Package 'spacc'

Description

Abundance-based Coverage Estimator (ACE) of total species richness (Chao & Lee 1992). Separates species into rare and abundant groups based on an abundance threshold.

Usage

ace(x, threshold = 10L)

Arguments

Details

ACE partitions species into rare (abundance $\le$ threshold) and abundant (abundance > threshold) groups. The estimate is:

$S_{ACE} = S_{abund} + \frac{S_{rare}}{C_{ACE}} + \frac{f_1}{C_{ACE}} \gamma^2$

where $C_{ACE}$ is the sample coverage of rare species and $\gamma^2$ is the estimated coefficient of variation.

Value

An object of class spacc_estimate.

References

Chao, A. & Lee, S.M. (1992). Estimating the number of classes via sample coverage. Journal of the American Statistical Association, 87, 210-217.

See Also

chao1(), chao2()

Examples

species <- matrix(rpois(50 * 30, 2), nrow = 50)
ace(species)

Description

Compute Hill numbers for each site individually.

Usage

alphaDiversity(x, q = c(0, 1, 2), coords = NULL)

Arguments

Details

Alpha diversity represents local (within-site) diversity. For Hill numbers:

• q=0: Species richness

• q=1: Exponential of Shannon entropy

• q=2: Inverse Simpson concentration

Value

If coords is NULL, a data.frame with columns for each q value. If coords is provided, a spacc_alpha object.

References

Jost, L. (2007). Partitioning diversity into independent alpha and beta components. Ecology, 88, 2427-2439.

See Also

gammaDiversity() for regional diversity, diversityPartition() for full alpha-beta-gamma decomposition

Examples

species <- matrix(rpois(50 * 30, 2), nrow = 50)
alpha <- alphaDiversity(species, q = c(0, 1, 2))
head(alpha)

# Mean alpha diversity
colMeans(alpha)

Description

These methods compute expected species accumulation without simulation. They are faster but don't provide spatial information.

Description

Convert metrics to an sf object for spatial analysis and integration with the areaOfEffect package.

Usage

as_sf(x, crs = NULL)

Arguments

Value

An sf object with POINT geometries and metric columns.

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
metrics <- spaccMetrics(species, coords)
if (requireNamespace("sf", quietly = TRUE)) {
  metrics_sf <- as_sf(metrics)
}

Description

ggplot2::autoplot() methods for spacc objects. These are thin wrappers around the corresponding plot() methods, provided for ggplot2 integration.

Arguments

Value

A ggplot2 object.

Examples

if (requireNamespace("ggplot2", quietly = TRUE)) {
  coords <- data.frame(x = runif(30), y = runif(30))
  species <- matrix(rbinom(30 * 15, 1, 0.3), nrow = 30)
  sac <- spacc(species, coords, n_seeds = 5, progress = FALSE)
  ggplot2::autoplot(sac)
}

Description

Compute the distance-decay of community similarity by fitting models to pairwise beta dissimilarity as a function of geographic distance.

Usage

betaDecay(
  x,
  coords,
  index = c("sorensen", "jaccard"),
  model = c("all", "exponential", "power", "linear"),
  distance = c("euclidean", "haversine"),
  n_bins = 50L,
  progress = TRUE
)

Arguments

Details

Three decay models are available:

• Exponential: $\beta = 1 - a \cdot e^{-b \cdot d}$

• Power: $\beta = a \cdot d^b$

• Linear: $\beta = a + b \cdot d$

The half-life (exponential model) is the distance at which similarity decays to half its initial value: $d_{1/2} = \ln(2) / b$.

Value

An object of class spacc_beta_decay containing:

References

Nekola, J.C. & White, P.S. (1999). The distance decay of similarity in biogeography and ecology. Journal of Biogeography, 26, 867-878.

Morlon, H., Chuyong, G., Condit, R., et al. (2008). A general framework for the distance-decay of similarity in ecological communities. Ecology Letters, 11, 904-917.

See Also

spaccBeta() for spatial beta diversity accumulation, distanceDecay() for species similarity decay

Examples

coords <- data.frame(x = runif(30), y = runif(30))
species <- matrix(rbinom(30 * 20, 1, 0.3), nrow = 30)

bd <- betaDecay(species, coords)
print(bd)
plot(bd)

Description

Bootstrap estimator of total species richness (Smith & van Belle 1984). Uses species detection probabilities to estimate undetected species.

Usage

bootstrap_richness(x, n_boot = 200L)

Arguments

Details

The bootstrap estimator is:

$S_{boot} = S_{obs} + \sum_{i=1}^{S_{obs}} (1 - p_i)^n$

where $p_i$ is the proportion of sites where species $i$ occurs.

Value

An object of class spacc_estimate.

References

Smith, E.P. & van Belle, G. (1984). Nonparametric estimation of species richness. Biometrics, 40, 119-129.

See Also

jackknife(), chao2()

Examples

species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
bootstrap_richness(species, n_boot = 100)

Description

Combine spacc Objects

Usage

## S3 method for class 'spacc'
c(...)

Arguments

Value

A grouped spacc object with per-group curves.

Description

Combine multiple spacc_beta objects by stacking their curve matrices. All objects must have the same number of sites and index.

Usage

## S3 method for class 'spacc_beta'
c(...)

Arguments

Value

A combined spacc_beta object with more seeds.

Description

Combine multiple spacc_coverage objects by stacking their curve matrices. All objects must have the same number of sites.

Usage

## S3 method for class 'spacc_coverage'
c(...)

Arguments

Value

A combined spacc_coverage object with more seeds.

Description

Combine multiple spacc_hill objects by stacking their curve matrices. All objects must have the same number of sites.

Usage

## S3 method for class 'spacc_hill'
c(...)

Arguments

Value

A combined spacc_hill object with more seeds.

Description

Estimate total species richness from abundance data using the Chao1 estimator (Chao 1984). Uses the number of singletons and doubletons to estimate undetected species.

Usage

chao1(x)

Arguments

Details

The Chao1 estimator is:

$S_{Chao1} = S_{obs} + \frac{f_1^2}{2 f_2}$

where $f_1$ is the number of singletons (species with total abundance 1) and $f_2$ is the number of doubletons (abundance 2).

