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On the Go Soil Sensing - Lecture Slides | AGEN 431, Exams of Engineering

Material Type: Exam; Professor: Adamchuk; Class: Site-specific Crop Management; Subject: Agricultural Engineering ; University: University of Nebraska - Lincoln; Term: Fall 2008;

Typology: Exams

Pre 2010

Uploaded on 08/26/2009

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On
On-
-the
the-
-Go Soil Sensing
Go Soil Sensing
AGRO/MSYM/AGEN 431
AGRO/MSYM/AGEN 431
Viacheslav I. Adamchuk
Viacheslav I. Adamchuk
Biological Systems Engineering Department
Biological Systems Engineering Department
University of Nebraska
University of Nebraska-
-Lincoln
Lincoln
October 7, 2008
October 7, 2008
Problem Statement
Problem Statement
The assessment of soil variability is one of the most
important steps in site-specific management
Conventional means to attain soil variability data are
incapable of accurately identifying spatial
inconsistency within a production field at an
economically feasible cost
There is a need to develop equipment for mapping
soil attributes on-the-go
Sensor Use Approaches
Sensor Use Approaches
Map-Based
Approach
Integrated Approach
(Real-Time with Supplemental Base Map)
Real-Time
Application
Nature of Proximity Sensing
Nature of Proximity Sensing
Listen
Taste
Smell
Touch
Look
On
On-
-the
the-
-go Soil Sensors
go Soil Sensors
Electrical and
Electromagnetic
Acoustic
Mechanical Electrochemical
H+
H+H+
H+
H+
Pneumatic
Optical and
Radiometric
Electrical end Electromagnetic Sensors
Electrical end Electromagnetic Sensors
Electrical Conductivity/Resistivity Sensors
ECa
EC1
EC2
EC3
EC4
EC5
Soil Soil
Galvanic Contact
Resistivity Method
Electromagnetic
Induction Method Capacitively-Coupled
Resistivity Method
Soil type/texture
Salinity
Water content
Organic matter content
Depth variability
Soil pH / nitrate content
Volumetric water content
Soil type/structure
Salinity
Dielectric
Sensors Magnetic
Sensors
Subsurface
soil impurities
Iron
pf3
pf4
pf5
pf8
pf9
pfa

Partial preview of the text

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On- On-thethe--Go Soil SensingGo Soil Sensing

AGRO/MSYM/AGEN 431AGRO/MSYM/AGEN 431

Viacheslav I. Adamchuk Viacheslav I. Adamchuk

Biological Systems Engineering DepartmentBiological Systems Engineering Department

University of NebraskaUniversity of Nebraska--LincolnLincoln

October 7, 2008October 7, 2008

Problem Statement Problem Statement

  • The assessment of soil variability is one of the most important steps in site-specific management
  • Conventional means to attain soil variability data are incapable of accurately identifying spatial inconsistency within a production field at an economically feasible cost
  • There is a need to develop equipment for mapping soil attributes on-the-go

Sensor Use ApproachesSensor Use Approaches

Map-Based Approach

Integrated Approach (Real-Time with Supplemental Base Map)

Real-Time Application

Nature of Proximity SensingNature of Proximity Sensing

Listen

Taste

Smell

Touch

Look

OnOn--thethe--go Soil Sensorsgo Soil Sensors

Electrical and

Electromagnetic

Acoustic

Mechanical Electrochemical

H + H +^ H +

H + H +

Pneumatic

Optical and

Radiometric

Electrical end Electromagnetic Sensors Electrical end Electromagnetic Sensors

Electrical Conductivity/Resistivity Sensors

ECa

EC (^1) EC (^2) EC (^4) EC (^3)

EC (^5)

Soil Soil

Galvanic Contact Resistivity Method

Electromagnetic Induction Method

Capacitively-Coupled Resistivity Method

  • Soil type/texture
  • Salinity
  • Water content
  • Organic matter content
  • Depth variability
  • Soil pH / nitrate content
    • Volumetric water content
    • Soil type/structure
    • Salinity

Dielectric Sensors

Magnetic Sensors

  • Subsurface soil impurities
  • Iron

Galvanic Contact Resistivity MethodGalvanic Contact Resistivity Method

I A U

NB M

Current flow

Equipotentials

Veris Technologies, Inc. (Salina, Kansas) http://www.veristech.com

Veris®^ 3100 and MSP (0.3 and 0.9 m)

