area2catena | R Documentation |
Takes raster data from a GRASS location and calculates catena properties.
area2catena(
mask = NULL,
flowacc = NULL,
eha = NULL,
distriv = NULL,
elevriv = NULL,
supp_quant = NULL,
supp_qual = NULL,
dir_out = "./",
catena_out = NULL,
catena_head_out = NULL,
ridge_thresh = 1,
min_cell_in_slope = 30,
min_catena_length = 3,
max_riv_dist = 10,
plot_catena = F,
grass_files = F,
ncores = 1,
eha_subset = NULL,
overwrite = F,
silent = F
)
mask |
Raster file to be used as MASK in the GRASS location defining the
area of interest. E.g. |
flowacc |
Name of flow accumulation raster map in GRASS location. Can
be created with |
eha |
Name of elementary hillslope area raster map in GRASS location.
Can be created with |
distriv |
Name of distance to river raster map in GRASS location. Can
be created with |
elevriv |
Name of relative elevation raster map in GRASS location. Can
be created with |
supp_quant |
Character vector containing names of quantitative supplemental raster maps in GRASS location; leave empty if you have none. |
supp_qual |
Character vector containing names of qualitative supplemental raster maps in GRASS location; leave empty if you have none. |
dir_out |
Character string specifying output directory (will be created; nothing will be overwritten). |
catena_out |
Output: Name of output file containing mean catena information
as input for |
catena_head_out |
Output: Name of output header file containing meta-information
as input for |
ridge_thresh |
Integer specifying threshold of flow accumulation, below which a cell is considered a start of a flowpath (usually 1 for D8 flowaccumulation grids, DEFAULT). |
min_cell_in_slope |
Integer specifying minimum number of cells a hillslope area must have, all smaller ones are skipped. Default: 30. |
min_catena_length |
Integer specifying minimum number of sampling points (cells) a catena should have. If there are less, the catena is not saved. Default: 3. |
max_riv_dist |
Integer specifying maximum distance to river [in cells]:
if the closest cell of an EHA is farther than |
plot_catena |
logical; produce plots (scatter, mean catena, etc.) for each area / class (written into sub-directory plots_area2catena). |
grass_files |
logical; produce GRASS reclassification files for qualitative raster data. If an attribute name starting with 'svc' is found, the respective reclass file is produced anyway. |
ncores |
Integer specifying number of cores that should be used for computation - allows faster parallel computations (see Details). |
eha_subset |
NULL or integer vector with subset of EHA ids that shall be processed (for debugging and testing). |
overwrite |
|
silent |
|
Function returns nothing. Output files are written into output directory as specified in arguments.
Prepare GRASS location and necessary raster files in advance (e.g. using
lump_grass_prep
) and start GRASS session in R using
initGRASS
.
IMPORTANT: Herein, when specifying the GRASS input maps, please do explicitly refer to the mapset if it is different from the mapset given in initGRASS() (even PERMANENT!), as otherwise internally used readRAST() command resulted in errors under Windows.
In case of long computation times or memory issues, try plot_catena = FALSE
and specify an RData file as catena_out
. Furthermore, make sure your
raster maps are not overly large (i.e. containing lots of NULL values around
the region of interest) and are of type CELL
(i.e. integer) where it makes
sense (check with r.info
in GRASS).
Parallel option (ncores
>1) may speed-up computations. It requires the packages
doMC
and doParallel
. Set ncores
to a value less than the number of cores
your computer has; larger values will decrease performance.
GUIs such as RStudio may not produce some runtime messages (within parallel
foreach loop).
File catena_out
contains information about the representative catena
for each hillslope (EHA). For meaning of columns see file catena_head_out
.
It usually contains the catena ID, the catena's profile point IDs, relative
vertical elevation above hillside toe, and supplemental information averaged
over all raster cells associated with a specific catena profile point. For
qualitative data the latter means the areal fraction of a specific attribute
class (sum over all classes of an attribute should be equal to one for a profile
point), for quantitative data it is a numerical value. Averages over raster
cells are weighted by relative flow path densities of the raster cells. For
more details on the algorithm see the reference below.
Tobias Pilz tpilz@uni-potsdam.de, Till Francke francke@uni-potsdam.de
Source code based on SHELL
and MATLAB
scripts of Till Francke.
lumpR package introduction with literature study and sensitivity analysis:
Pilz, T.; Francke, T.; Bronstert, A. (2017): lumpR 2.0.0: an R package facilitating
landscape discretisation for hillslope-based hydrological models.
Geosci. Model Dev., 10, 3001-3023, doi: 10.5194/gmd-10-3001-2017
Theory of LUMP:
Francke, T.; Guentner, A.; Mamede, G.; Mueller, E. N. and Bronstert, A (2008):
Automated catena-based discretization of landscapes for the derivation of
hydrological modelling units. International Journal of Geographical
Information Science, Informa UK Limited, 22(2), 111-132, DOI: 10.1080/13658810701300873
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