When $f_2 = 0$, the bias-corrected form is used:

$S_{Chao1} = S_{obs} + \frac{f_1 (f_1 - 1)}{2}$

Value

An object of class spacc_estimate with components:

estimator

Name of the estimator ("chao1")

estimate

Estimated total richness

se

Standard error of the estimate

lower

Lower 95 percent confidence bound

upper

Upper 95 percent confidence bound

S_obs

Observed species richness

details

List with f1 (singletons) and f2 (doubletons)

References

Chao, A. (1984). Nonparametric estimation of the number of classes in a population. Scandinavian Journal of Statistics, 11, 265-270.

Chao, A. (1987). Estimating the population size for capture-recapture data with unequal catchability. Biometrics, 43, 783-791.

See Also

chao2() for incidence-based estimation, ace() for abundance-based coverage estimator

Examples

species <- matrix(rpois(50 * 30, 2), nrow = 50)
chao1(species)

Description

Estimate total species richness from incidence (presence/absence) data using the Chao2 estimator (Chao 1987).

Usage

chao2(x)

Arguments

Details

The Chao2 estimator is the incidence-based analogue of Chao1:

$S_{Chao2} = S_{obs} + \frac{Q_1^2}{2 Q_2}$

where $Q_1$ is the number of uniques (species found at exactly 1 site) and $Q_2$ is the number of duplicates (species found at exactly 2 sites).

Value

An object of class spacc_estimate.

References

Chao, A. (1987). Estimating the population size for capture-recapture data with unequal catchability. Biometrics, 43, 783-791.

See Also

chao1() for abundance-based estimation

Examples

species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
chao2(species)

Description

Compute the expected species accumulation curve using the Coleman method (Coleman et al. 1982). This is an analytical formula, no simulation needed.

Usage

coleman(x)

Arguments

Value

A data.frame with columns: sites, expected, sd

References

Coleman, B.D., Mares, M.A., Willig, M.R. & Hsieh, Y.H. (1982). Randomness, area, and species richness. Ecology, 63, 1121-1133.

Description

Compute the species accumulation curve in the order sites appear in the data (no randomization). Useful for understanding how data was collected.

Usage

collector(x)

Arguments

Value

A data.frame with columns: sites, species

Description

Test whether two species accumulation curves differ significantly.

Usage

compare(
  x,
  y,
  method = c("permutation", "bootstrap", "auc"),
  normalize = FALSE,
  n_perm = 999L,
  ...
)

Arguments

Value

An object of class spacc_comp containing:

References

Colwell, R.K., Mao, C.X. & Chang, J. (2004). Interpolating, extrapolating, and comparing incidence-based species accumulation curves. Ecology, 85, 2717-2727.

Gotelli, N.J. & Colwell, R.K. (2011). Estimating species richness. In: Biological Diversity: Frontiers in Measurement and Assessment, pp. 39-54. Oxford University Press.

Examples

coords <- data.frame(x = runif(50), y = runif(50))
sp_a <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
sp_b <- matrix(rbinom(50 * 30, 1, 0.5), nrow = 50)

sac_a <- spacc(sp_a, coords, n_seeds = 10)
sac_b <- spacc(sp_b, coords, n_seeds = 10)
comp <- compare(sac_a, sac_b)
print(comp)

Description

Fit all (or a subset of) asymptotic species-area models and compare them using AIC, BIC, delta-AIC, and Akaike weights.

Usage

compareModels(
  object,
  models = c("michaelis-menten", "lomolino", "asymptotic", "weibull", "logistic", "evt"),
  ...
)

Arguments

Value

An object of class spacc_model_compare containing:

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
sac <- spacc(species, coords)
cm <- compareModels(sac)
print(cm)

Description

Compute the ratio of observed to estimated diversity across diversity orders, measuring how complete a sample is at each level of the Hill number spectrum.

Usage

completenessProfile(x, q = seq(0, 2, by = 0.2), coords = NULL)

Arguments

Details

Sample completeness at order q is:

$C_q = \frac{D_q^{obs}}{D_q^{est}}$

where $D_q^{obs}$ is the observed Hill number and $D_q^{est}$ is the estimated asymptotic Hill number.

Completeness near 1 means the sample captures most of the true diversity at that order. Completeness typically increases with q because dominant species are detected early.

Asymptotic estimators used:

• q = 0: Chao1 estimator

• q = 1: Chao & Jost (2015) entropy estimator

• q = 2: Inverse Simpson estimator with bias correction

• Other q: Interpolated between adjacent integer estimates

When coords is provided, per-site completeness is computed by treating each site's abundance vector as an independent sample.

Value

An object of class spacc_completeness containing:

References

Chao, A. & Jost, L. (2012). Coverage-based rarefaction and extrapolation: standardizing samples by completeness rather than size. Ecology, 93, 2533-2547.

Chao, A. & Jost, L. (2015). Estimating diversity and entropy profiles via discovery rates of new species. Methods in Ecology and Evolution, 6, 873-882.

See Also

diversityProfile() for observed diversity profiles, chao1() for richness estimation

Examples

species <- matrix(rpois(50 * 30, 2), nrow = 50)
comp <- completenessProfile(species)
print(comp)


plot(comp)

Description

Extend the classic species-area relationship (SAR) to a diversity-area relationship using Hill numbers of any order q. Instead of plotting species richness vs. sites, this plots effective diversity vs. cumulative area.

Usage

dar(
  x,
  coords,
  q = c(0, 1, 2),
  n_seeds = 50L,
  method = "knn",
  area_method = c("convex_hull", "voronoi", "count"),
  distance = c("euclidean", "haversine"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL
)

Arguments

Details

The DAR (Ma, 2018) generalizes the SAR by replacing species richness (q=0) with Hill numbers of any order. This reveals how different facets of diversity scale with area:

• q=0 (richness) recovers the classic SAR

• q=1 (Shannon) shows how common species diversity scales

• q=2 (Simpson) shows how dominant species diversity scales

Value

An object of class spacc_dar containing:

References

Ma, Z.S. (2018). DAR (diversity-area relationship): extending classic SAR for biodiversity and biogeography analyses. Ecology and Evolution, 8, 10023-10038.

Arrhenius, O. (1921). Species and area. Journal of Ecology, 9, 95-99.

See Also

spaccHill(), extrapolate()

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rpois(50 * 30, 2), nrow = 50)

dar <- dar(species, coords, q = c(0, 1, 2))
plot(dar)

Description

Analyze how species richness changes with distance from focal points.

Usage

distanceDecay(
  x,
  coords,
  n_seeds = 50L,
  breaks = NULL,
  distance = c("euclidean", "haversine"),
  progress = TRUE,
  seed = NULL
)

Arguments

Value

An object of class spacc_decay with distance-species relationships.

