# Landscape Metric Covariates

#### Bill Peterman

# 1 Why explicit covariate specifications?

Traditional `multiScaleR` workflows assume that each raster layer becomes one optimized, kernel-weighted covariate. That remains the default behavior. For landscape metrics, however, the relationship between raster layers and model covariates is no longer one-to-one.

For example, the same binary forest raster might be used to calculate:

- a distance-weighted proportion of forest cover,
- edge density within a fixed buffer, and
- edge density at an optimized scale.

Those are different covariates, even though they come from the same source raster. The `msr_vars()` interface lets you name those derived covariates explicitly.

# 2 Landscape metric reference

`landscape_var()` supports 25 metrics grouped into five families. All metrics are computed within a circular buffer centered on each sample point (or on each raster cell when projecting with `kernel_scale.raster()`). Metrics that operate on categorical rasters expect integer class values; continuous rasters should be classified before use.

Most metrics describe the whole landscape within the buffer. Three are class-level: they describe a single category and require a `class` argument naming the focal class (covered in Class-level metrics). All of the categorical metrics reproduce the values returned by the `landscapemetrics` package, which itself follows the FRAGSTATS conventions.

## 2.1 Composition metrics

These metrics describe the diversity and abundance of patch types within the buffer. They require a categorical (integer-valued) raster.

Code | Name | Description
--- | --- | ---
`shdi` | Shannon Diversity Index | \(-\sum p_i \ln p_i\), where \(p_i\) is the proportion of class \(i\). Increases with richness and evenness. The `base` argument controls the logarithm base (default: natural log).
`shei` | Shannon Evenness Index | SHDI / ln(richness). Ranges from 0 (one dominant class) to 1 (perfectly even).
`sidi` | Simpson Diversity Index | \(1 - \sum p_i^2\). Probability that two randomly selected cells belong to different classes. Ranges from 0 to 1.
`siei` | Simpson Evenness Index | SIDI / (1 - 1/richness). Standardizes SIDI against maximum possible diversity. Requires at least 2 classes and can be uninformative for optimized scales when local evenness is uniform across sample points.
`msidi` | Modified Simpson Diversity | \(-\ln \sum p_i^2\). Logarithmic transformation of Simpson concentration; unbounded above.
`msiei` | Modified Simpson Evenness | MSIDI / ln(richness). Evenness analogue of MSIDI. Can be uninformative for optimized scales when local evenness is uniform across sample points.
`pr` | Patch Richness | Count of distinct classes present in the buffer.
`prd` | Patch Richness Density | PR per 100 ha of buffer area.
`rpr` | Relative Patch Richness | (PR / `classes_max`) × 100. Requires the `classes_max` argument.
`ta` | Total Area | Total area of the buffer in hectares.

## 2.2 Edge metrics

These metrics quantify the amount and complexity of boundaries between classes. They require a categorical raster and use cell adjacency information.

Code | Name | Description
--- | --- | ---
`ed` | Edge Density | Total internal edge length (m) per hectare of buffer area. Higher values indicate a more fragmented landscape.
`te` | Total Edge | Total internal edge length in metres.
`lsi` | Landscape Shape Index | Total perimeter / minimum possible perimeter for the same number of cells. LSI = 1 for a perfectly compact (circular) patch; increases with irregularity.

## 2.3 Adjacency metrics

These metrics describe how often similar or dissimilar classes occur next to one another. They require a categorical raster and use cell-pair counts (the class-by-class co-occurrence matrix).

Code | Name | Description
--- | --- | ---
`ai` | Aggregation Index | Area-weighted aggregation of like adjacencies within classes. Higher values indicate that classes are more aggregated.
`pladj` | Proportion of Like Adjacencies | Percentage of cell-pair boundaries shared between cells of the same class. High values indicate a clumped or aggregated landscape.
`contag` | Contagion | Measures the degree of clumping across all class pairs. Ranges from 0 (maximum interspersion) to 100 (single class). Requires at least 2 classes.
`iji` | Interspersion & Juxtaposition | Evenness of adjacencies among different classes (like adjacencies are ignored). Ranges from near 0 (one class pair dominates the between-class boundaries) to 100 (every class is equally adjacent to every other). Requires at least 3 classes and enough between-class adjacencies in each buffer; otherwise it returns `NA`.

## 2.4 Information theory metrics

These metrics come from treating the class-pair co-occurrence matrix as a bivariate probability distribution, following Nowosad and Stepinski (2019). Their value is that they separate composition (how many classes, how evenly mixed) from configuration (how the classes are arranged), which the diversity and contagion metrics confound. They require a categorical raster. The `base` argument sets the logarithm base; use `base = 2` for bits, matching `landscapemetrics`.

