Note: This document is for an older version of GRASS GIS that has been discontinued. You should upgrade, and read the current manual page.
NAME
r.mess - Computes multivariate environmental similarity surface (MES)
KEYWORDS
similarity,
raster,
modelling
SYNOPSIS
r.mess
r.mess --help
r.mess [-mnkci] ref_env=names[,names,...] [ref_rast=name] [ref_vect=name] [ref_region=name] [proj_env=names[,names,...]] [proj_region=name] output=name [digits=string] [nprocs=integer] [memory=memory in MB] [--overwrite] [--help] [--verbose] [--quiet] [--ui]
Flags:
- -m
- Calculate Most dissimilar variable (MoD)
- -n
- Area with negative MESS
- -k
- sum(IES), where IES < 0
- -c
- Number of IES layers with values < 0
- -i
- Remove individual environmental similarity layers (IES)
- --overwrite
- Allow output files to overwrite existing files
- --help
- Print usage summary
- --verbose
- Verbose module output
- --quiet
- Quiet module output
- --ui
- Force launching GUI dialog
Parameters:
- ref_env=names[,names,...] [required]
- Reference conditions
- ref_rast=name
- Reference area (raster)
- Reference areas (1 = presence, 0 or null = absence)
- ref_vect=name
- Reference points (vector)
- Point vector layer with reference locations
- ref_region=name
- Reference region
- Region with reference conditions
- proj_env=names[,names,...]
- Projected conditions
- proj_region=name
- Projection region
- Region with projected conditions
- output=name [required]
- Root name of the output MESS data layers
- digits=string
- Precision of your input layers values
- Options: 0-6
- Default: 3
- nprocs=integer
- Number of threads for parallel computing
- Default: 1
- memory=memory in MB
- Maximum memory to be used (in MB)
- Cache size for raster rows
- Default: 300
r.mess computes the multivariate environmental similarity
(MES) [1], which measures how similar environmental conditions in one
area are to those in a reference area. This can also be used to compare
environmental conditions between current and future scenarios. See the
supplementary materials of Elith et al. (2010) [1] for more details.
Besides the MES, r.mess computes the individual similarity
layers (IES - the user can select to delete these layers) and,
optionally, several other layers that help to further interpret the MES
values:
- The area where for at least one of the variables has a value
that falls outside the range of values found in the reference set.
- The most dissimilar variable (MoD).
- The sum of the IES layers where IES < 0. This is similar to
the NT1 measure as proposed by Mesgaran et al. 2014 [2].
- The number of layers with negative values.
The user can compare a set of reference (baseline) conditions to
projected (test) conditions. The reference conditions are defined by a
set of environmental raster layers (ref_env). To specify the
reference area, one of the following can be used:
- ref_rast = reference raster layer: A raster with values of 1
and 0 (or nodata). Reference conditions are derived from the locations
where the raster value is 1.
- ref_vect = reference vector point layer: Reference conditions
are taken for the point locations in the vector layer.
- ref_region = reference region: Only areas within the
specified region's boundaries are considered as the reference
area.
If no reference raster map, vector map, or region is provided, the entire
area covered by the input environmental raster layers is used as the
reference area.
The projected (test) conditions are defined by a second set of
environmental variables (proj_env). They can represent future
conditions in the same area (similarity across time), or conditions in
another area (similarity between two different areas). If a projection
region (proj_region) is provided, the MESS (and other layers)
will be limited to that region.
If proj_env is not provided, the MESS value of a raster cell
represents how similar the conditions in that cell are compared to the
medium conditions across the whole area.
The examples below use the bioclimatic variables bio1 (mean annual
temperature), bio12 (annual precipitation), and bio15 (precipitation
seasonality) in Kenya and Uganda. All climate layers (current and
future) are from
Worldclim.org.
The protected areas layer includes all nationally designated protected
areas with a IUCN category of II or higher from
protectedplanet.net.
The simplest case is when only a set of reference data layers (
ref_env
) is provided. The multi-variate similarity values of the resulting
map are a measure of how similar conditions in a location are to the
median conditions in the whole region.
g.region raster=bio1
r.mess ref_env=bio1,bio12,bio15 output=Ex_01
Thus, in the following maps, the value in each pixel represents how
similar conditions are in that pixel to the median conditions in the
entire region, in terms of mean annual temperature (bio1), mean annual
precipitation (bio12), precipitation seasonality (bio15) and the three
combined (MES).
In the second example, conditions in the whole region are compared to
those in the region's protected areas (ppa), which thus serves as the
reference/sample area. See
van Breugel et
al.(2015) [3] for an example of how this can be useful.
g.region raster=bio1
r.mess -m -n -i ref_env=bio1,bio12,bio15 ref_rast=ppa output=Ex_02
In the figure below the map with the protected areas, the MES, the most
dissimilar variables, and the areas with novel conditions are given.
They show that the protected areas cover most of the region's annual
precipitation, mean annual temperature, and precipitation seasonality
gradients. Areas with novel conditions can be found in northern Kenya.
Similarity between long-term average conditions based on the period
1950-2000 (
ref_env) and projections for climate conditions in
2070 under RCP85 based on the IPSL General Circulation Models (
proj_env). No reference points or areas are defined in this
example, so the whole region is used as a reference.
g.region raster=bio1
r.mess ref_env=bio1,bio12,bio15 proj_env=IPSL_bio1,IPSL_bio12,IPSL_bio15
output=Ex_03
Results (below) shows that there is a fairly large area with novel
conditions. Note that in the MES map, the values are based on
the highest negative value across the input variables (here bio1,
bio12, bio15). In the SumNeg map, values of all input variables
are summed when negative. The Count map shows for each raster
cell how many variables have negative similarity scores. Thus, the
values in the MES and SumNeg maps only differ where the
MES of more than one variable is negative (dark gray areas in the
Count map).
[1] Elith, J., Kearney, M., & Phillips, S.
2010. The art of modelling range-shifting species. Methods in
Ecology and Evolution 1:330-342.
[2] Mesgaran, M.B., Cousens, R.D. & Webber, B.L. (2014) Here be
dragons: a tool for quantifying novelty due to covariate range and
correlation change when projecting species distribution models.
Diversity & Distributions, 20: 1147-1159, DOI: 10.1111/ddi.12209.
[3] van Breugel, P., Kindt, R., Lillesø, J.-P.B., & van Breugel,
M. 2015. Environmental Gap Analysis to Prioritize Conservation Efforts
in Eastern Africa. PLoS ONE 10: e0121444.
For an example of using the
r.mess addon as part of a modeling
workflow, see the tutorial
Species
distribution modeling using Maxent in GRASS GIS.
Paulo van Breugel,
https://ecodiv.earth | HAS green academy University of Applied Sciences |
Innovative
Biomonitoring research group |
Climate-robust
Landscapes research group
SOURCE CODE
Available at:
r.mess source code
(history)
Latest change: Monday Dec 02 10:49:41 2024 in commit: 68521b7f1148f838062401c1dcacbe1e7b358f4d
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GRASS Development Team,
GRASS GIS 8.3.3dev Reference Manual