References

Nekola, J.C. & White, P.S. (1999). The distance decay of similarity in biogeography and ecology. Journal of Biogeography, 26, 867-878.

Soininen, J., McDonald, R. & Hillebrand, H. (2007). The distance decay of similarity in ecological communities. Ecography, 30, 3-12.

Description

Pre-compute pairwise distances between sites for reuse across multiple spacc() calls. Supports sf objects with accurate geodesic distances for global-scale studies.

Usage

distances(x, method = NULL, fun = NULL, which = NULL)

Arguments

Details

For continental and global-scale studies, use sf objects with geographic CRS (e.g., EPSG:4326). The function will automatically use accurate geodesic distances via the S2 spherical geometry library.

For smaller study areas with projected coordinates (UTM, etc.), Euclidean distance is appropriate and faster.

Value

An object of class spacc_dist containing the distance matrix with coordinates stored as an attribute.

Examples

coords <- data.frame(x = runif(50), y = runif(50))
d <- distances(coords)

# Reuse for multiple analyses
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
sac <- spacc(species, d)

Description

Decompose regional (gamma) diversity into local (alpha) and turnover (beta) components using multiplicative partitioning of Hill numbers.

Usage

diversityPartition(x, q = c(0, 1, 2), weights = "equal", coords = NULL)

Arguments

Details

This function implements Jost (2007) multiplicative partitioning:

$\gamma = \alpha \times \beta$

Where:

• Alpha: Mean effective number of species per site

• Beta: Effective number of distinct communities (1 = all identical, n_sites = all completely different)

• Gamma: Total effective number of species in the region

Beta diversity is interpreted as the effective number of communities:

• Beta = 1: All sites have identical composition

• Beta = n_sites: Sites share no species

Value

An object of class spacc_partition containing:

References

Jost, L. (2007). Partitioning diversity into independent alpha and beta components. Ecology, 88, 2427-2439.

Chao, A., Chiu, C.H. & Jost, L. (2014). Unifying species diversity, phylogenetic diversity, functional diversity, and related similarity and differentiation measures through Hill numbers. Annual Review of Ecology, Evolution, and Systematics, 45, 297-324.

See Also

alphaDiversity(), gammaDiversity(), spaccBeta() for spatial beta diversity accumulation

Examples

# Simulated community data
species <- matrix(rpois(50 * 30, 2), nrow = 50)

# Partition diversity
part <- diversityPartition(species, q = c(0, 1, 2))
print(part)

# Beta near 1 = homogeneous region
# Beta near n_sites = heterogeneous region

Description

Compute Hill numbers across a continuous range of diversity orders (q), producing a diversity profile for each site and the regional pool.

Usage

diversityProfile(
  x,
  q = seq(0, 3, by = 0.1),
  type = c("both", "per_site", "regional"),
  coords = NULL
)

Arguments

Details

A diversity profile plots effective number of species as a function of the order q. The key property is that Hill numbers are non-increasing in q: $D_q \ge D_{q'}$ for $q \le q'$.

• q = 0: Species richness (insensitive to abundance)

• q = 1: Exponential of Shannon entropy (all species weighted equally by their proportional abundance)

• q = 2: Inverse Simpson concentration (emphasizes dominant species)

• q > 2: Increasingly dominated by common species

Value

An object of class spacc_profile containing:

References

Leinster, T. & Cobbold, C.A. (2012). Measuring diversity: the importance of species similarity. Ecology, 93, 477-489.

Chao, A., Chiu, C.H. & Jost, L. (2014). Unifying species diversity, phylogenetic diversity, functional diversity, and related similarity and differentiation measures through Hill numbers. Annual Review of Ecology, Evolution, and Systematics, 45, 297-324.

See Also

alphaDiversity() for per-site values at specific q, gammaDiversity() for regional diversity, evenness() for evenness profiles

Examples

species <- matrix(rpois(50 * 30, 2), nrow = 50)
prof <- diversityProfile(species)
print(prof)


plot(prof)

Description

Compute functional Hill numbers (Leinster & Cobbold 2012) across a continuous range of diversity orders (q), producing a functional diversity profile based on trait similarity.

Usage

diversityProfileFunc(
  x,
  traits,
  q = seq(0, 3, by = 0.1),
  type = c("both", "per_site", "regional"),
  dist_method = c("euclidean", "gower"),
  normalize = TRUE,
  coords = NULL
)

Arguments

Details

Functional Hill numbers (Leinster & Cobbold 2012) incorporate trait similarity via a similarity matrix Z = 1 - D. When all species are maximally dissimilar (Z = identity), this reduces to standard Hill numbers.

Value

An object of class spacc_profile with ⁠$profile_type = "functional"⁠.

References

Leinster, T. & Cobbold, C.A. (2012). Measuring diversity: the importance of species similarity. Ecology, 93, 477-489.

See Also

diversityProfile() for taxonomic profiles, diversityProfilePhylo() for phylogenetic profiles

Examples

species <- matrix(rpois(20 * 10, 2), nrow = 20,
                  dimnames = list(NULL, paste0("sp", 1:10)))
traits <- data.frame(
  body_size = rnorm(10), diet = rnorm(10),
  row.names = paste0("sp", 1:10)
)
prof <- diversityProfileFunc(species, traits)
print(prof)

Description

Compute phylogenetic Hill numbers (Chao et al. 2010) across a continuous range of diversity orders (q), producing a phylogenetic diversity profile.

Usage

diversityProfilePhylo(
  x,
  tree,
  q = seq(0, 3, by = 0.1),
  type = c("both", "per_site", "regional"),
  coords = NULL
)

Arguments

Details

Phylogenetic Hill numbers (Chao et al. 2010) weight branches by their evolutionary distance. At q=0 this approximates normalized Faith's PD. Higher q values increasingly emphasize common lineages.

Value

An object of class spacc_profile with ⁠$profile_type = "phylogenetic"⁠.

References

Chao, A., Chiu, C.H. & Jost, L. (2010). Phylogenetic diversity measures based on Hill numbers. Philosophical Transactions of the Royal Society B, 365, 3599-3609.

See Also

diversityProfile() for taxonomic profiles, diversityProfileFunc() for functional profiles

Examples

if (requireNamespace("ape", quietly = TRUE)) {
  species <- matrix(rpois(20 * 10, 2), nrow = 20,
                    dimnames = list(NULL, paste0("sp", 1:10)))
  tree <- ape::rcoal(10, tip.label = paste0("sp", 1:10))
  prof <- diversityProfilePhylo(species, tree)
  print(prof)
}

Description

Compute species evenness across sites using Hill-based, Pielou, or Simpson evenness measures.

