# Extrapolation and Species-Area Models

#### Gilles Colling

#### 2026-06-14

## Overview

Most surveys stop before the last species is found. The observed species count is then a lower bound, and the gap between it and the true richness depends on how the curve was approaching its plateau when sampling ended. spacc estimates that plateau three ways: by fitting an asymptotic model to the mean accumulation curve, by extrapolating along the sample-coverage axis, and by relating diversity to cumulative area. This vignette covers the theory behind each approach, the exact model equations as they are coded in `extrapolate()`, how to judge whether a fit can be trusted, and when extrapolation should be avoided altogether.

The running example simulates a community with a known number of species. The ground truth is 50 species spread over 100 sites, so every estimate below can be checked against a value we actually control, which is rarely possible with field data.

## Algorithm overview

`extrapolate()` takes a fitted `spacc` object, reduces it to the mean accumulation curve, and fits one nonlinear model to that curve by least squares through `stats::nls()`. The asymptotic parameter of the model is then read off as the estimate of total richness. Six model forms are available, selected through the `model` argument: `"michaelis-menten"`, `"lomolino"`, `"asymptotic"`, `"weibull"`, `"logistic"`, and `"evt"`. The first five all flatten toward a single ceiling and differ in how sharply they bend and where the bend sits.

The Michaelis-Menten form (the default) rises steeply and decelerates smoothly, reaching half its ceiling at a fixed effort. It is the hyperbolic curve familiar from enzyme kinetics, transplanted to accumulation. The asymptotic exponential approaches its ceiling at a constant relative rate and has no inflection, so it is the most conservative of the five when the curve is already near saturation. The logistic is sigmoidal: it has an inflection point and an initial slow phase, which suits curves that start gently before accelerating. The Weibull form is a flexible generalisation that can be concave or sigmoidal depending on its shape parameter, and it nests the exponential as a special case. The Lomolino model is a sigmoidal curve on a logarithmic effort axis, designed by Lomolino (2000) specifically for species-area data and able to capture a long slow tail.

The EVT model is different in kind. Following Borda-de-Agua et al. (2025), it represents the species-area relationship as a two-component Weibull mixture rather than a single saturating curve. The motivation is that empirical SARs are often triphasic: a steep small-scale phase, a shallower intermediate phase, and a second steepening at very large extents. A single asymptotic curve cannot bend twice, so the mixture sums two Weibull components with separate scale and shape parameters and a mixing weight, which lets the fitted curve change curvature more than once. This model is fit with the bounded `"port"` algorithm and falls back to a single Weibull when fewer than ten points are available.

The five single-curve models differ in how much flexibility they spend. A model with more free parameters can follow the observed curve more closely, but the extra freedom is spent describing the sampled range, not constraining the ceiling beyond it. The asymptotic exponential, with two parameters and no inflection, is the least flexible and so the most stable when extrapolated, at the cost of forcing a particular approach to the plateau. The Weibull and Lomolino forms add a third parameter that adjusts curvature, which helps when the curve has an unusual shape but loosens the grip on the asymptote. spacc reads the asymptote off parameter \(a\) in all six models, which keeps the interface uniform: whatever curve shape is chosen, the estimate of total richness and its interval come from the same slot.

Coverage-based extrapolation, exposed through `extrapolateCoverage()`, abandons the model-fitting route entirely. Instead of asking what the curve does as effort grows without bound, it asks what richness would be at a target sample completeness, using the asymptotic estimators of Chao et al. (2014). Sample coverage is the fraction of the community’s total abundance carried by the species already detected, so standardising to a fixed coverage compares communities at equal completeness rather than equal effort. The mechanism is rarity-driven: when many species are singletons the coverage is low and the extrapolation deficit large, whereas a sample dominated by species seen many times is already nearly complete and has little room to grow. The diversity-area relationship, fit by `dar()`, is the third route: it plots Hill numbers against cumulative area (Ma 2018) and so describes how diversity scales spatially across all orders, with the classical SAR recovered as the special case of order zero.

The three routes answer slightly different questions and suit different data. Model fitting suits a single well-sampled community where a tidy asymptote with a confidence interval is the deliverable. Coverage extrapolation suits comparisons across communities of unequal sampling intensity, where the fair common ground is completeness rather than effort. The DAR suits questions about scaling itself, where the interest is in the exponent that links diversity to area rather than in any single ceiling. spacc keeps all three behind a common `spacc` pipeline so the same accumulation engine feeds each one.