Code | Name | Description
--- | --- | ---
`ent` | Marginal entropy, H(x) | Diversity of the cell values entering adjacencies. Increases with the number and evenness of classes; this is the composition signal.
`joinent` | Joint entropy, H(x, y) | Diversity of the class-pair adjacencies themselves: the total complexity of the pattern.
`condent` | Conditional entropy, H(y | x) | Configurational complexity remaining once composition is accounted for: the uncertainty about a neighbor’s class given the focal cell’s class.
`mutinf` | Mutual information, I(y, x) | How much a cell’s class tells you about its neighbor’s. Rises as like classes cluster; this is configuration separated from composition.
`relmutinf` | Relative mutual information | `mutinf / ent`, rescaled to 0–1 so configuration can be compared across landscapes of differing composition. Equal to 1 when `mutinf` is 0. Unaffected by `base`.

## 2.5 Class-level metrics

The metrics above summarize the whole landscape within the buffer. These three instead describe a single focal class, supplied through the `class` argument of `landscape_var()` (an integer matching one of the raster’s class codes). Asking for one of these metrics without a `class`, or supplying `class` to any other metric, is an error. Where the focal class is absent from a buffer, `pland` and `ca` return 0 and `clumpy` returns `NA`.

Code | Name | Description
--- | --- | ---
`clumpy` | Clumpiness Index | Aggregation of the focal class, corrected for its own abundance. Ranges from -1 (maximally disaggregated) through 0 (random) to 1 (maximally clumped).
`pland` | Percentage of Landscape | The focal class’s share of the valid buffer cells, as a percentage.
`ca` | Class Area | Area of the focal class within the buffer, in hectares.

    ## Clumpiness of land-cover class 2, and that class's percentage cover,
    ## both within a fixed 500 m radius
    class_vars <- msr_vars(
      cover2_clumpy = landscape_var("landcover", metric = "clumpy", radius = 500, class = 2),
      cover2_pland  = landscape_var("landcover", metric = "pland",  radius = 500, class = 2)
    )

    class_vars

# 3 Load example data

This example uses the simulated count data and survey locations included with `multiScaleR`. The data contain 100 spatial sample points, which is large enough to demonstrate the workflow without making the vignette expensive to build.

    data("landscape_counts")
    dat <- landscape_counts

    data("surv_pts")
    pts <- vect(surv_pts)

    land_rast <- rast(pkg_extdata("landscape.tif"))

The raster layer `land1` is a binary habitat layer. To demonstrate a categorical landscape-diversity metric, we also create a simple three-class land-cover layer from the continuous `land2` raster. In a real analysis, this would usually be a mapped categorical land-cover product.

    landcover <- classify(
      land_rast$land2,
      rcl = matrix(
        c(-Inf, -0.5, 1,
          -0.5,  0.5, 2,
           0.5,  Inf, 3),
        ncol = 3,
        byrow = TRUE
      )
    )
    names(landcover) <- "landcover"

    metric_rasters <- c(land_rast$land1, landcover)

    plot(metric_rasters)
    plot(metric_rasters$land1, main = "land1 with survey points")
    points(pts, pch = 19, cex = 0.6, col = "red")

# 4 Define derived covariates

Use `msr_vars()` to define model covariates as transformations of source raster layers. Here, `land1_prop` is optimized as a kernel-weighted covariate, while `land1_ed_500` and `landcover_shdi_500` are fixed-radius landscape metrics calculated within 500 m of each point.

    scale_vars <- msr_vars(
      land1_prop = kernel_var("land1"),
      land1_ed_500 = landscape_var("land1", metric = "ed", radius = 500),
      landcover_shdi_500 = landscape_var("landcover", metric = "shdi", radius = 500)
    )

    scale_vars

This is the key distinction:

- `land1` and `landcover` are source raster layers.
- `land1_prop`, `land1_ed_500`, and `landcover_shdi_500` are model covariates.
- Only `land1_prop` receives an optimized sigma parameter in this example.

# 5 Prepare model data

Pass the covariate specification to `kernel_prep()`. The returned `kernel_dat` data frame contains the derived covariates, not merely the original raster layer names.

    kernel_inputs <- kernel_prep(
      pts = pts,
      raster_stack = metric_rasters,
      max_D = 1200,
      kernel = "gaussian",
      scale_vars = scale_vars,
      verbose = FALSE
    )

    head(kernel_inputs$kernel_dat)

Combine the derived covariates with the response data and fit the starting model.

    df <- data.frame(dat, kernel_inputs$kernel_dat)

    mod <- glm(
      counts ~ site + land1_prop + land1_ed_500 + landcover_shdi_500,
      family = poisson(),
      data = df
    )

# 6 Optimize the kernel covariate

Because the two landscape metrics were defined with fixed radii, only `land1_prop` is optimized. This keeps the example fast while still showing how kernel-scaled and landscape-metric covariates can be included in the same model.

