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Edge-of-field Water Quality Monitoring:
The First Step in Agricultural Practice Assessment
in the Field to Lake Continuum
USDA-ARS
Soil Drainage Research Unit
Columbus, OH
Nutrient Management and Edge of Field Monitoring; Memphis, TN; Dec 3, 2015
Edge-of-field research
40 fields (20 paired fields)
representative of Ohio crop
production agriculture
Surface runoff and tile
discharge measurements
Using a before-after control-
impact study design
Edge-of-field instrumentation
H-flumes for surface runoff
Thel-mar compound weirs and Isco
area velocity sensors for tile
Automated samplers
Year round sampling
4R Research Fund
USDA-ARS: USDA-Agriculture Research Service
CEAP: Conservation Effects Assessment Project
EPA: DW-12-92342501-0
Ohio Agri-Businesses
Ohio Corn and Wheat Growers
Funding Sources: CIG: 69-3A75-12-231 (OSU)
CIG: 69-3A75-13-216 (Heidelberg University)
MRBI: Mississippi River Basin Initiative
The Nature Conservancy
Becks Hybrids/Ohio State University
Ohio Soybean Association
Eventmeanconcentration(mg/L)
0.0
0.5
1.0
1.5
2.0
2.5
surface
tile
DRP TP
Phosphorus Concentrations
AnnualDRPloading(kg/ha/yr)
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
1.6
1.8
2.0
2.2
2.4
2.6
2.8
3.0
3.2
3.4
Tile
Surface
P Tack Force recommendation
AnnualTPloading(kg/ha/yr)
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
1.6
1.8
2.0
2.2
2.4
2.6
2.8
3.0
3.2
3.4
3.6
3.8
4.0
A B C D E F G H I J K L M N O P Q
4R Preliminary Findings
Rate Timing
PlacementSource
Fertilizer Rate
Discharge:Precipitation Ratio
0.0 0.2 0.4 0.6 0.8 1.0
Mehlich3STP(ppm)
0
20
40
60
80
100
120
140
160
180
300
400
500
<0.3 kg/ha
>0.3 kg/ha
tri-state critical level
tri-state maintencance level
Fertilizer Rate
3/1/15 4/1/15 5/1/15 6/1/15 7/1/15 8/1/15
0
500
1000
1500
2000
2500
DRP(mg/L)
0.0
0.1
0.2
0.3
0.4
Discharge(m3/s)
0
500
1000
1500
2000
2500
NO3+NO2-N(mg/L)
0
5
10
15
20
discharge
Data from Heidelberg Univ.
Laura Johnson
Timing
Time of Application
• Greatest potential for
surface and tile losses
occurs with fall and
winter application
• Applying P in spring or
after wheat harvest
seems to minimize
surface and tile losses
Mehlich3STP(ppm)
0
20
40
60
80
100
120
140
160
180
Time of application
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Jan
0
20
40
60
80
100
120
140
160
180
Surface Losses
Tile Losses
0.56 kg/ha 0.50 kg/ha
0.04 kg/ha
0.50 kg/ha0.06 kg/ha
Days since application
0 20 40 60 80 100 120 140
DRPconcentration(mg/L)
0
5
10
15
20
1/3/12: 225# MAP
11/13/13: 193# MAP
Placement
Broadcast variable rate application on May 6, 2014
4-part stratification
• Stratification evident even in the top 1” of soil
(ANOVA, P<0.001, n=232)
• Although the degree of stratification varied some…
• 85% of the samples had some degree of stratification
M3P (ppm)
0 25 50 75 100 125 300
Coredepth(inches)
0-1
1-2
2-5
5-8
Median
60
49
34
26
54.5
Source: Johnson and Baker, Heidelberg University
0
20
40
60
80
100
120
140
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1.40
0 10 20 30
0.00
1.00
2.00
3.00
4.00
5.00
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
0 20 40 60 80
Discharge
Preferential flow
DRP