Usage

evenness(
  x,
  q = seq(0.1, 3, by = 0.1),
  type = c("hill", "pielou", "simpson"),
  coords = NULL
)

Arguments

Details

All evenness measures are bounded in $[0, 1]$:

• 0 = maximally uneven (one dominant species)

• 1 = perfectly even (all species equally abundant)

Hill evenness (Jost 2010):

$E_q = D_q / D_0$

This divides the effective number of species at order q by species richness.

Pielou's J (Pielou 1966):

$J = \frac{\log(D_1)}{\log(S)} = \frac{H'}{\log(S)}$

Simpson evenness:

$E_{1/D} = \frac{1}{D_2 \cdot S}$

Value

An object of class spacc_evenness containing:

References

Jost, L. (2010). The relation between evenness and diversity. Diversity, 2, 207-232.

Pielou, E.C. (1966). The measurement of diversity in different types of biological collections. Journal of Theoretical Biology, 13, 131-144.

See Also

diversityProfile() for Hill number profiles, alphaDiversity() for raw diversity values

Examples

species <- matrix(rpois(50 * 30, 2), nrow = 50)

# Hill evenness profile
ev <- evenness(species)
print(ev)

# Pielou's J
ev_j <- evenness(species, type = "pielou")
print(ev_j)

Description

Fit an asymptotic model to estimate total species richness beyond the observed sampling effort.

Usage

extrapolate(
  object,
  model = c("michaelis-menten", "lomolino", "asymptotic", "weibull", "logistic", "evt"),
  ...
)

Arguments

Value

An object of class spacc_fit containing:

References

Lomolino, M.V. (2000). Ecology's most general, yet protean pattern: the species-area relationship. Journal of Biogeography, 27, 17-26.

Flather, C.H. (1996). Fitting species-accumulation functions and assessing regional land use impacts on avian diversity. Journal of Biogeography, 23, 155-168.

Borda-de-Agua, L., Whittaker, R.J., Cardoso, P., et al. (2025). Extreme value theory explains the topography and scaling of the species-area relationship. Nature Communications, 16, 5346.

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
sac <- spacc(species, coords)
fit <- extrapolate(sac)
print(fit)

Description

Predict species richness at coverage levels beyond the empirical maximum, following the Chao et al. (2014) framework. Provides seamless interpolation and extrapolation as a function of sample coverage.

Usage

extrapolateCoverage(x, target_coverage = c(0.9, 0.95, 0.99), q = 0)

Arguments

Details

For targets within observed coverage, linear interpolation is used. For targets beyond observed coverage, asymptotic estimators are applied:

• q = 0: Chao1 estimator: S_est = S_obs + f1^2 / (2 * f2), where f1/f2 are singleton/doubleton counts. Extrapolation via coverage deficit.

• q = 1: Shannon extrapolation based on the Good-Turing frequency formula.

• q = 2: Simpson extrapolation using the unbiased estimator.

Value

An object of class spacc_coverage_ext containing:

References

Chao, A. & Jost, L. (2012). Coverage-based rarefaction and extrapolation: standardizing samples by completeness rather than size. Ecology, 93, 2533-2547.

Chao, A., Gotelli, N.J., Hsieh, T.C., et al. (2014). Rarefaction and extrapolation with Hill numbers: a framework for sampling and estimation in species diversity studies. Ecological Monographs, 84, 45-67.

See Also

spaccCoverage(), interpolateCoverage()

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rpois(50 * 30, 2), nrow = 50)
cov <- spaccCoverage(species, coords)
ext <- extrapolateCoverage(cov, target_coverage = c(0.95, 0.99))
print(ext)

Description

Compute Hill numbers for the pooled community across all sites.

Usage

gammaDiversity(x, q = c(0, 1, 2))

Arguments

Details

Gamma diversity represents regional (total) diversity across all sites. It is computed by pooling abundances across all sites and calculating Hill numbers on the combined community.

Value

A named numeric vector with gamma diversity for each q.

References

Jost, L. (2007). Partitioning diversity into independent alpha and beta components. Ecology, 88, 2427-2439.

See Also

alphaDiversity() for local diversity, diversityPartition() for full alpha-beta-gamma decomposition

Examples

species <- matrix(rpois(50 * 30, 2), nrow = 50)
gammaDiversity(species, q = c(0, 1, 2))

Description

Estimate total species richness using the improved Chao1 estimator (Chiu et al. 2014). Uses singletons through quadrupletons (f1–f4) to reduce bias for small samples.

Usage

iChao1(x)

Arguments

Details

The improved Chao1 estimator adds a correction term using f3 and f4:

$S_{iChao1} = S_{Chao1} + \frac{f_3}{4 f_4} \max\left(f_1 - \frac{f_2 f_3}{2 f_4}, 0\right)$

When $f_4 = 0$, the estimator collapses to Chao1.

Value

An object of class spacc_estimate with components:

estimator

Name of the estimator ("iChao1")

estimate

Estimated total richness

se

Standard error of the estimate

lower

Lower 95 percent confidence bound

upper

Upper 95 percent confidence bound

S_obs

Observed species richness

details

List with f1, f2, f3, f4

References

Chiu, C.H., Wang, Y.T., Walther, B.A. & Chao, A. (2014). An improved nonparametric lower bound of species richness via a modified Good-Turing frequency formula. Biometrics, 70, 671-682.

See Also

chao1() for the standard estimator, iChao2() for incidence-based version

Examples

species <- matrix(rpois(50 * 30, 2), nrow = 50)
iChao1(species)

Description

Estimate total species richness from incidence data using the improved Chao2 estimator (Chiu et al. 2014). Uses uniques through quadruplicates (Q1–Q4) to reduce bias for small samples.

Usage

iChao2(x)

Arguments

Details

The improved Chao2 estimator is the incidence-based analogue of iChao1:

$S_{iChao2} = S_{Chao2} + \frac{Q_3}{4 Q_4} \max\left(Q_1 - \frac{Q_2 Q_3}{2 Q_4}, 0\right)$

When $Q_4 = 0$, the estimator collapses to Chao2.

Value

An object of class spacc_estimate with components:

estimator

Name of the estimator ("iChao2")

estimate

Estimated total richness

se

Standard error of the estimate

lower

Lower 95 percent confidence bound

upper

Upper 95 percent confidence bound

S_obs

Observed species richness

details

List with Q1, Q2, Q3, Q4, n_sites

References

Chiu, C.H., Wang, Y.T., Walther, B.A. & Chao, A. (2014). An improved nonparametric lower bound of species richness via a modified Good-Turing frequency formula. Biometrics, 70, 671-682.

