Use of Near-infrared Spectroscopy for Monitoring and Analysis of Carbon Sequestration in Soil - PowerPoint PPT Presentation

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Use of Near-infrared Spectroscopy for Monitoring and Analysis of Carbon Sequestration in Soil

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Title: Use of Near-infrared Spectroscopy for Monitoring and Analysis of Carbon Sequestration in Soil


1
Use of Near-infrared Spectroscopy for Monitoring
and Analysis of Carbon Sequestration in Soil
by P.D. Martin, and D.F. Malley PDK Projects,
Inc. Winnipeg, Manitoba, Canada
2
Vision
  • Soil and plant analyses are available when and
    where they are needed
  • Need for information, rather than analytical
    cost, to dictate the number and kinds of analyses
  • Analyses promote sound, sustainable environmental
    and agricultural management

3
Purpose
  • Introduce Near-infrared Spectroscopy (NIRS)
  • Describe
  • Benefits to use of NIRS
  • How NIR can be used for soil carbon assessment
  • Services available from PDK

4
NIR Facts
  • NIRS provides rapid, chemical-free, flexible
    analysis
  • NIRS is used globally for food and feed analysis
  • NIRS has enormous potential for
    agro-environmental applications, including soil
    carbon assessment

5
Near-infrared Spectroscopy
  • Utilizes the absorbance of NIR light (780 - 2500
    nm) by vibrating bonds between atoms in molecules
  • O-H, C-H, C-N, C-O, P-O, S-O
  • Molecular spectroscopy - analyzes intact samples
  • NIR absorbances obey the Beer/Lambert law

6
The Work of Doing NIR Analysis
  • Compositional information on samples (n gt100) is
    correlated with the spectral information to
    develop statistical calibration models
  • The calibrations train the instrument to
    analyze future unknown samples

7
Features
  • does not destroy the sample
  • is rapid, lt 2 min/test
  • analyzes many constituents simultaneously
  • analyzes compositional and functional properties
  • field portable

8
Lab and Field Instrument Zeiss Corona
9
Organic Matter Compositional Parameters
  • Organic matter/organic C
  • OM, OC
  • Total C (LECO)
  • C HUMUS
  • Humic acid fractions
  • Humic and Fulvic
  • Fulvic acid fractions
  • Lignin content
  • Cellulose content

r2 0.81-0.97 0.93-0.96 0.94 0.95 0.91 0.63 0.77-0.
83 0.81
Performance good exc. v.good -
exc. v.good v.good v.good poor good good
10
Compositional Parameters contd
  • r2 performance
  • Clay 0.81-0.87 good
  • Total N 0.86-0.96 good - v.good
  • moisture 0.93-0.98 v.good exc.
  • CEC 0.9 v.good

11
Organic Carbon
  • Miniota area
  • Newdale Soil Assoc.
  • Dried, ground samples (2mm)
  • N 267
  • 1100 - 2500 nm
  • r2 0.78
  • SEP 0.33

12
Field-moist applications
  • Moisture corrected calibration
  • 0.033 and 1.5 MPa moisture tension
  • r2 0.89
  • SEP 0.23
  • Range 0.45 3.16 OC

Sudduth, K.A. and J.W. Hummel (1993). Soil
organic matter, CEC and moisture sensing with a
portable NIR spectrophotometer. Trans of the
ASAE 361571-1582
13
Example of On-site Soil Testing Method
  • Soil cores - grid or stratified sampling
  • Cores sliced on-site
  • Presentation of static, as is, field moist
    samples
  • Multiple constituents simultaneously

14
NIRS Benefits
  • COST !
  • LECO OC 27/sample
  • NIR OC 6/sample
  • Minimal sample preparation
  • Dried and ground (2mm mesh)
  • Potential for as is or field moist
    determinations
  • Timeliness
  • Potential for immediate analysis

15
NIRS Benefits, cont.
  • Precision
  • Precision of NIR equal or better than reference
  • Does not destroy the sample
  • The same sample can be analyzed many times over
  • Positive implications for long term and/or
    incubative studies

