Water-Quality Monitoring in an Urban Watershed:

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Presentation transcript:

Water-Quality Monitoring in an Urban Watershed: The Influence of Septic Systems on Nitrate Concentrations and Spatial Patterns December 12th, 2016 Jimmy Webber jwebber@usgs.gov Ken Hyer kenhyer@usgs.gov John Jastram jdjastra@usgs.gov JK Böhlke jkbohlke@usgs.gov Judy Denver jmdenver@usgs.gov Michael Langland Langland@usgs.gov This information is preliminary and is subject to revision. It is being provided to meet the need for timely best science. The information is provided on the condition that neither the U.S. Geological Survey nor the U.S. Government shall be held liable for any damages resulting from the authorized or unauthorized use of the information.

Water-Quality Monitoring in an Urban Watershed: The Influence of Septic Systems on Nitrate Concentrations and Spatial Patterns Difficult Run nr Great Falls, VA USGS: 01646000 Sampling location included in Fairfax County monitoring network Sampling location within Difficult Run

Difficult Run nr Great Falls, VA Spatial Water-Quality Data Difficult Run nr Great Falls, VA USGS: 01646000 Reston Tysons Corner 1 100 Percent Impervious 1 Fairfax City 1Percent of impervious land cover from 2011 NLCD Hyer and others, 2016

Difficult Run nr Great Falls, VA Specific Conductance Data Difficult Run nr Great Falls, VA USGS: 01646000 2 Reston Tysons Corner 1 165 – 210 211 – 255 256 – 300 301 – 345 346 – 390 Specific Conductance, in μS/cm 2 Percent Impervious 1 Fairfax City 1 100 1Percent of impervious land cover from 2011 NLCD 2Specific conductivity data based on the average of 6 synoptic events between 2011 and 2015. Hyer and others, 2016

Difficult Run nr Great Falls, VA Landuse Difficult Run nr Great Falls, VA USGS: 01646000 Open Space Estate Residential Low-Density Residential Medium-Density Residential High-Density Residential Outside Jurisdiction High-Intensity Commercial Industrial Roads Low-Intensity Commercial Unknown LANDUSE 1 1Landuse from Fairfax County GIS data, 2014.

Difficult Run nr Great Falls, VA Nitrate-N Concentrations Captain Hickory Run Difficult Run nr Great Falls, VA USGS: 01646000 0.0 – 1.0 1.1 – 2.0 2.1 – 3.0 3.1 – 4.0 4.1 – 5.0 Nitrate-N, in mg/L Open Space Estate Residential Low-Density Residential Medium-Density Residential High-Density Residential Outside Jurisdiction High-Intensity Commercial Industrial Roads Low-Intensity Commercial Unknown LANDUSE 1 2 1Landuse from Fairfax County GIS data, 2014. 2Nitrate-N data based on the average of 6 synoptic events between 2011 and 2015. Hyer and others, 2016

Captain Hickory Run: Nitrate-N Concentrations Historic Agricultural Practices? Wastewater? Fertilizer Application? 0.0 – 2.0 2.1 – 4.0 4.1 – 6.0 6.1 – 8.0 8.1 – 10.0 Nitrate-N, in mg/L 2 Watershed Area = 1.38 mi2 2Nitrate-N data collected between 2012 and 2016. Preliminary Information-Subject to Revision. Not for Citation or Distribution

Difficult Run: Nitrogen Sources Captain Hickory Run Difficult Run nr Great Falls, VA USGS: 01646000 Geochemically Similar 1 2 Little Difficult Run 0.0 – 1.0 1.1 – 2.0 2.1 – 3.0 3.1 – 4.0 4.1 – 5.0 Nitrate-N, in mg/L 1 Conventional Septic System Alternative Septic System 2 2 1Nitrate-N data based on the average of 6 synoptic events between 2011 and 2015. 2GIS data of properties served by septic systems provided by Fairfax County, May 2015. Hyer and others, 2016