Discharge(mm) Before P application & tillage
(April 28th)
DRP(mg/L)
TD1 TD2
0
20
40
60
80
100
120
140
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
0 20 40 60 80
Discharge
DRP
DRP(g/ha)
After P application & tillage
(May 12th)
0.0
1.0
2.0
3.0
4.0
5.0
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1.40
0 10 20 30
0.0
1.0
2.0
3.0
4.0
5.0
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1.40
0 10 20 30
TD1 TD2
0
20
40
60
80
100
120
140
0
0.2
0.4
0.6
0.8
1
1.2
1.4
0 20 40 60 80
0.0
1.0
2.0
3.0
4.0
5.0
0
0.2
0.4
0.6
0.8
1
1.2
1.4
0 20 40 60 80
0
20
40
60
80
100
120
140
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1.40
0 10 20 30
Avg DRP (mg/L) =0.08 Avg DRP (mg/L) =0.08 Avg DRP (mg/L) =0.58 Avg DRP (mg/L) =2.12
DRP Load (g/ha) = 12.6 DRP Load (g/ha) = 12.4 DRP Load (g/ha) = 18.2 DRP Load (g/ha) = 129.6
DRP(mg/L)DRP(g/ha)
Fertilizer Source
DRPLoad(kg/ha)
0.0
1.0
2.0
3.0
5.0
5.5
6.0
DRPNO3-NLoad(kg/ha)
0
10
20
30
40
50
60
70
80
90
100
110
120
NO3-N
inorganic mixed organic
Fertilizer Source (chronic vs acute risk)
Structural and Other Management
Gypsum
Cover Crops
Drainage Water Mgt
Drainage Water Management
Quantify tile discharge and nutrient dynamics before and
after implementation of drainage water management
Drainage area:
B2 = 14 ha; B4 = 15 ha
Tile depth:
0.9 - 1.0 m
Soil type:
Bennington silt loam
Pewamo clay loam
Soil test P concentration:
60 mg/kg (0-20 cm)
2006-2008: Both sites were free draining
2009-2012: DWM was implemented at B4
B2
B4
0 90 180 m
Ditch
Legend
Tile outlet
Drainage area
Upper Big
Walnut Creek
Watershed
Ohio
DWM - Case Study
0.00
0.05
0.10
0.15
0.20
0.25
0.30
2005.520062006.520072007.520082008.520092009.520102010.520112011.520122012.5
MeanDRPconc.(mgL-1)
Year
B2
B4
0.00
0.30
0.60
0.90
1.20
2006 2007 2008 2009 2010 2011 2012
Year
AnnualDRPload(kg/ha)DWM did not significantly affect DRP concentration
65-74% reduction in annual DRP load with DWM
DWM - Case Study
Gypsum Treatment
• Mercer County Ohio
• >400 ppm Mehlich 3 in the top 8 inches
• Corn-soybean rotation in a no-till
system
• Blount soil; randomly tiled
• June 2011 to October 2014
• October 3 of 2013, 1-ton of gypsum was
applied to treatment area
• Baseline period (86 rainfall events )
• Treatment period (34 rainfall events)
0.0 0.5 1.0 1.5 2.0 2.50.0 0.5 1.0 1.5 2.0 2.5
DRPconcentration(mg/L)
0.0
0.5
1.0
1.5
2.0
2.5
0.0 0.1 0.2 0.3 0.4 0.5
DRPload(kg/ha)
0.0
0.1
0.2
0.3
0.4
0.5
0.0 0.1 0.2 0.3 0.4 0.5
0.0 1.0 2.0 3.0 4.0 5.0
TPconcentration(mg/L)
0.0
1.0
2.0
3.0
4.0
5.0
kn4-tp-cnc-c vs kn1-tp-cnc-c
kn4-tp-cnc-t vs kn1-tp-cnc-t
xp vs surf TP conc c
xp vs surf TP conc t
0.0 1.0 2.0 3.0 4.0 5.0 0.0 1.0 2.0 3.0 4.0 5.0
0.0 0.1 0.2 0.3 0.4 0.5
TPload(kg/ha)
0.0
0.1
0.2
0.3
0.4
0.5
kn4-tp-ld-c vs kn1-tp-ld-c
kn4-tp-ld-t vs kn1-tp-ld-t
xp vs surf TP load c
xp vs surf TP load t
0.0 0.1 0.2 0.3 0.4 0.5 0.0 0.1 0.2 0.3 0.4 0.5
Treatmentfield
0.0 0.5 1.0 1.5 2.0 2.5
0.0 0.1 0.2 0.3 0.4 0.5
Control field
Surface Tile Combined
Gypsum effect on
surface drainage and P
• Significant increase in tile
drainage discharge
• Significant decrease in
DRP and TP event
concentrations
• Significant decrease in
DRP and TP loading
Cover Crops (what is the resource concern?)