Geocarta (Paris, France) http://www.geocarta.net

Geocarta ARP (0.5, 1, and 2 m)

Crop Tehchnologies, Inc. (Spring, Texas) http://www.soildoctor.com

Soil Doctor ®^ System (real-time approach)

Electromagnetic Induction Method Electromagnetic Induction Method

Receiver

Primary field Soil Eddy currents

Transmitter

Secondary field

Geonics Limited (Mississauga, Ontario) http://www.geonics.com

Geonics EM- horizontal – 0.75 m vertical – 1.5 m

Dualem, Inc. (Milton, Ontario) http://www.dualem.com

DUALEM – 1S co-planar – 0.4 m perpendicular – 0.95 m

CapacitivelyCapacitively--Coupled ResistivityCoupled Resistivity

MethodMethod

Capacitor analogue Metal shield as acapacitor plate

Soil as a capacitor plate

Insulation as dielectric material

Coaxial cable

Soil

Transmitter

Inner wire

Geometrics, Inc. (San Jose, California) http://www.geometrics.com

Geometrix OhmMapper TR

Example 1Example 1

Electrical Conductivity MapElectrical Conductivity Map

Improved Soil Type Separation

Soil Survey EC Map

Example 2Example 2

Electrical Conductivity Map Electrical Conductivity Map

EC Map

Low Yielding Area

High Yielding Area

Yield Map

Example 3Example 3

Electrical Conductivity Map Electrical Conductivity Map

Shallow EC Deep EC

Excessive manure application^ Area of excessive manure application

Shallow/Deep EC

VIS/NIR SpectrophotometerVIS/NIR Spectrophotometer

Predicted Carbon Measured Carbon Sapphire Window Veris Technologies, Inc. (Salina, Kansas) http://www.veristech.com

Traveling Spectrophotometer Traveling Spectrophotometer

CCD camera

Optical fiber for visible reflection

Soil flattener Soil surfaceillumination

Optical fibers for illumination

Penetrator tip

Shank NIR thermometer

Laser displacesensor Optical fiber for NIR reflection

Travel direction

Ground surface

Tokyo University of Agriculture and Technology (Tokyo, Japan) Load Cell EC Electrode

Mechanical Sensors Mechanical Sensors

Cantilever beam sensors

Direct load sensors

Single-tip horizontal sensors

Multiple-tip horizontal sensors

Vertically oscillating sensors

Vertically- operated cone penetrometers

Soil profile sensors

Tine-based sensors

Tip-based sensors

Soil strength sensors

  • Soil mechanical resistance
  • Soil compaction
  • Water content
  • Soil types
  • Depth of hard (plow) pan

Vertically actuated sensors

Bulk soil strength sensors

Draft and vertical force sensors

Strain Gauges

Soil Mechanical Resistance MappingSoil Mechanical Resistance Mapping

Tool Bar

Travel Direction

Purdue University (West Lafayette, Indiana)

Discrete Depth Profiling ToolsDiscrete Depth Profiling Tools

UC-Davis (Davis, California)

Three CuttingThree Cutting BladesBlades

UNL (Lincoln, Nebraska)

University of Missouri (Columbia, Missouri)

Load CellLoad Cell ArrayArray

ExampleExample

Soil Mechanical Resistance Map Soil Mechanical Resistance Map

Soil Mechanical Resistance Map (20-30 cm)

Yield Map

Compacted area Old roads

Integrated Soil Physical Properties Integrated Soil Physical Properties

Mapping SystemMapping System

Two wavelengths soil reflectance sensor

Soil mechanical resistance profiler with an array of strain gage bridges

Capacitor-based sensor

UNL

(Lincoln, Nebraska)

Vertical Blade with Strain Gage ArrayVertical Blade with Strain Gage Array

UNL (Lincoln, Nebraska)

Discrete Model

Soil surface

Travel direction

Strain gages

Polynomial Model

Apparent soil surface

Apparent Soil Profiles Apparent Soil Profiles

Plot B (disked)

0

5

10

15

20

25

-0.8 -0.4 0.0 0.4 0.8 1.2 1.6 2.0 2.4 2.

Soil mechanical resistance, MPa

Relative depth, cmISPPMS - pass 1Cone - pass 1 ISPPMS - pass 2 Cone - pass 2

Plot D (chiselled and disked)

0

5

10

15

20

25

-0.8 -0.4 0.0 0.4 0.8 1.2 1.6 2.0 2.4 2.