SF Little Difficult Run Fairfax County: Nitrogen Sources Captain Hickory Run 1 SF Little Difficult Run 2 Sampling location included in Fairfax County monitoring network in Small Watershed study (within Difficult Run) Elevated nitrate concentrations appear to be caused by high septic system density based on: (1) nitrate isotopes, (2) monthly nitrate concentrations, (3) land-use data, and (4) chemical indicators of wastewater. 0.0 – 1.0 1.1 – 2.0 2.1 – 3.0 3.1 – 4.0 4.1 – 5.0 Nitrate-N, in mg/L 1 Conventional Septic System Alternative Septic System 2 2 1Small watershed nitrate-N data based on the average of 6 synoptic events between 2011 and 2015. Fairfax county nitrate-N data based on the average of baseflow samples collected between 2008 and 2015. 2GIS data of properties served by septic systems provided by Fairfax County, May 2015. Hyer and others, 2016

Fairfax County: Nitrogen Sources No evidence of seasonally elevated nitrate concentrations that might be attributed to the runoff of lawn fertilization in the spring and fall. 1 Baseflow Conditions Stormflow Conditions Hyer and others, 2016

septic1/fertilizer2 TN load Fairfax County: Nitrogen Sources The mass of nitrogen available from septic system leachate could be approximately an order of magnitude greater than that from fertilizer. 0.1 – 1.0 1.1 – 4.0 4.1 – 7.0 7.1 – 10.0 Ratio of estimated septic1/fertilizer2 TN load 10.1 – 13.0 Primarily Fertilizer Primarily Septic 1Septic load computed from an estimated per capita septic system loading rate (Maizel and others, 1997). 2Fertilizer load computed from an estimated fertilizer application (Law and others 2004) and fertilizer-N leaching rate (Petrovic, 2008). Preliminary Information-Subject to Revision. Not for Citation or Distribution

Difficult Run: Nitrogen Sources Sites with elevated nitrate concentrations have δ15N values similar to those commonly attributed to sewage or septic system sources. Common delta N-15 values of nitrate sources: Forest soils Septic Art. fert. Manure Septic Watershed Difficult Run Smith Creek Upper Chester Common delta N-15 values of nitrate sources: Art. fert. Forest soils 2 2 **Typical range of error, 2-sigma Hyer and others, 2016

Captain Hickory Run: Indicators of Wastewater: 4-nonylphenol March 2016 June 2016 Site D Site C Site A Site B Site 34 Site 33 0.0 – 2.0 2.1 – 4.0 4.1 – 6.0 6.1 – 8.0 8.1 – 10.0 Nitrate-N, in mg/L 2 Site 25 Watershed Area = 1.38 mi2 2Nitrate-N data collected between 2012 and 2016. This information is preliminary and is subject to revision. It is being provided to meet the need for timely best science. The information is provided on the condition that neither the U.S. Geological Survey nor the U.S. Government shall be held liable for any damages resulting from the authorized or unauthorized use of the information.

Captain Hickory Run: Indicators of Wastewater: HF-183 Nitrate-N, July 2014 March 2016 June 2016 Below Detection Site D Site C Site A Site B Site 34 Site 33 0.0 – 2.0 2.1 – 4.0 4.1 – 6.0 6.1 – 8.0 8.1 – 10.0 Nitrate-N, in mg/L 2 Site 25 Watershed Area = 1.38 mi2 2Nitrate-N data collected between 2012 and 2016. This information is preliminary and is subject to revision. It is being provided to meet the need for timely best science. The information is provided on the condition that neither the U.S. Geological Survey nor the U.S. Government shall be held liable for any damages resulting from the authorized or unauthorized use of the information.