See Also

chao2() for the standard estimator, iChao1() for abundance-based version

Examples

species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
iChao2(species)

Description

Estimate species richness at specified coverage levels by interpolation.

Usage

interpolateCoverage(x, target = c(0.9, 0.95, 0.99))

Arguments

Value

A data.frame with columns for each target coverage level, showing interpolated richness for each seed.

References

Chao, A. & Jost, L. (2012). Coverage-based rarefaction and extrapolation: standardizing samples by completeness rather than size. Ecology, 93, 2533-2547.

Description

First- or second-order jackknife estimator of total species richness (Burnham & Overton 1978, 1979).

Usage

jackknife(x, order = 1L)

Arguments

Details

First-order jackknife:

$S_{jack1} = S_{obs} + Q_1 \frac{n-1}{n}$

Second-order jackknife:

$S_{jack2} = S_{obs} + \frac{Q_1(2n-3)}{n} - \frac{Q_2(n-2)^2}{n(n-1)}$

Value

An object of class spacc_estimate.

References

Burnham, K.P. & Overton, W.S. (1978). Estimation of the size of a closed population when capture probabilities vary among animals. Biometrika, 65, 625-633.

Burnham, K.P. & Overton, W.S. (1979). Robust estimation of population size when capture probabilities vary among animals. Ecology, 60, 927-936.

See Also

chao2(), bootstrap_richness()

Examples

species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
jackknife(species, order = 1)
jackknife(species, order = 2)

Description

Compute the expected species accumulation curve using sample-based rarefaction (Mao Tau estimator). This is analytically identical to the expected curve from random permutations.

Usage

mao_tau(x)

Arguments

Value

A data.frame with columns: sites, expected, sd, lower, upper

References

Colwell, R.K., Mao, C.X. & Chang, J. (2004). Interpolating, extrapolating, and comparing incidence-based species accumulation curves. Ecology, 85, 2717-2727.

Description

Create a ggplot2 visualization of species accumulation curves. For grouped spacc objects, curves are overlaid with different colors.

Usage

## S3 method for class 'spacc'
plot(
  x,
  ci = TRUE,
  ci_level = 0.95,
  ci_alpha = 0.3,
  show_seeds = FALSE,
  saturation = FALSE,
  saturation_level = 0.9,
  facet = FALSE,
  ...
)

Arguments

Value

A ggplot2 object.

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
sac <- spacc(species, coords)
plot(sac)

Description

Create visualizations of per-site accumulation metrics.

Usage

## S3 method for class 'spacc_metrics'
plot(
  x,
  metric = NULL,
  type = c("heatmap", "points", "histogram"),
  point_size = 3,
  palette = "viridis",
  ...
)

Arguments

Value

A ggplot2 object.

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
metrics <- spaccMetrics(species, coords, metrics = c("slope_10", "auc"))
plot(metrics, metric = "slope_10", type = "heatmap")

Description

Interpolate the mean empirical accumulation curve at arbitrary site counts using linear interpolation. Unlike the predict method for spacc_fit objects, this does not use a fitted model; it interpolates the observed curve directly.

Usage

## S3 method for class 'spacc'
predict(object, n = NULL, ci = TRUE, ci_level = 0.95, warn = TRUE, ...)

Arguments

Value

A data frame (if ci = TRUE) or named numeric vector (if ci = FALSE). Out-of-range values return NA.

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
sac <- spacc(species, coords, n_seeds = 10, progress = FALSE)
predict(sac, n = c(10, 25, 50))
predict(sac, n = c(10, 25), ci = FALSE)

Description

Compute individual-based rarefaction curves for Hill numbers at any order q. This complements the sample-based accumulation in spacc().

Usage

rarefy(x, n_individuals = NULL, q = 0, n_boot = 100L)

Arguments

Details

For q=0 (species richness): uses the Hurlbert (1971) formula.

For q=1 (Shannon diversity): rarefied Shannon entropy is computed and converted to effective number of species via exponentiation.

For q=2 (Simpson diversity): rarefied Simpson concentration is computed and converted to effective number of species via inversion.

Value

An object of class spacc_rare containing:

References

Hurlbert, S.H. (1971). The nonconcept of species diversity: a critique and alternative parameters. Ecology, 52, 577-586.

Chao, A., Gotelli, N.J., Hsieh, T.C., et al. (2014). Rarefaction and extrapolation with Hill numbers: a framework for sampling and estimation in species diversity studies. Ecological Monographs, 84, 45-67.

Examples

abundance_matrix <- matrix(rpois(50 * 30, 2), nrow = 50)
rare <- rarefy(abundance_matrix)
plot(rare)

# Shannon rarefaction
rare_q1 <- rarefy(abundance_matrix, q = 1)
plot(rare_q1)

Description

Compute standardized effect sizes by comparing observed diversity metrics against a null distribution from randomized communities. Supports multiple null model algorithms and works with most spacc output classes.

Usage

ses(
  x,
  species,
  coords = NULL,
  metric = NULL,
  null_model = c("frequency", "richness", "both", "curveball", "torus", "spatial_swap"),
  n_perm = 999L,
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL
)

Arguments

Details

SES is computed as:

$SES = \frac{observed - \bar{null}}{sd_{null}}$

A two-tailed p-value is calculated as the proportion of null values at least as extreme as the observed value:

$p = \frac{2 \cdot \min(r, n_{perm} + 1 - r)}{n_{perm} + 1}$

where $r$ is the rank of the observed value among null values.

Null model algorithms:

• "frequency": Tests whether species composition matters given observed species frequencies

• "richness": Tests whether species identity matters given observed site richness

• "both": Maintains both marginal totals; tests non-random species co-occurrence patterns

• "curveball": Efficient alternative to "both" with proven uniform sampling properties

Value

An object of class spacc_ses containing:

References

Gotelli, N.J. (2000). Null model analysis of species co-occurrence patterns. Ecology, 81, 2606-2621.

Strona, G., Nappo, D., Boccacci, F., Fattorini, S. & San-Miguel-Ayanz, J. (2014). A fast and unbiased procedure to randomize ecological binary matrices with fixed row and column totals. Nature Communications, 5, 4114.