Positives
Increase infiltration
Reduce erosion
Improve soil health
Increase OM
Negatives
Increase DRP surface losses following freeze thaw cycles
(Miller et al., 1994; Bechmann, et al 2005; Cavadini, 2013)
Leachate concentrations of P differ depending on catch
crop and soil (Riddle and Bergstrom 2013; Liu et al 2014)
P concentration around tuber of tillage radish
significantly greater than surrounding soil (White and
Weil, 2011)
 P & N losses are impacted by:
 STP
 Connectivity to water
 Placement of P fertilizer
 Timing of fertilizer
 Rate of fertilizer
 Source and legacy effects
Conclusions
 Practices that will address excess P
 Adherence to tri-state
recommendations or lesser application
 Increased organic matter/carbon, cover
crops, no-till, etc
 Avoiding fall and winter applications
 Accounting for manure in nutrient
calculations
 Subsurface placement of nutrients
(banding or injecting)
 Disconnecting hydrologic pathways
(DWM, blind inlets, linear wetlands,
water storage/increased OM)
Conclusions
 Cover crops – correct cover crop or
blend is critical
 Gypsum –water quality benefits are
minimal but significant
Collaborators, Partners, and Outreach
• SWCDs
• OSU Extension and OARDC
• Agri-businesses (Commodities, retailers)
• Ohio Farm Bureau
• TNC
• State agencies (ODNR, ODA, OEPA)
• NRCS (local, state, and federal)
• Crop consultants
• Producers/landowners
• Lake Improvement
• Other ARS locations
• NOAA and NWS
• Great Lakes Commission
• Great Lakes Protection Fund
• Greenleaf Advisors
• Multiple University Partners
• (OSU, Utoledo, Oklahoma State
Univ., Univ. of Waterloo, NC State,
Purdue Univ.)
• 4R Research Fund (IPNI, TFI)
• NCWQR at Heidelberg
• Agriculture and Agri-Food Canada
• Consultants (CCAs, Limno-Tech)
• USGS
• Private Industry (Agri-Drain, ADS,
Hancor, John Deere, The Andersons,
Becks Hybrids)
• Gypsoil
Contact Information
Kevin King
590 Woody Hayes Dr.
Columbus, OH 43210
kevin.king@ars.usda.gov
Technical Support Staff
Mark Day, Eric Fischer, Phil
Levison, Paxton MacDonald,
Katie Rumora, Marie
Schrecengost, Jed Stinner

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King - Edge of Field Water Quality Monitoring

  • 1. Edge-of-field Water Quality Monitoring: The First Step in Agricultural Practice Assessment in the Field to Lake Continuum USDA-ARS Soil Drainage Research Unit Columbus, OH Nutrient Management and Edge of Field Monitoring; Memphis, TN; Dec 3, 2015
  • 2. Edge-of-field research 40 fields (20 paired fields) representative of Ohio crop production agriculture Surface runoff and tile discharge measurements Using a before-after control- impact study design
  • 3. Edge-of-field instrumentation H-flumes for surface runoff Thel-mar compound weirs and Isco area velocity sensors for tile Automated samplers Year round sampling
  • 4. 4R Research Fund USDA-ARS: USDA-Agriculture Research Service CEAP: Conservation Effects Assessment Project EPA: DW-12-92342501-0 Ohio Agri-Businesses Ohio Corn and Wheat Growers Funding Sources: CIG: 69-3A75-12-231 (OSU) CIG: 69-3A75-13-216 (Heidelberg University) MRBI: Mississippi River Basin Initiative The Nature Conservancy Becks Hybrids/Ohio State University Ohio Soybean Association
  • 6. AnnualDRPloading(kg/ha/yr) 0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 1.6 1.8 2.0 2.2 2.4 2.6 2.8 3.0 3.2 3.4 Tile Surface P Tack Force recommendation AnnualTPloading(kg/ha/yr) 0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 1.6 1.8 2.0 2.2 2.4 2.6 2.8 3.0 3.2 3.4 3.6 3.8 4.0 A B C D E F G H I J K L M N O P Q