16
NIRS Limitations
  • Site to Site Bias
  • Potential for bias in predictions of samples from
    one site using calibrations derived from samples
    from another site.
  • Affects absolute accuracy
  • Does not affect precision
  • This can be corrected by incorporating a small
    number of samples from the new site into the
    calibration.
  • At present, this means that NIRS is not practical
    for small sample groups

17
How can NIRS work for you?
  • Objective sample selection1
  • NIRS can be used to select sample sets from a
    large group of samples which
  • Retain a maximum representation of overall sample
    population variability
  • Samples selected better than random because
  • Greater recovery of range
  • Higher variance
  • Better Kurtosis (more even distribution)

1Stenberg, B. et al. (1995) Use of near infrared
reflectance spectra of soils for objective
selection of samples. Soil Science. 159109-114.
18
Objective Sample Selection, cont.
  • Using NIR for selecting analytical samples
    reduces cost directly by lowering the number of
    samples that need to be analyzed to encompass
    soil variability.
  • Stenberg, et al. estimated a 70 reduction in
    cost for their study using this method
  • For their study, the overall n 144 samples,
    selected n 20 samples

19
Calibration and Prediction
  • Calibrations are developed on a selected set of
    samples (ie. using the NIR selection method)
  • These calibrations can be used to predict the
    remaining samples.
  • Requires large sample sets
  • ncalibration 100 samples recommended

20
Calibration and Prediction, cont.
  • Extra cost of calibration and accompanying wet
    chemistry is offset by a large economy of scale
  • Once a calibration is developed, it only requires
    updating with a much smaller number of QA/QC
    samples
  • Calibrations will eventually exist for various
    soils, bringing initial costs down

21
Monitoring and Long-term Soil Quality Assessment
  • NIR spectra contain information for both carbon
    quantity, and carbon quality in soil
  • High precision plus lower cost of NIR results
    make large scale assessments of soil carbon flux
    much more feasible, both
  • Over time
  • Under varying management practices.

22
Monitoring and Long-term Soil Quality Assessment,
cont.
  • Non destructive nature of NIR, coupled with
    as-is and/or on-site assessment potential
    mean that
  • The same sample could be analyzed indefinitely
    over time.
  • Could reduce potential subsampling error
  • Could increase relevance of results

23
Sensing Soil QualityLarge Area Surveillance of
Soil Condition and Trend
http//www.worldagroforestrycentre.org/sites/progr
am1/specweb/home.htm
24
Services Available from PDKIntroductory Pricing
  • Objective Sample Selection
  • Samples submitted dried and ground (2mm)
  • 6.00 per sample

25
Services Available from PDK, cont.
  • Compositional Analysis
  • Calibration
  • Samples (100 samples, 5 g/sample min) submitted
    dried and ground in borosilicate vials or bags
  • Reference values submitted for constituents of
    interest, including QA/QC data from the
    analytical laboratory. (Reference chemistry can
    be arranged at a Lab of your choice, at
    commercial rates -extra)
  • First calibration 6.00/sample plus 150
  • Each additional calibration 250

26
Compositional Analysis, cont.
  • 2. Prediction of future samples
  • Prediction of future unknown samples of the same
    type as in the calibrations, submitted dried and
    ground
  • First constituent 6.00/sample
  • Each additional constituent 1.00/sample

27
Services available from PDK, cont.
  • Consulting
  • Custom Quote for
  • Setup of personal NIR program
  • Setup of field portable instrument
  • Contract Research
  • Instrument selection/evaluation

28
Conclusions
  • NIR is the only practical method for analyzing
    large numbers of samples for measurement of C
    stores
  • NIR has potential to determine quality/persistence
    of organic C in soil

29
Acknowledgments
  • Foss NIRSystems Inc., USA
  • Carl Zeiss, Germany
  • Agriculture and Agri-Food Canada
  • Manitoba Rural Adaptation Council (MRAC)
  • Industrial Research Assistance Program (IRAP)
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