1 / 32

Method of Soil Analysis 1.5 Geostatistics 1.5.1 Introduction 1.5.2 Using Geostatistical Methods

Method of Soil Analysis 1.5 Geostatistics 1.5.1 Introduction 1.5.2 Using Geostatistical Methods. 1 Dec. 2004 D1 Takeshi TOKIDA. 1.5.1 Introduction. True understanding of the spatial variability in the soil map is very limited. Distinct boundary (too continuous or sudden change).

casimir
Télécharger la présentation

Method of Soil Analysis 1.5 Geostatistics 1.5.1 Introduction 1.5.2 Using Geostatistical Methods

An Image/Link below is provided (as is) to download presentation Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author. Content is provided to you AS IS for your information and personal use only. Download presentation by click this link. While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server. During download, if you can't get a presentation, the file might be deleted by the publisher.

E N D

Presentation Transcript


  1. Method of Soil Analysis1.5 Geostatistics1.5.1 Introduction1.5.2 Using Geostatistical Methods 1 Dec. 2004 D1 Takeshi TOKIDA

  2. 1.5.1 Introduction • True understanding of the spatial variability in the soil map is very limited. • Distinct boundary (too continuous or sudden change). • Assumption of uniformity within a mapping unit is not necessarily valid. • Spatial and temporal variability diversify our environment. It’s Benefit! • However Soil variation can be problematic for landscape management.

  3. 1.5.1Introduction • There is a need to study surface variations in a systematic manner. • Geostatistical methods are used in a variety of disciplines. • e.g. mining, geology, and recently biological sciences also. • Numerous books have been published.

  4. 1.5.1.1 Geostatistical Investigations Geostatistics is used to… • map and identify the spatial patterns of given attributes across a landscape. • improve the efficiency of sampling networks. • identify locations in need of remediation. • Disjunctive kriging→Probability map • predict future effects in the landscape. • Random field generation→Conditioned→Predict

  5. Analysis Appropriate data collection Objective of the study 1.5.2 Using Geostaitstical Methods1.5.2.1 Sampling • Consider the appropriate sampling methodology (see Section 1.4) The analysis of the data depend on the objective of the study and appropriate data collection.

  6. Table 1.5-1 • If the Kolmogrov-Smirnov statistic is greater than the critical value, the hypothesis of “not being normal” is adopted. • If the distribution is completely normal, skew and kurtosis values are 0.

  7. Table 1.5-2 ? Na values can be used to estimates B content at lower cost.

  8. Randome function & realization • Observed data are a single realization of the random field, Z(x). Z(xα) Realization + Assumptions, i.e. stationarity Random field (Random function)

  9. 1.5.2.2 Spatial Autocorrelation • Only if a spatial correlation exists, geostatistical analysis can be used. • Fig. 1.5-1 A: No spatial correlation • Fig.1.5-1 B: spatially correlated Fig. 1.5-1

  10. 1.5.2.2.a Variogram Variogram Experimental variogram (Estimator) How to create pairs?

  11. Variogram model Variance is undefined Var(Z) 95% Practical range

  12. Important considerations when calculating the variogram 1 Between a lag interval, in this case 1.5 to 4.5, a wide range of actual separation distance occurs. Imprecision compared with a situation where every sampling pair has the same distance A large number of pairs are used to calculate a variogram value. It is generally accepted that 30 or more pairs are sufficient to produce a reasonable sample variogram. Fig. 1.5-3

  13. Important considerations when calculating the variogram 2 • Width of the lag interval can affect the variance. • This is not the case. • The value for h (actual separation distance) is affected by the lag width. Fig. 1.5-4

  14. Fig. 1.5-1 & 1.5-5 • The variograms reproduce spatial structure of simulated random fields. Fig. 1.5-1

  15. Example of variogram Sill • Some information at the smaller scales (less than 48 m) has been lost. • For both attribute, the range is about 900 m. Sill Nugget effect Range

  16. 1.5.2.2.d Directional Variograms • Often there is a preferred orientation with higher spatial correlation in a certain direction. • For many situations, the anisotropic variogram can be transformed into an isotropic variogram by a linear transformation. Geometric anisotropy Fig. 1.5-7 Fig. 1.5-8

  17. 1.5.2.2.e Stationarity A sample at a location Impossible to determine the probability distribution at the point! The joint distribution do not depend on the location. Assumption: A stationary Z(x) has the same joint probability distribution for all locations xi and xi+h.

  18. Autocovariance Second-Order Stationarity 1.5-3, 1.5-6 C(0) g(h) g Sill Nugget effect C(h) h Range

  19. If , the random field is stationary in terms of Intrinsic hypothesis. Intrinsic Stationarity(Hypothesis) No Drift Theoretical Variogram Drift? No Drift? Fig. 1.5-9

  20. 1.5.2.2.c Integral Scale 1.5-5 A measure of the distance for which the attribute is spatially correlated. 1.5-4 Autocorrelation function: normalized form of the autocovariance function

  21. 1.5.2.3 Geostatistics and Estimation • Kriging produces a best linear unbiased estimate of an atribute together with estimation variance. • Multivariate or cokriging: Superior accuracy • Powerful tool, useful in a wide variety of investigations.

  22. 1.5.2.3.a Ordinary Kriging We wish to estimate a value at xo using the data values and combining them linearly with the weiths: λi xo 1.5-7 Z* should be unbiased: 1.5-9

  23. Derivation of equation 1.5-10 Z* should be best-linear, unbiased estimator. Our goal is to reduce as much as possible the variance of the estimation error. First, rewrite the estimation variance 0

  24. Derivation of equation 1.5-10 Let’s rewrite the estimation variance in terms of the semivariogram. We assume intrinsic hypothesis. From the definition of the semivariogram we know:

  25. Just substitute: Derivation of equation 1.5-10 0 1 1

  26. Derivation of equation 1.5-10 We define an objective function φ containing a term with the Lagrange multiplier, 2β. To solve the optimization problem we set the partial derivatives to zero:

  27. Derivation of equation 1.5-10 Ordinary Kriging system equation 1.5-10 Example:

  28. Derivation of equation 1.5-10 Kriging Variance equation 1.5-12 Block Kriging Estimation of an average value of a spatial attribute over a region. equation 1.5-13 Average variogram values Variance equation 1.5-14 equation 1.5-15

  29. 1.5.2.3.b Validation Cross validation Little bias Estimated kriging variance is nearly equal to the actual estimation error.

  30. 1.5.2.3.c Examples Isotropic Case, Kriging Matrix. equation 1.5-18 equation 1.5-10 1.5-11 But we can’t find the values of a given attribute! λ1=0.107, λ2=0.600, λ3=0.154, λ4=0.140 Note that the weight for point 1 is less than point 4, even though the distance from the estimation site is almost the same.

  31. Creating Maps Using Kriging Directional variogram oriented in 0°& 90° Length of each ray is equal to the range of the directional variogram. Anisotropy ratio = major axes / minor axes

  32. Creating Maps Using Kriging Fig. 1.5-12 Based on Anisotropic variogram Fig. 1.5-13 Based on isotropic variogram

More Related