Difficult Run nr Great Falls, VA Nitrate-N Trend Nitrate concentrations and loads have increased at the Difficult Run streamgage between 1985-20143. Difficult Run nr Great Falls, VA USGS: 01646000 1Nitrate-N data based on the average of 6 synoptic events between 2011 and 2015. 2GIS data of properties served by septic systems provided by Fairfax County, May 2015. 3Trend analysis using Weighted Regressions on Time, Discharge, and Season (WRTDS). Results available online: http://cbrim.er.usgs.gov/ Hyer and others, 2016

Difficult Run: Nitrogen Load from Septic Based on base flow sampling results, approximately 5% of the total nitrogen load leaving the watershed may be contributed by septic systems: Water Year 2013: 9,000 lbs of TN from septic Water Year 2014: 16,500 lbs of TN from septic Water Year 2015: 13,000 lbs of TN from septic Recent USGS SPARROW results estimate that 26% of the total nitrogen load leaving the watershed may be contributed by septic systems3: Water Year 2013: 37,000 lbs of TN from septic Water Year 2014: 92,000 lbs of TN from septic Water Year 2015: 62,000 lbs of TN from septic Difficult Run nr Great Falls, VA USGS: 01646000 1Nitrate-N data based on the average of 6 synoptic events between 2011 and 2015. 2GIS data of properties served by septic systems provided by Fairfax County, May 2015. 3Ator S.W. and Sekellick A.J. To be released as a 2016 USGS Open File Report This information is preliminary and is subject to revision. It is being provided to meet the need for timely best science. The information is provided on the condition that neither the U.S. Geological Survey nor the U.S. Government shall be held liable for any damages resulting from the authorized or unauthorized use of the information.

Metro Washington COG: Landuse Percent Impervious Frederick County Difficult Run Watershed Frederick County Montgomery County Loudoun County D.C. Prince George Charles County Fairfax William Frederick County Montgomery County Loudoun County D.C. Prince George Charles County Fairfax William 25 50 75 100 Impervious1 Percent Forested Pasture/Hay Row Crop Low/High Development Wetlands/Open Water Landuse1 1Landuse and percent impervious from 2011 National Land Cover Dataset. http://www.mrlc.gov/nlcd2011.php

Metro Washington COG: Septic System Density Difficult Run Watershed Frederick County Septic system density = (total population in 2010) * (% of population on septic in 19901) Montgomery County Loudoun County Prince George County D.C. Fairfax County Prince William County Septic System Density Low High Difficult Run Watershed Charles County 11990 septic ratio = (person per household * housing units with septic) / total population. Values based on U.S. Census data. This information is preliminary and is subject to revision. It is being provided to meet the need for timely best science. The information is provided on the condition that neither the U.S. Geological Survey nor the U.S. Government shall be held liable for any damages resulting from the authorized or unauthorized use of the information.

Water-Quality Monitoring in an Urban Watershed: The Influence of Septic Systems on Nitrate Concentrations and Spatial Patterns Empirical nitrate concentrations are significantly correlated with septic system density. Although there tends to be a greater potential for fertilizer application in areas underlain by septic systems, septic system effluent appears to be the dominant source of nitrogen in Difficult Run and in similar Fairfax County watersheds. Septic Effluent vs Fertilizer Leachate December 12th, 2016 Nitrate concentrations from two watersheds with a high septic system density do not show seasonal variability or stormflow responses expected from inputs of N from fertilizer. How would changes to the septic infrastructure affect water-quality? Jimmy Webber jwebber@usgs.gov How quickly would water-quality respond to changes in landuse? Ken Hyer kenhyer@usgs.gov Evidence of Septic Leachate Unresolved Questions…. Nitrate isotopes are suggestive of septic system effluent. What are the transport processes and fate of HF-183 within the watershed? John Jastram jdjastra@usgs.gov In general, nitrogen mass balances show septic system effluent to be a greater input than fertilizer leachate. JK Böhlke jkbohlke@usgs.gov Nitrogen concentrations and loads have increased at the Difficult Run downstream monitoring location1. Judy Denver jmdenver@usgs.gov Michael Langland Langland@usgs.gov 1Based on long-term WRTDS trends in total nitrogen and nitrate flux and concentration. http://cbrim.er.usgs.gov/index.html Preliminary Information-Subject to Revision. Not for Citation or Distribution

Metro Washington COG: SPARROW: Septic System Density Frederick County Montgomery County Loudoun County Prince George County D.C. Fairfax County Prince William County Septic System Density Low High Difficult Run Watershed Charles County Hyer and others, 2016