mri: mri

View source: R/mri.R

mriR Documentation

mri

Description

Local adaptation and evaluation of maps of continuous variables in raster format by use of point location data.

Usage

mri(
  x = NULL,
  y = NULL,
  z = NULL,
  field = NULL,
  edge = 0,
  filter = 1,
  resolution = NULL,
  md = "Sph",
  rg = NULL,
  ng = 0.1,
  check.data = TRUE
)

Arguments

x

SpatRaster. Required. Must be have a defined Cartesian coordinate system. Data must be continuous. If more than one layer, the first layer will be used.

y

SpatVector of polygons. Optional. Delineates the area within which the raster layer shall be locally adapted and evaluated. If not provided, the analyses will be performed within the intersect of the raster and the sampled area. Must be have a defined Cartesian coordinate system (same as x).

z

SpatVector of points Required. Must have at least one column with numerical data and these data must be of the same entity and unit as x (specify this column by argument: field). Must be have a defined Cartesian coordinate system (same as x).

field

Character value. Required. Name of the column in y with the data that shall be used to locally adapt and evaluate the raster.

edge

Numeric value. Optional. Specifies the width (unit of the coordinate reference system) of a buffer zone inside the edge of the polygon that is excluded from the analyses. Allowed values are within the closed range of 0-10000.

filter

Positive integer. Optional. No of cells in the side of a square window for mean filtering of x. Filtering is done before any resampling (see argument: resolution). Allowed values are within the closed range of 1-20.

resolution

Positive numeric value. Optional. The resolution (m) to which the imported raster shall be resampled before the adaptation. Allowed values are within the closed range of 0.1-10000. In addition, a resolution that means more than 1E+8 raster cells is not allowed.

md

Character value. Optional. Variogram model type for the standardized variograms used for ordinary kriging interpolation of observed data or residuals. Variograms are generated by gstat::vgm. Default is "Sph" (spherical model).

rg

Numeric value. Optional. Range of the standardized variograms used for ordinary kriging interpolation of observed data or residuals. Variograms are generated by gstat::vgm. If no rg is specified it will be set to half of the square root of the mapping area: y (possibly shrinked by edge).

ng

Numeric value. Optional. Nugget of the standardized variograms used for ordinary kriging interpolation of observed data or residuals. Variograms are generated by gstat::vgm. The nugget is expressed as a fraction of the sill. A ng = 0.1 means that the nugget is 10 percent of the sill. The sill is by default equal to the variance of the data to be kriged (i.e the point observations or the residuals). Allowed values of ng are within the closed range of 0-1.

check.data

Logical value. Default is TRUE. Shall attributes, geometries and projections of the input data (arguments x, y and z) be checked.

Details

The mri function is intended for local adaptation and evaluation of raster maps with continuous variables. A SpatRaster and a SpatVector of point data (same variable and unit as the raster) are required. A SpatVector of polygons can optionally be used to delineate the area for local adaptation and evaluation.

It is a requirement that all spatial objects (x, y and z) have the same projection. The analyses require a Cartesian coordinate reference system.

Four maps are (created and) evaluated: the original raster map, a map created solely based on the soil samples data (ordinary kriging using a standardized variogram), two maps based on a combination of the raster data and the point observations (regression kriging and residual kriging, both using standardized variograms).

The maps are evaluated by leave-one-out cross validation and a number of evaluation measures are computed: the Nash-Sutcliffe modelling efficiency (E), the mean absolute error (MAE; Janssen & Heuberger, 1995), the coefficient of determination of a linear regression between predicted and measured values (r2).

The mapped area is the intersection between the original raster map (argument: x), any provided SpatVector of polygons (argument: y) and the buffered point locations. The buffer width is 1.5*(next largest distance) between one point and its nearest neighbor).

The mapsRInteractive algorithmns have been described ad by Piikki et al.(2017) and Nijbroek et al. (2018), where more details can be found .

On error: check that required data are provided (arguments x, y, z and field), check that all spatal datasets (arguments x, y, z) are projected, check that they do overlap and check that the arguments edge, filter and resolution have appropriate values.

Value

A list with:

1) 'maps'. A raster stack of the original raster map ('map'), the map, created by ordinary kriging of observed data ('ordkrig'), by residual kriging ('reskrig') and by regression kriging ('regkrig').

2) 'area'. SpatVector of the polygon delineating the mapped area.

3) 'pts'. SpatVector of point locations used for mapping, i.e points falling within the mapped area, excluding points with NA values in the observed values or the values extacted from the original map. The column names mean: obs = observed values. map = original map values. ordkrig_cv = values from the leave-one-out cross validation of the ordinary kriging. res = residuals (map - obs) reskrig_cv = values from the leave-one-out cross validation of the residual kriging. regpred = predicted values from the linear regression (obs = a*map + b) regres = residuals (regpred - obs) regkrig_cv = values from the leave-one-out cross validation of the regression kriging.

4) 'evaluation'. a data.frame with evaluation statistics for the original map and the leave-one-out cross-validation of the other mapping methods.

5) 'feedback' a character vector with logged feedback on inputted and used data.

References

Nijbroek, R., Piikki, K., Söderström, M., Kempen, B., Turner, K. G., Hengari, S., & Mutua, J. (2018). Soil Organic Carbon Baselines for Land Degradation Neutrality: Map Accuracy and Cost Tradeoffs with Respect to Complexity in Otjozondjupa, Namibia. Sustainability, 10(5), 1610. doi:10.3390/su10051610

Piikki, K.,Söderström, M., Stadig, H. 2017. Local adaptation of a national digital soil map for use in precision agriculture. Adv. Anim. Biosci. 8, 430–432.

Janssen, P.H.M.; Heuberger, P.S.C.1995. Calibration of process-oriented models. Ecol. Model., 831, 55–66.

Nash, J.E.; Sutcliffe, J.V. River flow forecasting through conceptual models part I—A discussion of principles. J. Hydrol. 1970, 103, 282–290.

Examples

#load package
require(terra)

#create a synthetic example raster dataset
rr1<-rast(nrow=10, ncol=10, 
  vals= sample(1:4, 100, replace=TRUE), 
  crs=crs("EPSG:3857")
  )
rr2<-disagg(rr1, 4, 'bilinear')

#create an example SpatVector of points
p<-spatSample(x=rr1, size=30, values=TRUE, as.points=TRUE)

#do local evaluation and adaptation of the raster data based on the point data
m<-mri(x = rr2, z = p, field ="lyr.1")

##check evaluation measures
print(m$evaluation)
plot(m$maps)

mapsRinteractive documentation built on April 24, 2023, 9:10 a.m.