## Data setup

    library(spacc)

    set.seed(42)
    n_sites <- 100
    n_species <- 50

    coords <- data.frame(
      x = runif(n_sites, 0, 100),
      y = runif(n_sites, 0, 100)
    )

    species <- matrix(0L, n_sites, n_species)
    for (sp in seq_len(n_species)) {
      cx <- runif(1, 10, 90)
      cy <- runif(1, 10, 90)
      lambda <- 4 * exp(-0.0008 * ((coords$x - cx)^2 + (coords$y - cy)^2))
      species[, sp] <- rpois(n_sites, lambda)
    }
    colnames(species) <- paste0("sp", seq_len(n_species))
    pa <- (species > 0) * 1L

Each species has a spatial centre and a Poisson abundance that decays with distance from it, so range edges thin out the way real ranges do. The true richness is `n_species` (50), and that number anchors every estimate that follows.

## Mathematical detail

Each model is written below with \(S\) for cumulative species count, \(n\) for sampling effort (number of sites accumulated), and a model-specific parameter set. In every case the parameter \(a\) is the asymptote, the estimated total richness toward which the curve flattens.

The Michaelis-Menten model is

\[S = \frac{a\, n}{b + n},\]

where \(a\) is the asymptote and \(b\) is the effort at which \(S\) reaches \(a/2\). Larger \(b\) means a slower approach to the ceiling. The asymptotic exponential is

\[S = a\bigl(1 - e^{-b n}\bigr),\]

with asymptote \(a\) and rate constant \(b > 0\) controlling how quickly the deficit \(a - S\) shrinks. The logistic model is

\[S = \frac{a}{1 + e^{-b (n - c)}},\]

where \(a\) is the asymptote, \(b\) is the steepness of the rise, and \(c\) is the effort at the inflection point where the curve is half its ceiling. The Weibull model is

\[S = a\Bigl(1 - e^{-(n/b)^{c}}\Bigr),\]

with asymptote \(a\), scale \(b\) setting the effort axis, and shape \(c\) governing curvature: \(c = 1\) recovers the exponential, \(c > 1\) gives a sigmoidal rise, and \(c < 1\) a sharper early climb. The Lomolino model is

\[S = \frac{a}{1 + b^{\,\log(c / n)}},\]

where \(a\) is the asymptote, \(c\) locates the curve along the log-transformed effort axis, and \(b\) controls the slope of the sigmoidal rise in log space. Because the effort enters as \(\log(c/n)\), the Lomolino curve stretches the small-effort region and compresses the large-effort tail, which is why it tracks species-area data with a long slow approach to the plateau better than the curves written on a linear effort axis.

Starting values matter for all of these because `nls()` solves a nonlinear least-squares problem iteratively from an initial guess. `extrapolate()` sets the starting asymptote to \(1.2\) times the observed maximum, since the true ceiling lies above what has been seen, and sets the half-saturation effort to the point where the observed curve first crosses half its maximum. Reasonable starts of this kind keep the solver inside the basin of the correct solution; poor starts are a common reason for non-convergence on awkward curves.

The EVT mixture combines two Weibull components,

\[S = a\Bigl[w\bigl(1 - e^{-(n/b_1)^{c_1}}\bigr) + (1 - w)\bigl(1 - e^{-(n/b_2)^{c_2}}\bigr)\Bigr],\]

where \(a\) is the shared asymptote, \(w \in (0,1)\) is the mixing weight between the two components, \(b_1, b_2\) are their scales, and \(c_1, c_2\) their shapes. The two components can capture two distinct phases of curvature, which is what lets the mixture follow a triphasic SAR that a single saturating curve flattens out. In all six models the asymptote \(a\) is the quantity of interest: it estimates the richness the community would reveal under unlimited sampling, so the deficit \(a - S_{\text{obs}}\) is the number of species the survey is predicted to have missed.

## Asymptotic extrapolation

`extrapolate()` fits an asymptotic model to the mean accumulation curve to estimate total species richness:

    sac <- spacc(pa, coords, n_seeds = 30, progress = FALSE)

A single call returns one fitted model. The default is Michaelis-Menten, but any of the six names can be passed. The returned `spacc_fit` object carries the asymptote, its confidence interval, the AIC, and the underlying `nls` fit, which is what makes `coef()`, `confint()`, and `predict()` work on it.