Soil mechanical resistance, MPa

Relative depth, cm

ISPPMS - pass 1 Cone - pass 1 ISPPMS - pass 2 Cone - pass 2

Integrated Load ComparisonIntegrated Load Comparison

1

3

5

7

9

1 1

1 3

0 2000 4000 6000 8000 10000 Overall integrated load (ISPPMS), N

Tillage plot

Center row Wheel row

A

F

E

D

C

B

pass 1

2

1

2

1

2

1

2

1

2

1

2

1

3

5

7

9

1 1

1 3

0 2000 4000 6000 8000 10000 Overall integrated load (cone penetrometer), N

Tillage plot

Center row Wheel row

A

F

E

D

C

B

pass 1

2

1

2

1

2

1

2

1

2

1

2

Instrumented Blade Cone Penetrometer

B disked E double disked C no-till with cultivation F no-till w/o cultivation

A plowed and double disked D chiselled and disked

Tillage Plot Treatment Tillage Plot Treatment

Vertical Blade with Strain Gage ArrayVertical Blade with Strain Gage Array

UNL (Lincoln, Nebraska)

Discrete Model

Soil surface

Travel direction

Strain gages

Polynomial Model

Apparent soil surface

Linear Model

Soil Mechanical Resistance Soil Mechanical Resistance

Profile

Average

5 – 30 cm depth

Increase

with Depth

Sample collection for calibration Cleaning

ISFET Electrode

Water jet ~50 g soil core

Mixing

Add 20 ml DI H 2 O

Automated Soil Testing Automated Soil Testing

Shank

Soil cutters

Coring tube

Purdue University (West Lafayette, Indiana)

Soil/Buffer pH Mapping OnSoil/Buffer pH Mapping On--thethe--GoGo

The University of Sydney (Sydney, Australia) JTI (Uppsala, Sweden)

Waived sampling disc

Soil preparation and analysis unit

Automated Soil pH Mapping SystemsAutomated Soil pH Mapping Systems

US Patent No. 6,356,

Purdue University (West Lafayette, Indiana)

Soil Sampling Mechanism

Travel Direction

Water Supply

Water Nozzle

Sensors Output

Soil Shank

Removable Plates pH Sensor

Air Supply Air Cylinder

Soil Sample

Sampling Platform

5 mm

Soil pH Measurements OnSoil pH Measurements On--thethe--GoGo

Distance from the W est End, m

Soil pH

Data Set 1 Data Set 2

Laboratory

Mobil Sensor Platform (MSP)Mobil Sensor Platform (MSP)

Veris Technologies, Inc. (Salina, Kansas)

http://www.veristech.com

EC Surveyor 3150

Soil pH Manager

Direct Soil MeasurementDirect Soil Measurement

Purdue University (West Lafayette, Indiana) Veris Technologies, Inc. (Salina, Kansas) UNL (Lincoln, Nebraska)

Water Nozzle

Soil Sampler

Ion-selective Electrodes

ExampleExample

Soil pH MappingSoil pH Mapping

Soil pH Maps of

a Kansas Field

On-the-Go Mapping Conventional 1 ha Grid Sampling

Directed Soil Sampling

Evaluation Fields Evaluation Fields

27-84 acre fields 12-34 grid samples (0.3-0.5 samples/acre) 250-598 MSP measurements (4-11 measurements/acre) 5 calibration samples & 5 validation samples

WI1 Silt loam 18% 6.66 (0.47) 3.22 (1.08)

OK1 Loamy fine sand 2% 6.16 (0.64) 0.96 (0.99)

NE1 Silty clay loam 11% 5.95 (0.84) 25.86 (4.97)

KS2 Silty clay loam 3% 6.62 (0.68) 16.49 (4.6)

KS1 Silt loam / silty clay loam 6% 5.34 (0.27) 3.17 (1.00)

IL2 Loam / clay loam 2% 6.52 (0.86) 14.88 (3.66)

IL1 Loam / clay loam 2% 6.28 (0.41) 11.44 (2.22)

IA1 Loam / silty clay loam 5% 5.18 (0.77) 9.26 (5.58)