  • 7. 4R Preliminary Findings Rate Timing PlacementSource
  • 9. Discharge:Precipitation Ratio 0.0 0.2 0.4 0.6 0.8 1.0 Mehlich3STP(ppm) 0 20 40 60 80 100 120 140 160 180 300 400 500 <0.3 kg/ha >0.3 kg/ha tri-state critical level tri-state maintencance level Fertilizer Rate
  • 10. 3/1/15 4/1/15 5/1/15 6/1/15 7/1/15 8/1/15 0 500 1000 1500 2000 2500 DRP(mg/L) 0.0 0.1 0.2 0.3 0.4 Discharge(m3/s) 0 500 1000 1500 2000 2500 NO3+NO2-N(mg/L) 0 5 10 15 20 discharge Data from Heidelberg Univ. Laura Johnson
  • 12. Time of Application • Greatest potential for surface and tile losses occurs with fall and winter application • Applying P in spring or after wheat harvest seems to minimize surface and tile losses Mehlich3STP(ppm) 0 20 40 60 80 100 120 140 160 180 Time of application Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Jan 0 20 40 60 80 100 120 140 160 180 Surface Losses Tile Losses 0.56 kg/ha 0.50 kg/ha 0.04 kg/ha 0.50 kg/ha0.06 kg/ha
  • 13. Days since application 0 20 40 60 80 100 120 140 DRPconcentration(mg/L) 0 5 10 15 20 1/3/12: 225# MAP 11/13/13: 193# MAP
  • 15. Broadcast variable rate application on May 6, 2014
  • 16. 4-part stratification • Stratification evident even in the top 1” of soil (ANOVA, P<0.001, n=232) • Although the degree of stratification varied some… • 85% of the samples had some degree of stratification M3P (ppm) 0 25 50 75 100 125 300 Coredepth(inches) 0-1 1-2 2-5 5-8 Median 60 49 34 26 54.5 Source: Johnson and Baker, Heidelberg University
  • 17. 0 20 40 60 80 100 120 140 0.00 0.20 0.40 0.60 0.80 1.00 1.20 1.40 0 10 20 30 0.00 1.00 2.00 3.00 4.00 5.00 0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 0 20 40 60 80 Discharge Preferential flow DRP Discharge(mm) Before P application & tillage (April 28th) DRP(mg/L) TD1 TD2 0 20 40 60 80 100 120 140 0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 0 20 40 60 80 Discharge DRP DRP(g/ha) After P application & tillage (May 12th) 0.0 1.0 2.0 3.0 4.0 5.0 0.00 0.20 0.40 0.60 0.80 1.00 1.20 1.40 0 10 20 30 0.0 1.0 2.0 3.0 4.0 5.0 0.00 0.20 0.40 0.60 0.80 1.00 1.20 1.40 0 10 20 30 TD1 TD2 0 20 40 60 80 100 120 140 0 0.2 0.4 0.6 0.8 1 1.2 1.4 0 20 40 60 80 0.0 1.0 2.0 3.0 4.0 5.0 0 0.2 0.4 0.6 0.8 1 1.2 1.4 0 20 40 60 80 0 20 40 60 80 100 120 140 0.00 0.20 0.40 0.60 0.80 1.00 1.20 1.40 0 10 20 30 Avg DRP (mg/L) =0.08 Avg DRP (mg/L) =0.08 Avg DRP (mg/L) =0.58 Avg DRP (mg/L) =2.12 DRP Load (g/ha) = 12.6 DRP Load (g/ha) = 12.4 DRP Load (g/ha) = 18.2 DRP Load (g/ha) = 129.6 DRP(mg/L)DRP(g/ha)
  • 20. Structural and Other Management Gypsum Cover Crops Drainage Water Mgt
  • 21. Drainage Water Management Quantify tile discharge and nutrient dynamics before and after implementation of drainage water management
  • 22. Drainage area: B2 = 14 ha; B4 = 15 ha Tile depth: 0.9 - 1.0 m Soil type: Bennington silt loam Pewamo clay loam Soil test P concentration: 60 mg/kg (0-20 cm) 2006-2008: Both sites were free draining 2009-2012: DWM was implemented at B4 B2 B4 0 90 180 m Ditch Legend Tile outlet Drainage area Upper Big Walnut Creek Watershed Ohio DWM - Case Study
  • 23. 0.00 0.05 0.10 0.15 0.20 0.25 0.30 2005.520062006.520072007.520082008.520092009.520102010.520112011.520122012.5 MeanDRPconc.(mgL-1) Year B2 B4 0.00 0.30 0.60 0.90 1.20 2006 2007 2008 2009 2010 2011 2012 Year AnnualDRPload(kg/ha)DWM did not significantly affect DRP concentration 65-74% reduction in annual DRP load with DWM DWM - Case Study