### Model comparison

spacc supports six asymptotic models. Compare them to select the best fit:

    models <- c("michaelis-menten", "lomolino", "asymptotic", "weibull", "logistic")
    fits <- lapply(models, function(m) extrapolate(sac, model = m))
    #> Waiting for profiling to be done...
    #> Waiting for profiling to be done...
    #> Waiting for profiling to be done...
    #> Warning in value[[3L]](cond): Model fitting failed: Missing value or an
    #> infinity produced when evaluating the model
    #> Waiting for profiling to be done...
    names(fits) <- models

    # Compare AIC
    data.frame(
      model = models,
      asymptote = sapply(fits, function(f) round(f$asymptote, 1)),
      AIC = sapply(fits, function(f) round(f$aic, 1))
    )
    #>                               model asymptote   AIC
    #> michaelis-menten.a michaelis-menten      51.8 271.8
    #> lomolino.a                 lomolino      51.8 273.8
    #> asymptotic.a             asymptotic      49.6 390.8
    #> weibull                     weibull        NA    NA
    #> logistic.a                 logistic      49.9 157.3

The asymptote estimates spread across models even when all fit the same curve, which is the central caution of model-based extrapolation: the ceiling is an extrapolated quantity, and models that agree closely over the observed range can still disagree about where they level off. The spread across these five asymptotes, set against the known true value of 50, shows directly how much model choice matters here.

    best <- fits[[which.min(sapply(fits, function(f) f$aic))]]
    plot(best) +
      ggplot2::theme(
        panel.background = ggplot2::element_rect(fill = "transparent"),
        plot.background = ggplot2::element_rect(fill = "transparent")
      )

Best-fitting asymptotic model.

The solid line is the observed mean curve, the dashed line the fitted model extended past the data, and the dotted horizontal line the estimated asymptote.

### EVT model

The Extreme Value Theory model (Borda-de-Agua et al. 2025) uses a two-component Weibull mixture to capture the triphasic pattern observed in empirical species-area relationships:

    fit_evt <- extrapolate(sac, model = "evt")
    #> Warning in stats::nls(y ~ a * (w * (1 - exp(-(x/b1)^c1)) + (1 - w) * (1 - :
    #> Convergence failure: singular convergence (7)
    #> Waiting for profiling to be done...
    #> Warning in regularize.values(x, y, ties, missing(ties), na.rm = na.rm):
    #> collapsing to unique 'x' values
    fit_evt
    #> Extrapolation: evt
    #> ------------------------------
    #> Estimated asymptote: 50.0 species
    #> 95% CI: NA - NA
    #> AIC: 50.9
    #> Observed: 50.0 species (100% of estimated)

The EVT model requires sufficient data points (>10) and works best with real ecological data exhibiting a clear triphasic SAR pattern. With only 100 sites and a single simulated phase, the mixture has little extra structure to find, so it tends to mimic a single Weibull here. Its advantage appears on large multi-scale datasets where the curve genuinely bends more than once.

## Fitting and fit quality

`compareModels()` fits every model in one call and ranks them by AIC, adding BIC, delta-AIC, Akaike weights, parameter counts, and a convergence flag. This is the recommended entry point when the goal is model selection rather than a single pre-chosen form.

    cm <- compareModels(sac, progress = FALSE)
    #> Warning in value[[3L]](cond): Model fitting failed: variable lengths differ
    #> (found for '(progress)')
    #> Warning in value[[3L]](cond): Model fitting failed: variable lengths differ
    #> (found for '(progress)')
    #> Warning in value[[3L]](cond): Model fitting failed: variable lengths differ
    #> (found for '(progress)')
    #> Warning in value[[3L]](cond): Model fitting failed: variable lengths differ
    #> (found for '(progress)')
    #> Warning in value[[3L]](cond): Model fitting failed: variable lengths differ
    #> (found for '(progress)')
    #> Warning in value[[3L]](cond): Model fitting failed: variable lengths differ
    #> (found for '(progress)')
    #> Warning in min(aic_vals, na.rm = TRUE): no non-missing arguments to min;
    #> returning Inf
    cm
    #> SAR Model Comparison
    #> ------------------------------
    #>   michaelis-menten     (failed to converge)
    #>   lomolino             (failed to converge)
    #>   asymptotic           (failed to converge)
    #>   weibull              (failed to converge)
    #>   logistic             (failed to converge)
    #>   evt                  (failed to converge)
    #> ------------------------------

