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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

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Page 1: King - Edge of Field Water Quality Monitoring

Edge-of-field Water Quality Monitoring: The First Step in Agricultural Practice Assessment

in the Field to Lake Continuum

USDA-ARSSoil Drainage Research Unit

Columbus, OH

Nutrient Management and Edge of Field Monitoring; Memphis, TN; Dec 3, 2015

Page 2: King - Edge of Field Water Quality Monitoring

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

Page 3: King - Edge of Field Water Quality Monitoring

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

Page 4: King - Edge of Field Water Quality Monitoring

4R Research FundUSDA-ARS: USDA-Agriculture Research ServiceCEAP: Conservation Effects Assessment ProjectEPA: DW-12-92342501-0Ohio Agri-BusinessesOhio Corn and Wheat Growers

Funding Sources: CIG: 69-3A75-12-231 (OSU)CIG: 69-3A75-13-216 (Heidelberg University)MRBI: Mississippi River Basin InitiativeThe Nature ConservancyBecks Hybrids/Ohio State UniversityOhio Soybean Association

Page 5: King - Edge of Field Water Quality Monitoring

Ev

en

t m

ea

n c

on

ce

ntr

ati

on

(m

g/L

)

0.0

0.5

1.0

1.5

2.0

2.5surface

tile

DRP TP

Phosphorus Concentrations

Page 6: King - Edge of Field Water Quality Monitoring

An

nu

al

DR

P l

oa

din

g (

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

TileSurfaceP Tack Force recommendation

An

nu

al

TP

lo

ad

ing

(k

g/h

a/y

r)

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

Page 7: King - Edge of Field Water Quality Monitoring

4R Preliminary FindingsRate Timing

PlacementSource

Page 8: King - Edge of Field Water Quality Monitoring

Fertilizer Rate

Page 9: King - Edge of Field Water Quality Monitoring

Discharge:Precipitation Ratio

0.0 0.2 0.4 0.6 0.8 1.0

Me

hli

ch

3 S

TP

(p

pm

)

0

20

40

60

80

100

120

140

160

180

300

400

500

<0.3 kg/ha>0.3 kg/hatri-state critical leveltri-state maintencance level

Fertilizer Rate

Page 10: King - Edge of Field Water Quality Monitoring

3/1/15 4/1/15 5/1/15 6/1/15 7/1/15 8/1/15

0

500

1000

1500

2000

2500

DR

P (

mg

/L)

0.0

0.1

0.2

0.3

0.4

Dis

ch

arg

e (

m3

/s)

0

500

1000

1500

2000

2500

NO

3 +

NO

2 -

N (

mg

/L)

0

5

10

15

20

discharge

Data from Heidelberg Univ.Laura Johnson

Page 11: King - Edge of Field Water Quality Monitoring

Timing

Page 12: King - Edge of Field Water Quality Monitoring

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

Meh

lich

3 S

TP

(p

pm

)

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/ha0.04 kg/ha

0.50 kg/ha0.06 kg/ha

Page 13: King - Edge of Field Water Quality Monitoring

Days since application

0 20 40 60 80 100 120 140

DR

P c

on

cen

trati

on

(m

g/L

)

0

5

10

15

20

1/3/12: 225# MAP11/13/13: 193# MAP

Page 14: King - Edge of Field Water Quality Monitoring

Placement

Page 15: King - Edge of Field Water Quality Monitoring

Broadcast variable rate application on May 6, 2014

Page 16: King - Edge of Field Water Quality Monitoring

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

Co

re d

ep

th (

inch

es)

0-1

1-2

2-5

5-8

Median

60

49

34

26

54.5

Source: Johnson and Baker, Heidelberg University

Page 17: King - Edge of Field Water Quality Monitoring

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

Dis

ch

arg

e (

mm

)Before P application & tillage

(April 28th)

DR

P (

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

DR

P (

g/h

a)

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

DR

P (

mg

/L)

DR

P (

g/h

a)

Page 18: King - Edge of Field Water Quality Monitoring

Fertilizer Source

Page 19: King - Edge of Field Water Quality Monitoring

DR

P L

oad

(k

g/h

a)

0.0

1.0

2.0

3.0

5.05.56.0

DRPN

O3

-N L

oa

d (

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)

Page 20: King - Edge of Field Water Quality Monitoring

Structural and Other Management

Gypsum

Cover Crops

Drainage Water Mgt

Page 21: King - Edge of Field Water Quality Monitoring

Drainage Water Management

Quantify tile discharge and nutrient dynamics before and

after implementation of drainage water management

Page 22: King - Edge of Field Water Quality Monitoring

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

Page 23: King - Edge of Field Water Quality Monitoring

0.00

0.05

0.10

0.15

0.20

0.25

0.30

2005.520062006.520072007.520082008.520092009.520102010.520112011.520122012.5

Mean

DR

P c

on

c. (m

g L

-1)

Year

B2

B4

0.00

0.30

0.60

0.90

1.20

2006 2007 2008 2009 2010 2011 2012

Year

An

nu

al

DR

P l

oad

(kg

/ha)

DWM did not significantly affect DRP concentration

65-74% reduction in annual DRP load with DWM

DWM - Case Study

Page 24: King - Edge of Field Water Quality Monitoring

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)

Page 25: King - Edge of Field Water Quality Monitoring

0.0 0.5 1.0 1.5 2.0 2.50.0 0.5 1.0 1.5 2.0 2.5

DR

P c

on

ce

ntr

ati

on

(m

g/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

DR

P lo

ad

(k

g/h

a)

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

TP

co

nc

en

tra

tio

n (

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

TP

lo

ad

(k

g/h

a)

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

Tre

atm

en

t fi

eld

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

Page 26: King - Edge of Field Water Quality Monitoring

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)

Page 27: King - Edge of Field Water Quality Monitoring

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

Page 28: King - Edge of Field Water Quality Monitoring

Practices that will address excess P

Adherence to tri-staterecommendations 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

Page 29: King - Edge of Field Water Quality Monitoring

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

Page 30: King - Edge of Field Water Quality Monitoring

Contact Information

Kevin King

590 Woody Hayes Dr.

Columbus, OH 43210

[email protected]

Technical Support StaffMark Day, Eric Fischer, Phil Levison, Paxton MacDonald, Katie Rumora, Marie Schrecengost, Jed Stinner