    opt <- multiScale_optim(
      fitted_mod = mod,
      kernel_inputs = kernel_inputs,
      verbose = FALSE
    )

    opt <- vignette_cache$landscape$opt
    summary(opt)
    #>
    #> Call:
    #> multiScale_optim(fitted_mod = landscape_mod, kernel_inputs = landscape_inputs,
    #>     verbose = FALSE)
    #>
    #>
    #> Kernel used:
    #>
    #>
    #> ***** Optimized Scale of Effect -- Sigma *****
    #>
    #>                Mean      SE     2.5%    97.5%
    #> land1_prop 179.1503 39.2233 101.2822 257.0184
    #>
    #>
    #>   ====================================
    #>
    #> ***** Optimized Scale of Effect -- Distance *****
    #> 90% Kernel Weight
    #>
    #>              Mean   2.5%  97.5%
    #> land1_prop 294.68 166.59 422.76
    #>
    #>
    #>   ====================================
    #>
    #>  *****     Fitted Model Summary     *****
    #>
    #>
    #> Call:
    #> glm(formula = counts ~ site + land1_prop + land1_ed_500 + landcover_shdi_500,
    #>     family = poisson(), data = data)
    #>
    #> Coefficients:
    #>                    Estimate Std. Error z value Pr(>|z|)
    #> (Intercept)         0.58563    0.07789   7.519 5.53e-14 ***
    #> site                0.19109    0.07762   2.462 0.013817 *
    #> land1_prop         -0.33519    0.08770  -3.822 0.000132 ***
    #> land1_ed_500       -0.11827    0.07755  -1.525 0.127223
    #> landcover_shdi_500 -0.14202    0.06091  -2.332 0.019723 *
    #> ---
    #> Signif. codes:  0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1
    #>
    #> (Dispersion parameter for poisson family taken to be 1)
    #>
    #>     Null deviance: 224.24  on 99  degrees of freedom
    #> Residual deviance: 180.00  on 95  degrees of freedom
    #> AIC: 386.67
    #>
    #> Number of Fisher Scoring iterations: 5
    #>
    #>
    #>
    #> ***** Follow-up recommendation *****
    #> Recommended `max_D`: 1200
    #> Recommended starting `sigma` values:
    #> land1_prop
    #>   179.1503
    #>
    #> Action:
    #> Use the optimized parameters as efficient starting values if refitting.

# 7 Project derived covariates to rasters

`kernel_scale.raster()` also understands `scale_vars`. When a fitted `multiScaleR` object is supplied, optimized covariates use their fitted scale and fixed-radius landscape metrics use their specified radius.

    projected <- terra::unwrap(vignette_cache$landscape$projected)

    plot(projected)

Projected derived covariates.

The resulting raster names match the model covariates:

    names(projected)
    #> [1] "land1_prop"         "land1_ed_500"       "landcover_shdi_500"
    #> [4] "site"

# 8 Producing landscape metric rasters without a fitted model

`kernel_scale.raster()` can generate landscape metric raster surfaces directly, without having fitted a model at all. This is useful when you want to explore how a metric varies across the landscape at a given scale, compare metrics side-by-side before committing to a model structure, or simply produce a covariate map from a classified raster.

Pass a `scale_vars` object in which all covariates have a fixed `radius` (i.e., `radius` is not `NULL` in `landscape_var()`). No `sigma` argument is needed because no scale is being optimized.

    ## Define several metrics at a fixed 500 m radius
    standalone_vars <- msr_vars(
      land1_ai    = landscape_var("land1",    metric = "ai",    radius = 500),
      land1_ed    = landscape_var("land1",    metric = "ed",    radius = 500),
      land1_lsi   = landscape_var("land1",    metric = "lsi",   radius = 500),
      land1_pladj = landscape_var("land1",    metric = "pladj", radius = 500),
      cover_shdi  = landscape_var("landcover", metric = "shdi",  radius = 500),
      cover_pr    = landscape_var("landcover", metric = "pr",    radius = 500),
      cover_sidi  = landscape_var("landcover", metric = "sidi",  radius = 500)
    )

    ## Apply directly: no multiScaleR object or sigma values required
    metric_surfaces <- kernel_scale.raster(
      raster_stack = metric_rasters,
      scale_vars   = standalone_vars,
      verbose      = FALSE
    )

    plot(metric_surfaces)

Each output layer is named after the covariate defined in `msr_vars()`:

    names(metric_surfaces)

You can also compute a single metric in one line without defining a `msr_vars()` object. Simply wrap a single `landscape_var()` call:

    ed_300 <- kernel_scale.raster(
      raster_stack = metric_rasters["land1"],
      scale_vars   = msr_vars(ed_300m = landscape_var("land1", metric = "ed", radius = 300)),
      verbose      = FALSE
    )

    plot(ed_300, main = "Edge density (m/ha) within 300 m")