  • 24. Gypsum Treatment • Mercer County Ohio • >400 ppm Mehlich 3 in the top 8 inches • Corn-soybean rotation in a no-till system • Blount soil; randomly tiled • June 2011 to October 2014 • October 3 of 2013, 1-ton of gypsum was applied to treatment area • Baseline period (86 rainfall events ) • Treatment period (34 rainfall events)
  • 25. 0.0 0.5 1.0 1.5 2.0 2.50.0 0.5 1.0 1.5 2.0 2.5 DRPconcentration(mg/L) 0.0 0.5 1.0 1.5 2.0 2.5 0.0 0.1 0.2 0.3 0.4 0.5 DRPload(kg/ha) 0.0 0.1 0.2 0.3 0.4 0.5 0.0 0.1 0.2 0.3 0.4 0.5 0.0 1.0 2.0 3.0 4.0 5.0 TPconcentration(mg/L) 0.0 1.0 2.0 3.0 4.0 5.0 kn4-tp-cnc-c vs kn1-tp-cnc-c kn4-tp-cnc-t vs kn1-tp-cnc-t xp vs surf TP conc c xp vs surf TP conc t 0.0 1.0 2.0 3.0 4.0 5.0 0.0 1.0 2.0 3.0 4.0 5.0 0.0 0.1 0.2 0.3 0.4 0.5 TPload(kg/ha) 0.0 0.1 0.2 0.3 0.4 0.5 kn4-tp-ld-c vs kn1-tp-ld-c kn4-tp-ld-t vs kn1-tp-ld-t xp vs surf TP load c xp vs surf TP load t 0.0 0.1 0.2 0.3 0.4 0.5 0.0 0.1 0.2 0.3 0.4 0.5 Treatmentfield 0.0 0.5 1.0 1.5 2.0 2.5 0.0 0.1 0.2 0.3 0.4 0.5 Control field Surface Tile Combined Gypsum effect on surface drainage and P • Significant increase in tile drainage discharge • Significant decrease in DRP and TP event concentrations • Significant decrease in DRP and TP loading
  • 26. Cover Crops (what is the resource concern?) Positives Increase infiltration Reduce erosion Improve soil health Increase OM Negatives Increase DRP surface losses following freeze thaw cycles (Miller et al., 1994; Bechmann, et al 2005; Cavadini, 2013) Leachate concentrations of P differ depending on catch crop and soil (Riddle and Bergstrom 2013; Liu et al 2014) P concentration around tuber of tillage radish significantly greater than surrounding soil (White and Weil, 2011)
  • 27.  P & N losses are impacted by:  STP  Connectivity to water  Placement of P fertilizer  Timing of fertilizer  Rate of fertilizer  Source and legacy effects Conclusions
  • 28.  Practices that will address excess P  Adherence to tri-state recommendations or lesser application  Increased organic matter/carbon, cover crops, no-till, etc  Avoiding fall and winter applications  Accounting for manure in nutrient calculations  Subsurface placement of nutrients (banding or injecting)  Disconnecting hydrologic pathways (DWM, blind inlets, linear wetlands, water storage/increased OM) Conclusions  Cover crops – correct cover crop or blend is critical  Gypsum –water quality benefits are minimal but significant
  • 29. Collaborators, Partners, and Outreach • SWCDs • OSU Extension and OARDC • Agri-businesses (Commodities, retailers) • Ohio Farm Bureau • TNC • State agencies (ODNR, ODA, OEPA) • NRCS (local, state, and federal) • Crop consultants • Producers/landowners • Lake Improvement • Other ARS locations • NOAA and NWS • Great Lakes Commission • Great Lakes Protection Fund • Greenleaf Advisors • Multiple University Partners • (OSU, Utoledo, Oklahoma State Univ., Univ. of Waterloo, NC State, Purdue Univ.) • 4R Research Fund (IPNI, TFI) • NCWQR at Heidelberg • Agriculture and Agri-Food Canada • Consultants (CCAs, Limno-Tech) • USGS • Private Industry (Agri-Drain, ADS, Hancor, John Deere, The Andersons, Becks Hybrids) • Gypsoil
  • 30. Contact Information Kevin King 590 Woody Hayes Dr. Columbus, OH 43210 kevin.king@ars.usda.gov Technical Support Staff Mark Day, Eric Fischer, Phil Levison, Paxton MacDonald, Katie Rumora, Marie Schrecengost, Jed Stinner