See Also

spaccHill(), spaccBeta(), spaccMetrics()

Examples

coords <- data.frame(x = runif(20), y = runif(20))
species <- matrix(rbinom(20 * 15, 1, 0.3), nrow = 20)

sac <- spacc(species, coords, n_seeds = 10)
result <- ses(sac, species, n_perm = 19)
print(result)

Description

Model the joint effect of sampling effort and area on species richness. Corrects for unequal survey intensity across sites, common in atlas data and citizen science datasets.

Usage

sesars(object, effort, model = c("power", "additive"), ...)

Arguments

Details

Standard SARs assume complete sampling within each area unit. SESARS incorporates sampling effort (E) alongside area (A) to provide unbiased richness estimates across regions with unequal survey intensity.

Value

An object of class spacc_sesars containing:

References

Dennstadt, F., Horak, J. & Martin, M.D. (2019). Predictive sampling effort and species-area relationship models for estimating richness in fragmented landscapes. Diversity and Distributions, 26, 1112-1123.

See Also

extrapolate(), spacc()

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
sac <- spacc(species, coords)
effort <- rpois(50, 10)
ses <- sesars(sac, effort, model = "power")
print(ses)

Description

Separate the effects of habitat loss (area reduction) from fragmentation (splitting into patches) on species richness. Extends the classic power-law SAR with an explicit fragmentation term.

Usage

sfar(object, patches, model = c("power", "log"), ...)

Arguments

Details

The SFAR (Hanski et al. 2013) extends the power-law SAR to quantify the additional effect of habitat fragmentation on species richness. The model S = c * A^z * n^(-f) adds a penalty term for fragmentation (n = number of fragments), where f > 0 indicates that fragmentation reduces richness beyond what area loss alone would predict.

Value

An object of class spacc_sfar containing:

References

Hanski, I., Zurita, G.A., Bellocq, M.I. & Rybicki, J. (2013). Species-fragmented area relationship. Proceedings of the National Academy of Sciences, 110, 12715-12720.

Rybicki, J. & Hanski, I. (2013). Species-area relationships and extinctions caused by habitat loss and fragmentation. Ecology Letters, 16, 27-38.

See Also

extrapolate(), sesars()

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
sac <- spacc(species, coords)
patches <- kmeans(coords, centers = 5)$cluster
sfar_result <- sfar(sac, patches)
print(sfar_result)

Description

Compute species accumulation curves using various spatial sampling methods with C++ backend for performance.

Usage

spacc(
  x,
  coords,
  n_seeds = 50L,
  method = c("knn", "kncn", "random", "radius", "gaussian", "cone", "collector"),
  distance = c("euclidean", "haversine"),
  backend = c("auto", "exact", "kdtree"),
  support = NULL,
  include_halo = TRUE,
  sigma = NULL,
  cone_width = pi/4,
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  groups = NULL,
  time = NULL,
  w_space = 1,
  w_time = 1,
  seed = NULL,
  order = NULL
)

Arguments

Value

When groups = NULL, an object of class spacc containing:

References

Arrhenius, O. (1921). Species and area. Journal of Ecology, 9, 95-99.

Scheiner, S.M. (2003). Six types of species-area curves. Global Ecology and Biogeography, 12, 441-447.

Chiarucci, A., Bacaro, G., Scheiner, S.M. (2011). Old and new challenges in using species diversity for assessing biodiversity. Philosophical Transactions of the Royal Society B, 366, 2426-2437.

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)

# Basic usage
sac <- spacc(species, coords)
plot(sac)

# Different methods
sac_knn <- spacc(species, coords, method = "knn")
sac_rand <- spacc(species, coords, method = "random")
comp <- compare(sac_knn, sac_rand)

Description

Analyze how beta diversity changes as sites are accumulated spatially. Partitions beta diversity into turnover (species replacement) and nestedness (species loss) components following Baselga (2010).

Usage

spaccBeta(
  x,
  coords,
  n_seeds = 50L,
  method = "knn",
  index = c("sorensen", "jaccard"),
  distance = c("euclidean", "haversine"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL,
  map = FALSE
)

Arguments

Details

At each step of spatial accumulation, beta diversity is calculated between the accumulated species pool and the newly added site. This reveals how species composition changes as you expand spatially.

Interpretation:

• High turnover: New sites contribute different species (replacement)

• High nestedness: New sites contribute subsets of existing species (loss)

The sum of turnover and nestedness equals total beta diversity.

Value

An object of class spacc_beta containing:

References

Baselga, A. (2010). Partitioning the turnover and nestedness components of beta diversity. Global Ecology and Biogeography, 19, 134-143.

See Also

betapart::beta.pair() for pairwise beta diversity

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)

beta <- spaccBeta(species, coords, n_seeds = 30)
plot(beta)

# Compare Sorensen vs Jaccard
beta_jac <- spaccBeta(species, coords, index = "jaccard")

Description

Compute spatial accumulation of functional beta diversity, partitioned into turnover and nestedness components. Measures how functional trait space composition changes as sites are accumulated spatially.

Usage

spaccBetaFunc(
  x,
  coords,
  traits,
  n_seeds = 50L,
  method = "knn",
  index = c("sorensen", "jaccard"),
  distance = c("euclidean", "haversine"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL
)

Arguments

Details

Functional beta diversity quantifies the turnover of functional traits across space. At each accumulation step, beta is computed based on the overlap of trait ranges (functional space) between the accumulated pool and the newly added site.

Value

An object of class spacc_beta with additional attribute beta_type = "functional".

References

Baselga, A. (2012). The relationship between species replacement, dissimilarity derived from nestedness, and nestedness. Global Ecology and Biogeography, 21, 1223-1232.

Cardoso, P., Rigal, F. & Carvalho, J.C. (2015). BAT – Biodiversity Assessment Tools. Methods in Ecology and Evolution, 6, 232-236.

See Also

spaccBeta(), spaccBetaPhylo()

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 20, 1, 0.3), nrow = 50)
traits <- matrix(rnorm(20 * 3), nrow = 20)
rownames(traits) <- colnames(species) <- paste0("sp", 1:20)

beta_func <- spaccBetaFunc(species, coords, traits)
plot(beta_func)

Description

Compute spatial accumulation of phylogenetic beta diversity, partitioned into turnover and nestedness components. Measures how evolutionary composition changes as sites are accumulated spatially.