Different radii produce notably different surfaces for the same metric. The example below computes edge density at three scales and plots them together for comparison:

    ed_multi <- kernel_scale.raster(
      raster_stack = metric_rasters["land1"],
      scale_vars   = msr_vars(
        ed_200m = landscape_var("land1", metric = "ed", radius = 200),
        ed_500m = landscape_var("land1", metric = "ed", radius = 500),
        ed_900m = landscape_var("land1", metric = "ed", radius = 900)
      ),
      verbose = FALSE
    )

    plot(ed_multi,
         main = c("ED: 200 m", "ED: 500 m", "ED: 900 m"))

## 8.1 Separating composition from configuration

The information-theory metrics are most useful when you want to ask whether an effect is driven by what is in the neighborhood (its composition) or by how it is arranged (its configuration). The surfaces below project three metrics for the three-class `landcover` layer at a fixed 500 m radius.

    info_surfaces <- kernel_scale.raster(
      raster_stack = metric_rasters["landcover"],
      scale_vars   = msr_vars(
        H_x    = landscape_var("landcover", metric = "ent",    radius = 500, base = 2),
        MI     = landscape_var("landcover", metric = "mutinf", radius = 500, base = 2),
        relMI  = landscape_var("landcover", metric = "relmutinf", radius = 500)
      ),
      verbose = FALSE
    )

    plot(info_surfaces, main = c("Marginal entropy (bits)",
                                 "Mutual information (bits)",
                                 "Relative mutual information"))

How to read these surfaces: marginal entropy (`ent`, here in bits because `base = 2`) is a composition measure: it is high where the buffer holds several classes in roughly equal proportion, and near 0 where one class dominates. Mutual information (`mutinf`) is a configuration measure: it is high where like classes cluster into contiguous patches and low where the classes are finely interspersed, independent of how many classes are present. Relative mutual information (`relmutinf`) divides the two, putting configuration on a 0 to 1 scale so it is comparable between neighborhoods that differ in composition. Two buffers can share the same `ent` yet have very different `mutinf`: same ingredients, different spatial arrangement. That separation is the reason to prefer these metrics over contagion when arrangement is the hypothesis of interest.

For a single class, `clumpy` answers the same configuration question on the -1 to 1 scale familiar from FRAGSTATS, while `pland` reports that class’s cover:

    class2_surfaces <- kernel_scale.raster(
      raster_stack = metric_rasters["landcover"],
      scale_vars   = msr_vars(
        clumpy2 = landscape_var("landcover", metric = "clumpy", radius = 500, class = 2),
        pland2  = landscape_var("landcover", metric = "pland",  radius = 500, class = 2)
      ),
      verbose = FALSE
    )

    plot(class2_surfaces, main = c("CLUMPY (class 2)", "PLAND (class 2, %)"))

# 9 Optimizing landscape metric radii

To optimize the scale of a landscape metric, omit `radius` from `landscape_var()`. For example:

    scale_vars_opt <- msr_vars(
      land1_prop = kernel_var("land1"),
      land1_ed = landscape_var("land1", metric = "ed"),
      landcover_shdi = landscape_var("landcover", metric = "shdi")
    )

This is statistically meaningful, but it is more computationally expensive than optimizing a kernel-weighted mean. At each candidate radius, the landscape metric must be recalculated for every sample point. For moderate or large data sets, consider first testing the workflow with a subset of points or using precomputed results in reproducible documents.

Before optimizing `iji`, `siei`, or `msiei`, inspect a pilot `kernel_prep()` result or compare a few fixed radii. These metrics can be all `NA` or nearly constant when buffers contain too few classes, too few between-class adjacencies, or nearly identical evenness at all sample points. In that case, use a larger radius, increase `max_D`, or choose a more stable diversity, entropy, or edge metric.

# 10 Practical guidance

Use fixed-radius landscape metrics when you have a biologically motivated buffer distance or when the metric is expensive to recompute. Use optimized landscape metric radii when the scale itself is a central question and computation time is acceptable.

At present, optimized landscape metrics are not supported with `kernel = "expow"` because the exponential-power shape parameter does not apply cleanly to fixed-buffer landscape metrics.

# 11 See also

- `vignette("surface_metric_covariates", package = "multiScaleR")` for the continuous-surface analogue of these metrics (roughness, gradient, and texture of a continuous raster).
- `vignette("multiScaleR_Guide", package = "multiScaleR")` for the core kernel-weighting workflow.
- The help page `?msr_vars` lists every supported metric with its definition.

# 12 References

Nowosad, J., & Stepinski, T. F. (2019). Information theory as a consistent framework for quantification and classification of landscape patterns. Landscape Ecology, 34(9), 2091–2101. https://doi.org/10.1007/s10980-019-00830-x