then groundwater nitrate values respond to precipitation

  9. When might policy managers want to sample?

  10. Can we relate temporal variability to spatial variability?

  11. n = 6 n = 6 n = 7 n = 9 n = 10 Sample Distributions Based on Geology and Soil Qal = Holocene Floodplain and Alluvial Deposits Qs = Pleistocene Alluvium and Flood Deposits FSL= Fine Sandy Loam SCL= Silty Clay Loam SL= Silt Loam n = 6 n = 6 n = 6

  12. Part II: What if we can model these Variabilities?

  13. Modeling Goals • Calibrate SWAT so that reasonable outputs are obtained and validated • Examine different land management options and their impact on leached nitrate • Examine future scenarios and the impacts of nitrate Best Management Practices

  14. DEM LULC Soils SWAT GIS Inputs

  15. Non-GIS Model Inputs • Climate Data • River flows originating from non-modeled areas • Land Management Practices

  16. Cascades Coast Range Modeled Area & Pre-Calibration Results

  17. Closing Points • Relationship between NO3- and precipitation may be biased by data set: needs further analysis • Data uncertainties have yet to be analyzed • Small sample size could limit the significance of results

  18. Conclusions • Nitrate concentrations in the Southern Willamette Valley are dynamically linked to precipitation during recharge months • The recharge month with the highest annual precipitation is likely to have the highest annual groundwater NO3-concentration (but also the highest variability!!) • Wells drilled in different geologic formations or soil classes are likely to exhibit different seasonal variabilities

  19. Acknowledgements: • Funding provided by: USGS Small Grants Program, Award No. 01HQGR0145 • SWAT Development: USDA ARS and Blackland Research Center, Texas A&M University

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