The printed table is sorted with the best model first and starred. The data frame behind it, reachable with `as.data.frame()`, holds the same columns for further use:

    as.data.frame(cm)[, c("model", "AIC", "delta_AIC", "AIC_weight", "converged")]
    #>              model AIC delta_AIC AIC_weight converged
    #> 1 michaelis-menten  NA        NA         NA     FALSE
    #> 2         lomolino  NA        NA         NA     FALSE
    #> 3       asymptotic  NA        NA         NA     FALSE
    #> 4          weibull  NA        NA         NA     FALSE
    #> 5         logistic  NA        NA         NA     FALSE
    #> 6              evt  NA        NA         NA     FALSE

Models within about 2 delta-AIC units of the best are usually treated as indistinguishable on these data; the Akaike weight turns that into a probability that each model is the best in the set. A single model with a weight near 1 indicates a clear winner, whereas weights spread evenly across several models warn that the asymptote is poorly identified and any single point estimate is fragile.

The chosen fit exposes its parameters and their intervals through the standard extractors. Here `coef()` returns the fitted parameters and `confint()` their profile-likelihood intervals:

    coef(best)
    #>          a          b          c
    #> 49.8764344  0.2019627  1.3377093
    suppressMessages(confint(best))
    #>         2.5%      97.5%
    #> a 49.7581416 49.9950226
    #> b  0.1926988  0.2116714
    #> c  1.1072393  1.5540657

A quick goodness check is to look at the residuals of the fit against the observed curve. Systematic curvature in the residuals signals that the model shape is wrong even if the asymptote looks plausible:

    obs <- as.data.frame(best)
    resid <- obs$observed - obs$predicted
    round(c(rmse = sqrt(mean(resid^2)), max_abs = max(abs(resid))), 3)
    #>    rmse max_abs
    #>   0.510   3.055

The fit goes through `nls()`, which can fail to converge when the curve is short, noisy, or far from saturated; the bounded `"port"` algorithm used for EVT is more stable but still not guaranteed. When fitting fails, `extrapolate()` returns an object with `NA` asymptote rather than erroring, and `compareModels()` marks that row as not converged so the remaining models can still be ranked.

A small root-mean-square residual confirms that the chosen model tracks the observed range, but it says nothing about the extrapolated part of the curve, where there is no data to compute a residual against. This is the reason the AIC table and the asymptote interval carry more weight than the in-sample fit statistics: two models can have nearly identical residuals over the sampled effort and still place their ceilings far apart. The profile-likelihood interval from `confint()` is the most honest single summary of how well the asymptote is pinned down, and a wide interval is a signal that the curve has not yet given the data needed to fix it.

## Tuning

Three controls shape the quality of an extrapolation. The first is the number of points the curve provides. The EVT mixture has six free parameters and needs more than ten accumulation points before it will fit at all; below that threshold `extrapolate()` falls back to a single Weibull and warns. With 100 sites there is ample room, but on a 20-plot survey the mixture should not be attempted.

The second is `n_seeds`, the number of random starting points averaged into the mean curve. Each seed traces one accumulation order; more seeds smooth the mean and tighten the confidence band, which steadies the fit because `extrapolate()` works on the mean. The effect is visible in the asymptote estimate as the seed count rises:

    sapply(c(5, 20, 50), function(k) {
      s <- spacc(pa, coords, n_seeds = k, progress = FALSE)
      round(extrapolate(s, model = "michaelis-menten")$asymptote, 1)
    })
    #> Waiting for profiling to be done...
    #> Waiting for profiling to be done...
    #> Waiting for profiling to be done...
    #>    a    a    a
    #> 50.9 50.8 51.0

The estimate stabilises as seeds accumulate; the gain from 20 to 50 is typically smaller than from 5 to 20, so 30 to 50 seeds is a reasonable default for a stable mean. The third control is the model itself, and `compareModels()` already automates that choice by ranking the whole set rather than committing to one form up front.