Usage

spaccBetaPhylo(
  x,
  coords,
  tree,
  n_seeds = 50L,
  method = "knn",
  index = c("sorensen", "jaccard"),
  distance = c("euclidean", "haversine"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL
)

Arguments

Details

Phylogenetic beta diversity quantifies evolutionary turnover across space. The PhyloSor index (phylogenetic Sorensen) is used: the fraction of branch length shared between two communities relative to total branch length. Partitioned into replacement (turnover) and loss (nestedness) components.

Value

An object of class spacc_beta with additional attribute beta_type = "phylogenetic".

References

Baselga, A. (2010). Partitioning the turnover and nestedness components of beta diversity. Global Ecology and Biogeography, 19, 134-143.

Chao, A., Chiu, C.H., Villeger, S., et al. (2023). Rarefaction and extrapolation with beta diversity under a framework of Hill numbers: the iNEXT.beta3D standardization. Ecological Monographs, 93, e1588.

See Also

spaccBeta(), spaccBetaFunc()

Examples

if (requireNamespace("ape", quietly = TRUE)) {
  tree <- ape::rtree(20)
  coords <- data.frame(x = runif(50), y = runif(50))
  species <- matrix(rbinom(50 * 20, 1, 0.3), nrow = 50)
  colnames(species) <- tree$tip.label

  beta_phylo <- spaccBetaPhylo(species, coords, tree)
  plot(beta_phylo)
}

Description

Compute spatial accumulation curves with sample coverage tracking. Allows standardization by completeness (coverage) rather than sample size, following Chao & Jost (2012) or the sample-based estimator of Chiu (2023).

Usage

spaccCoverage(
  x,
  coords,
  n_seeds = 50L,
  method = "knn",
  distance = c("euclidean", "haversine"),
  coverage = c("chao", "chiu"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL,
  map = FALSE
)

Arguments

Details

Sample coverage estimates the proportion of the total community abundance represented by observed species. It provides a measure of sampling completeness that is independent of sample size.

The Chao-Jost (2012) estimator counts singletons (f1) and doubletons (f2) in the cumulative abundance vector. It assumes individuals are sampled independently, which may not hold for plot-based spatial data.

The Chiu (2023) estimator uses incidence frequency counts instead: Q1 (species in exactly 1 site), Q2 (species in exactly 2 sites), and G1 (total abundance of Q1 species). It gives near-unbiased coverage estimates when organisms are spatially aggregated across sampling units.

Coverage-based rarefaction allows fair comparison of diversity across communities with different abundances by standardizing to equal completeness rather than equal sample size.

Value

An object of class spacc_coverage containing:

References

Chao, A. & Jost, L. (2012). Coverage-based rarefaction and extrapolation: standardizing samples by completeness rather than size. Ecology, 93, 2533-2547.

Chiu, C.-H. (2023). A sample-based estimator for sample coverage. Ecology, 104, e4099.

See Also

iNEXT::iNEXT() for coverage-based rarefaction without spatial structure

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rpois(50 * 30, 2), nrow = 50)

cov <- spaccCoverage(species, coords)
plot(cov)

# Sample-based coverage (recommended for spatial data)
cov_chiu <- spaccCoverage(species, coords, coverage = "chiu")

# Interpolate richness at 90% and 95% coverage
interp <- interpolateCoverage(cov, target = c(0.90, 0.95))

Description

Accumulate any user-supplied diversity index along a spatial ordering of sites. At each accumulation step the cumulative community is passed to fun, which returns a single number. This is the general escape hatch behind the built-in metric functions: use it for indices that spacc does not implement directly.

Usage

spaccDiversity(
  x,
  coords,
  fun,
  ...,
  method = c("knn", "kncn", "random", "radius", "collector"),
  incidence = FALSE,
  n_seeds = 50L,
  distance = c("euclidean", "haversine"),
  progress = TRUE,
  seed = NULL
)

Arguments

Details

The site ordering reuses the same spatial traversals as the built-in methods (nearest-neighbour, nearest-centroid, random, distance-rank, or data order), then evaluates fun on the accumulating community. Because the index is an arbitrary R function, this trades the speed of the compiled metrics for full flexibility.

Value

An object of class spacc_diversity that inherits from spacc, so the standard summary(), plot(), as.data.frame() and predict() methods apply. curves is an ⁠n_seeds x n_sites⁠ matrix of the metric along the accumulation.

See Also

spaccHill(), spaccPhylo(), spaccFunc() for built-in metrics.

Examples

coords <- data.frame(x = runif(40), y = runif(40))
species <- matrix(rpois(40 * 20, 2), nrow = 40)

# Shannon entropy along the accumulation
shannon <- function(comm) {
  p <- comm[comm > 0] / sum(comm)
  -sum(p * log(p))
}
div <- spaccDiversity(species, coords, shannon, n_seeds = 20)
plot(div)

Description

Compute the number of endemic species (species found only within the accumulated area) as sites are added spatially. Complements the standard SAC by tracking species unique to each spatial extent.

Usage

spaccEndemism(
  x,
  coords,
  n_seeds = 50L,
  method = "knn",
  distance = c("euclidean", "haversine"),
  map = FALSE,
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL
)

Arguments

Details

At each accumulation step k, an endemic species is one that is present in the accumulated sites (1..k) but absent from all remaining unvisited sites (k+1..n). This tracks how many species are unique to the area sampled so far.

The endemism curve typically starts low (few endemics at small areas), increases as the region grows, and eventually equals total richness when all sites are included.

Value

An object of class spacc_endemism containing:

References

Kier, G., Kreft, H., Lee, T.M., et al. (2009). A global assessment of endemism and species richness across island and mainland regions. Proceedings of the National Academy of Sciences, 106, 9322-9327.

May, F., Gerstner, K., McGlinn, D.J., et al. (2018). mobsim: an R package for the simulation and measurement of biodiversity across spatial scales. Methods in Ecology and Evolution, 9, 1401-1408.

See Also

spacc(), spaccHill()

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)

end <- spaccEndemism(species, coords, n_seeds = 30)
plot(end)

Description

Compute spatial accumulation of functional diversity metrics based on traits.

Usage

spaccFunc(
  x,
  coords,
  traits,
  metric = c("fdis", "fric"),
  n_seeds = 50L,
  method = "knn",
  distance = c("euclidean", "haversine"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL,
  map = FALSE
)

Arguments

Details

Functional diversity metrics quantify trait space occupation:

• FDis (Functional Dispersion): Abundance-weighted mean distance from the community centroid in trait space. Captures functional divergence.

• FRic (Functional Richness): Volume of trait space occupied (convex hull). Requires more species than traits to compute.