Field ID Textural range Max slope Lab pH* EC (mS m -1) *

Mapping AlternativesMapping Alternatives

Universal MSPpH = InterceptUniversal + SlopeUniversalMSP pH

Adjusted MSPpH = InterceptFieldspecific + SlopeFieldspecificMSP pH

Shifted MSPpH = ShiftFieldspecific + MSP pH

On-the-Go Sensing Soil Sampling

MSP pH

Universal MSP pH

Directed Sampling

Adjusted MSP pH

Shifted MSP pH

Field Average

Interpolated Grid Map

Soil pH Maps Evaluation Soil pH Maps Evaluation

4

5

6

7

8

9

4 5 6 7 8 9 Grid Sampling pH

Lab pH

IA1IL IL2KS KS2NE OK1WI 1:1 lineReg 4

5

6

7

8

9

4 5 6 7 8 9 Field Average pH

Lab pH

IA1IL IL2KS KS2NE OK1WI 1:1 lineReg

4

5

6

7

8

9

4 5 6 7 8 9 Shifted MSP pH

Lab pH

IA1IL IL2KS KS2NE OK1WI 1:1 lineReg 4

5

6

7

8

9

4 5 6 7 8 9 Adjusted MSP pH

Lab pH

IA1IL IL2KS KS2NE OK1WI 1:1 lineReg

4

5

6

7

8

9

4 5 6 7 8 9 Unprocessed MSP pH

Lab pH

IA1IL IL2KS KS2NE OK1WI 1:1 lineReg 4

5

6

7

8

9

4 5 6 7 8 9 Universal MSP pH

Lab pH

IA1IL IL2KS KS2NE OK1WI 1:1 lineReg

R^2 = 0.47 R^2 = 0.

R^2 = 0.60 R^2 = 0.

R^2 = 0.81 R^2 = 0.

2.5 Acre Grid

Raw MSP Universal MSP

Adjusted MSP Shifted MSP

Field Average

Numeric AgroNumeric Agro--Economic ModeEconomic Mode

NRCL = f (Income, Cost)

Income = f (Soil pH) Soil pH = f (True pH, Lime, Probability)

Cost = f (Lime)

Lime = f (Estimated pH)

Estimated pH = f (True pH, Probability)

True pH = f (Probability)

Model Input Modules:

  • Categorized distributions
  • Categorized functional relationships
  • Multidimensional arrays

Model Output (Net Return over Cost of Lime)

Ys CL Q L d

Ps Yc d

Pc Ys d

Ps Yc d

Pc NRCL − ⋅

= (^1 ) 1 ( 1 ) ( 1 ) ( 1 )

d = annual discount rate Yc = corn yield Ys = soybean yield Q (^) L = prescribed lime application rate

NRCL = Net return over cost of lime Pc = price of corn Ps = price of soybean CL = cost of lime

Integrated Agitated Soil Measurement Integrated Agitated Soil Measurement

1:1 solutions with 15 Nebraska soils

4.0 4.5 5.0 5.5 6.0 6.5 7.0 7. Reference pH

Measured pH R 2 = 0.87 (0.91 means) RMSE (Precision) = 0.15 pH Reg. SE (Accuracy) = 0.20 pH

pH

1

10

100

1 10 100 Reference nitrate-nitrogen (CR), mg/kg

Measured nitrate-nitrogen, mg/kg

(^) R 2 = 0.32 (0.40 means) RMSE (Precision) = 0.17 pNO 3 Reg. SE (Accuracy) = 0.22 pNO 3

1 pNO^3

10

100

10 100 1000 Reference soluble potassium (AAS), mg/kg

Measured soluble potassium, mg/kg

R 2 = 0.54 (0.63 means) RMSE (Precision) = 0.10 pK Reg. SE (Accuracy) = 0.13 pK

pK

Integrated Agitated Soil MeasurementIntegrated Agitated Soil Measurement

4.0 4.5 5.0 5.5 6.0 6.5 7. Reference pH

Measured pH

R2 = 0.98 (0.99 means) RMSE (Precision) = 0.08 pH Reg. SE (Accuracy) = 0.09 pH

pH

10

100

1000

10 100 1000 Reference soluble potassium (AAS), mg/kg

Measured soluble potassium, mg/kg

R 2 = 0.95 (0.98 means) RMSE (Precision) = 0.05 pK Reg. SE (Accuracy) = 0.03 pK

pK

Reference tests:

  • Soil pH
    • glass ion-selective electrode
    • RMSE = 0.05 pH
  • Soluble potassium
    • atomic adsorption spectroscopy (AAS)
    • RMSE = 0.01 pK
  • Residual nitrate
    • cadmium reduction (CR)
    • RMSE = 0.02 pNO 3

1

10

100

1 10 100 Reference nitrate-nitrogen (CR), mg/kg

Measured nitrate-nitrogen, mg/kg

R 2 = 0.48 (0.67 means) RMSE (Precision) = 0.13 pNO 3 Reg. SE (Accuracy) = 0.10 pNO 3

pNO 3

VRT Prescription VRT Prescription

6.0 6.5 7.0 7. Measured buffer pH

Measured soil pH and predicted buffer pH

Predicted buffer pHMeasured soil pH 1:1 line( )

LR = f (buffer pH)

Buffer pH = f (soil pH, CEC) R 2 = 0.

R 2 = 0.

0

200

400

600

0 200 400 600 Measured exchangeble K, mg kg -

Measured soluble K and predicted

exchangeble K, mg kg

Predicted exchangable KMeasured soluble K 1:1 line

K rate = f (exchangeable K)

Exchangeable K = f (soluble K, CEC)

R 2 = 0.

R 2 = 0.

Integrated Multiple Data LayersIntegrated Multiple Data Layers

Maps produced by Veris Technologies, Inc. (Salina, Kansas)

Soil pH & Clay & OM

= Lime Recommendation

Applicability of OnApplicability of On--thethe--Go Soil SensorsGo Soil Sensors

Residual nitrate (total nitrogen) Some Some OK

CEC (other buffer indicators) OK OK

Other nutrients (potassium) Some OK

Soil pH Some Good

Depth variability (hard pan) Some OK Some

Soil compaction (bulk density) Good Some

Soil salinity (sodium) OK Some

Soil water (moisture) Good Good

Soil organic matter or total carbon Some Good

Soil texture (clay, silt and sand) Good OK Some

Soil property H+ H+ (^) H+H

H+

Status of Implementation Status of Implementation

  • Commercial
    • Electrical conductivity
    • Topography
    • Soil pH
    • Visual/near-infrared spectroscopy
  • Available solutions
    • Implement draft
    • Ground penetrating radar
    • Magnetic field
    • Gamma-radiometry
  • Upcoming solutions
    • Capacitance (moisture)
    • Residual nitrate and soluble potassium
    • Soil mechanical resistance
    • Machine vision
    • Small scale topography

Sensor fusion

  • and New applications

Directed (Guided) Sampling Directed (Guided) Sampling

  • Directed sampling should be used to

calibrate and/or validate sensor data

  • Directed samples should be collected

from relatively homogeneous field areas

away from the boundary and other

transitional areas

  • Directed samples should cover the entire

range of sensor-based measurements,

especially toward low and high ends

  • Directed samples should be physically

spread across the entire field

  • It should be possible to process multiple

sensor-based data layers

Currently Considered Criteria Currently Considered Criteria

Homogeneity

Neighborhood variability

Even data spread

D-optimality

Even field coverage

S-optimality

Example of Objective FunctionExample of Objective Function

OF = SoptDoptpHDoptECHcrpHHcrEC

  • S-optimality
  • D-optimality (soil pH)
  • D-optimality (soil EC)
  • H-criteria (soil pH)
  • H-criteria (soil EC)

Prescribed SamplingPrescribed Sampling

4.5 5.0 5.5 6.0 6.5 7.0 7.5 8. Soil pH

Soil EC, mS/m

pH - L EC - H

pH - L EC - L

pH - H EC - L

pH - H EC - H

4.5 5.0 5.5 6.0 6.5 7.0 7.5 8. Soil pH

Soil EC, mS/m

a) b)

Categorical data

separation

Latin Hypercube

Sampling (LHS)

Summary Summary

  • On-the-go soil sensors can provide high

density information about soil properties

  • Many sensor approaches are past initial

commercialization stage

  • Sensor fusion provides the ability to separate

various agronomic effects

  • Site-specific sensor calibration and validation

are essential steps of the mapping process

  • Laboratory soil analysis remains a required

supplementary practice

  • Agro-economic value of selected sensor-

based data layers is site-specific http://bse.unl.edu/adamchuk

E:mail: vadamchuk2@.unl.edu