nitrate distribution, fate and transport in helena area waters james swierc, pg lewis & clark...
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Nitrate Distribution, Fate and Transport in Helena Area Waters
James Swierc, PGLewis & Clark Water Quality Protection DistrictLewis & Clark County, MT
April 22, 2014
Background• Helena Valley – SW Montana
– “Typical” Western Montana Valley• Alluvial Aquifer in Valley bounded by Bedrock/Tertiary
Basin Fill• River/Stream – Aquifer connections
– Losing Streams at Upgradient Valley Margins– Gaining Streams at Downgradient Margins
• Irrigation Canals
– Local Water Issues – Nitrate Related• Ground (Drinking) Water Quality
– Public Water Supplies vs Private Wells
• Wastewater treatment/management– Sewered Areas vs Septic Systems
• Concerns over Nitrate Contamination– USGS Studies 1973, 1980, 1992, 2000– County – Septic Maintenance District
• Recent Studies: TMDL 319, MBMG– Water Quality Map (Major Ion Types)– Isotopes (Nitrogen & Oxygen of Nitrate)– Drain Assessment & Cl/Br Ratios
• LCWQPD Monitoring Well Data (2009-2012)
• Residential Areas with Reported Problems (limited data)
• “Background”– Streams
• Recharge Areas < 1 mg/L
– Ground Water • Undefined, < 2 mg/L
• Sources?– Agriculture vs Septics– Differentiation Methods
• Nitrate Isotopes• Cl/Br Ratios
Nitrate in Ground Water
Helena Valley Hydrogeology• Aquifer - Unconsolidated Alluvium
– Clay lenses towards central valley– Vertical upward gradient
• Ground Water Flow– Shallow - Towards Lake Helena– Unconfined at valley margins– Upwelling in central valley
• Artesian flowing wells• Vertical Upward Gradient
– Gaining streams in central valley• Recharge
– Stream loss at valley margins– precipitation, irrigation loss– Bedrock Aquifer discharge in
subsurface to Alluvial Aquifer• Helena Valley Irrigation Canal
– Missouri River Water into Basin– Distribution Laterals/Drains
• Lake Helena– Discharge point for surface and
ground waterWater Surface Map from Briar & Madison (1992)
Recharge to Aquifer from Stream Loss
Recharge to Aquifer from Precipitation
Recharge from Irrigation Waters
Nitrate Isotopes• Nitrate Isotopes– Nitrogen– Oxygen
• Tracking Nitrate Recharge Sources
• Denitrification Pathway– “Lighter” atoms
denitrify first– Microbially
mediated
From Kendall (1998)
All Helena Area Nitrate Isotope Data
Nitrate Isotope Sampling Locations• Datasets– USGS, 2000
(Not Shown)• Bedrock Locations
– MBMG GWIP Studies (2011)
– LCWQPD Studies (2011, 2012)
Nitrate Isotope Sampling Results• Datasets– LCWQPD Studies
(2011, 2012)– No long decay series…
Nitrate Isotope Sampling Results• Sources
– “Old” Problem near Helena; Fairgrounds
– Fertilizer in Central Valley– Remaining Data
“clustered”
Chloride/Bromide Ratio
• Cl/Br ratio – premise, Cl from anthropogenic uses discharged to septic system drainfield
• Bromine stable/constant for “background”• Increase in nitrates associated with increase in
chloride– Nitrate can degrade, leaving elevated chloride
• Problem for Helena Valley – different recharge sources/ hydrologic areas
Ground Water Cl/Br Results• Poor Correlation
at Valley Scale– Inconclusive
Results• Look at Drains
Drain System – Central Valley• Irrigation
System– Main HVID
Canal– Distribution
Laterals– Ditches/Return
Flow Laterals– Tile Drains
• Samples Ground Water from top of water table
Drain Data – West Valley• D2-4
– Drains Residential and Agricultural Areas
– Nitrate decreases in summer, increase after irrigation season
– Cl/Br Ratio varies, 164-500
Drain Data – Southwest• D3-2– Drains Residential and
Agricultural Areas– Nitrate “stable”– Cl/Br Ratio varies, 205-
517
Drain Data – Northwest
• D2.2-1– Drains Residential and Agricultural
Areas– Nitrate increases in summer– Cl/Br Ratio varies, 182-420
• D2.2-5– Drains Agriculture Area– Nitrate increases post-irrigation– Cl/Br Ratio varies, 111-535
Drain Data – North
• D1-1– Drains Residential and Agricultural
Areas– Nitrate increases in summer– Cl/Br Ratio varies, 146-543
• D0-1– Drains Agriculture Area– Nitrate increases post-irrigation– Cl/Br Ratio varies, 170-792
Drain Data – East Valley• D7-1– Drains Primarily
Agricultural Areas– Nitrate low, “stable”– Cl/Br Ratio varies, 145-375
Drain Data – Observations• Nitrates– Some Variability pre/post
irrigation season• Chloride / Bromide – Chloride – generally stable– Bromide – widely variable
• Low/Trace Levels – Lab quantification issues• Different Sources for Br
• Need to characterize recharge sources as baseline for comparison
Chloride (& Bromide) Sources?• From De-icing Solutions for Roads (MgCl, NaCl, etc.)– Highest Chloride concentrations adjacent to roads
• From Fertilizers?– Saffigna & Keeney, 1977 Ground Water, V. 15, No. 2• Wisconsin Agricultural Areas, NO3/CL Ratio constant• Noted FERTILIZERs as source for Nitrate & Chloride
– Potassium Chloride used for Potassium source
– See Nitrate-Chloride Linear Relationship at valley residential wells with Nitrate Problems, by agricultural fields
Fate & TransportVertical Upward Gradient
• East Helena area well cluster (trio)– Well 1, TD 103’– Well 2, TD 128’– Well 3, TD 169’
• 4 feet vertical head upward over 60 feet
Horizontal vs Vertical flow rates• Vertical gradient order of magnitude
higher than horizontal gradient– Hydrograph shows similar response pattern
so affected by same surficial recharge sources– Deep water recharge source, vertical flow
retarded by finer-grained layers• Result – keeps surface contaminants near
surface, even if drawn down by well pumping
Gradients are real, aquifer hydraulic properties are estimated to illustrate concept
High K
High K
Lower K Aquitard
flowpath
flowpath
What does clustering ofIsotope data here mean?
Mixing of different sources?Rapid Denitrification?
Fate and Transport Summary• Nitrates released to top of aquifer from surface– Fertilizer AND Septic System sources
• Central Valley – area near Drains– Denitrification occurs, low Nitrate and low
dissolved oxygen levels in shallow wells– Drains flush top of water table into ditches
• Vertical upward gradient– Dilution of nitrate waters
• High Chloride, Low NO3
– Denitrification, dilution– Added chloride
Questions/Discussion?
Helena Valley from Divide (view East)
Note – work is ongoing, drain study continues through 2014James Swierc, PG [email protected] Project Report(s), Poster(s) and more information available at http://www.lccountymt.gov/health/water.html