Value

An object of class spacc_func containing:

References

Laliberté, E. & Legendre, P. (2010). A distance-based framework for measuring functional diversity from multiple traits. Ecology, 91, 299-305.

See Also

FD::dbFD() for comprehensive functional diversity analysis

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rpois(50 * 20, 2), nrow = 50)

# Trait matrix (species x traits)
traits <- matrix(rnorm(20 * 3), nrow = 20)
rownames(traits) <- paste0("sp", 1:20)
colnames(species) <- rownames(traits)

func <- spaccFunc(species, coords, traits, metric = c("fdis", "fric"))
plot(func)

Description

Compute spatial species accumulation curves using Hill numbers (effective number of species) instead of raw richness. Hill numbers unify diversity measures: q=0 is richness, q=1 is exponential Shannon, q=2 is inverse Simpson.

Usage

spaccHill(
  x,
  coords,
  q = c(0, 1, 2),
  n_seeds = 50L,
  method = "knn",
  distance = c("euclidean", "haversine"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL,
  map = FALSE
)

Arguments

Details

Hill numbers (Chao et al. 2014) provide a unified framework for diversity measurement. Unlike raw richness (q=0), higher-order Hill numbers (q=1, q=2) down-weight rare species, providing different perspectives on diversity.

The spatial accumulation of Hill numbers can reveal scale-dependent diversity patterns missed by richness alone.

Value

An object of class spacc_hill containing:

References

Chao, A., Gotelli, N.J., Hsieh, T.C., Sander, E.L., Ma, K.H., Colwell, R.K. & Ellison, A.M. (2014). Rarefaction and extrapolation with Hill numbers: a framework for sampling and estimation in species diversity studies. Ecological Monographs, 84, 45-67.

See Also

spacc() for richness-only accumulation, iNEXT::iNEXT() for non-spatial Hill number rarefaction

Examples

# Compare diversity at different orders
coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rpois(50 * 30, 2), nrow = 50)

hill <- spaccHill(species, coords, q = c(0, 1, 2))
plot(hill)

# Extract summary at final site
summary(hill)

Description

Compute multisite beta diversity as gamma/alpha decomposition of Hill numbers along the spatial accumulation curve (Jost 2007 framework).

Usage

spaccHillBeta(
  x,
  coords,
  q = c(0, 1, 2),
  n_seeds = 50L,
  distance = c("euclidean", "haversine"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL
)

Arguments

Details

At each accumulation step k, the function computes:

• Gamma: Hill number of the pooled community (all k sites combined)

• Alpha: Generalized mean of per-site Hill numbers (Jost's power mean)

• Beta: gamma / alpha (effective number of distinct communities)

Beta = 1 means all sites are identical; beta = k means all sites are completely different. This provides the Hill-number analogue of the Baselga-based spaccBeta().

Value

An object of class spacc_hill_beta containing:

References

Jost, L. (2007). Partitioning diversity into independent alpha and beta components. Ecology, 88, 2427-2439.

See Also

spaccBeta() for P/A-based Baselga partitioning, spaccHill() for Hill accumulation without beta decomposition

Examples

coords <- data.frame(x = runif(40), y = runif(40))
species <- matrix(rpois(40 * 20, 2), nrow = 40)

hb <- spaccHillBeta(species, coords, n_seeds = 10, progress = FALSE)
plot(hb)

Description

Compute spatial accumulation of Hill numbers alongside sample coverage, enabling standardized comparison at equal completeness levels (iNEXT-style analysis applied spatially).

Usage

spaccHillCoverage(
  x,
  coords,
  q = c(0, 1, 2),
  target_coverage = NULL,
  n_seeds = 50L,
  distance = c("euclidean", "haversine"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE,
  seed = NULL
)

Arguments

Details

Combines spatial kNN accumulation with simultaneous Hill number and coverage computation. At each accumulation step, both the Chao-Jost sample coverage and Hill numbers for all requested orders are calculated.

When target_coverage is specified, Hill numbers are interpolated at those coverage levels using the existing interpolate_at_coverage() C++ function, enabling fair comparison between sites with different sampling completeness.

Value

An object of class spacc_hill_coverage containing:

References

Chao, A. & Jost, L. (2012). Coverage-based rarefaction and extrapolation: standardizing samples by completeness rather than size. Ecology, 93, 2533-2547.

Chao, A., Gotelli, N.J., Hsieh, T.C., Sander, E.L., Ma, K.H., Colwell, R.K. & Ellison, A.M. (2014). Rarefaction and extrapolation with Hill numbers. Ecological Monographs, 84, 45-67.

See Also

spaccHill() for Hill accumulation without coverage, spaccCoverage() for coverage accumulation without Hill numbers

Examples

coords <- data.frame(x = runif(40), y = runif(40))
species <- matrix(rpois(40 * 20, 2), nrow = 40)

hc <- spaccHillCoverage(species, coords, n_seeds = 10, progress = FALSE)
plot(hc)

# Standardize at 90% coverage
hc2 <- spaccHillCoverage(species, coords, target_coverage = 0.9,
                          n_seeds = 10, progress = FALSE)
summary(hc2)

Description

Compute spatial accumulation metrics for each site as a starting point. Useful for identifying sites with high or low accumulation rates, visualizing spatial patterns in diversity, and understanding edge effects.

Usage

spaccMetrics(
  x,
  coords,
  metrics = c("slope_10", "half_richness", "auc"),
  method = c("knn", "kncn", "random"),
  distance = c("euclidean", "haversine"),
  parallel = TRUE,
  n_cores = NULL,
  progress = TRUE
)

Arguments

Details

This function runs a spatial accumulation curve starting from each site individually, then extracts summary metrics from each curve. This allows you to identify:

• Sites in species-rich areas (high initial slope)

• Core vs edge sites (fast vs slow accumulation)

• Spatial patterns in community structure

The metrics can be plotted as a heatmap using plot(result, type = "heatmap"), which requires the ggplot2 package. For more sophisticated spatial visualization with study area boundaries, see the areaOfEffect package.

Value

An object of class spacc_metrics containing:

References

Soberon, J.M. & Llorente, J.B. (1993). The use of species accumulation functions for the prediction of species richness. Conservation Biology, 7, 480-488.

See Also

spacc() for standard accumulation curves

Examples

coords <- data.frame(x = runif(50), y = runif(50))
species <- matrix(rbinom(50 * 30, 1, 0.3), nrow = 50)
metrics <- spaccMetrics(species, coords,
                        metrics = c("slope_10", "auc"))
metrics$metrics$slope_10