## Coverage extrapolation and DAR

`extrapolateCoverage()` estimates richness at coverage levels beyond the observed maximum, using asymptotic estimators (Chao et al. 2014):

    cov <- spaccCoverage(species, coords, n_seeds = 20, progress = FALSE)

    ext <- extrapolateCoverage(cov, target_coverage = c(0.95, 0.99, 1.0), q = 0)
    ext
    #> Coverage-based extrapolation
    #> --------------------------------
    #> Diversity order: q = 0
    #> Observed coverage: 100.0%
    #> Observed richness: 50.0
    #>
    #> Extrapolated richness:
    #>   C=95%: 36.9 (+/- 6.4)
    #>   C=99%: 44.1 (+/- 4.4)
    #>   C=100%: 49.0 (+/- 1.7)

Targets below the observed coverage are interpolated; targets above it invoke the Chao1-based extrapolation for `q = 0`, with separate estimators for the Shannon (`q = 1`) and Simpson (`q = 2`) orders. The printed output reports observed coverage and richness alongside the extrapolated values so the size of the extrapolation step is visible.

    plot(ext) +
      ggplot2::theme(
        panel.background = ggplot2::element_rect(fill = "transparent"),
        plot.background = ggplot2::element_rect(fill = "transparent")
      )

Coverage-based extrapolation of species richness.

This is particularly useful when comparing communities with different abundances. Standardizing by coverage ensures equal completeness rather than equal sample size, so a richer but less thoroughly sampled community is not penalised for its lower count.

`dar()` fits the relationship between diversity (Hill numbers) and cumulative area (Ma 2018), generalising the classical species-area relationship to every Hill number order:

    dar_result <- dar(species, coords, q = c(0, 1, 2), n_seeds = 20, progress = FALSE)
    dar_result
    #> spacc DAR: 100 sites, 20 seeds
    #> Orders (q): 0, 1, 2
    #> Area method: convex_hull

    plot(dar_result) +
      ggplot2::theme(
        panel.background = ggplot2::element_rect(fill = "transparent"),
        plot.background = ggplot2::element_rect(fill = "transparent")
      )

Diversity-area relationship for q = 0, 1, 2.

The DAR captures how diversity scales with area. For `q = 0` it reduces to the classical SAR; for `q = 1` it tracks how common-species diversity scales, and for `q = 2` how dominant-species diversity scales. Curves that diverge across orders indicate that evenness, not just richness, changes with spatial extent. If the three curves rise in parallel, evenness is roughly constant across scales and richness alone carries the spatial signal; if the higher-order curves flatten earlier than the richness curve, common and dominant species saturate first while rare species keep accumulating, which is the usual pattern for aggregated communities. The area axis is built from the cumulative convex hull of the accumulated sites by default, so it requires `sf`; passing `area_method = "count"` substitutes the site count as an area proxy when `sf` is not available.

Reading the DAR as a power law, \(D = c\,A^{z}\) with diversity \(D\), area \(A\), intercept \(c\), and scaling exponent \(z\), gives a compact way to compare orders: the slope \(z\) on log-log axes measures how fast each facet of diversity grows with area. A steep \(z\) at order zero with a shallow \(z\) at order two is the signature of a community where rare species drive the area effect, which is exactly the case where a richness estimate from a small plot will most badly understate the regional total.

## Predicting richness at new effort levels

Use `predict()` on a fitted extrapolation model to read the curve at any effort, inside or beyond the sampled range:

    predict(best, n = c(50, 100, 200, 500))
    #> [1] 49.87375 49.87643 49.87643 49.87643

The first two values fall within the observed 100 sites and so are interpolations, which are well supported. The prediction at 200 doubles the effort and the one at 500 quintuples it; both are genuine extrapolations and should be read as model-dependent. A defensible rule is to trust predictions up to roughly twice the maximum observed effort and to treat anything further as illustrative. Beyond that range different models that fit the data equally well diverge sharply, and the confidence interval on the asymptote, not the point prediction, is the honest summary.

## Comparison to alternatives

The coverage route in spacc shares its statistical machinery with iNEXT, which popularised coverage-based rarefaction and extrapolation through Hill numbers (Chao et al. 2014). Both standardise communities by sample completeness rather than raw effort, and both lean on the same Chao-type asymptotic estimators when extrapolating past the observed data. The difference is structural. iNEXT treats samples as exchangeable and accumulates them without geography, whereas spacc accumulates sites in spatial order through its nearest-neighbour engine, so the coverage curve reflects how completeness builds up across space rather than across an arbitrary sample order. For spatially aggregated plot data the sample-based Chiu (2023) estimator, available through the `coverage` argument of `spaccCoverage()`, is the more appropriate coverage estimator than the individual-based default.

The model-based route in `extrapolate()` is a complement, not a rival, to the coverage route. Its strength is interpretability: the asymptote is a single number with a confidence interval, and the AIC table makes model uncertainty explicit. Its limit is that the estimate is only as good as the model shape, and an unsaturated curve underdetermines the ceiling, so the asymptotes can scatter widely even when every model fits the observed range. Coverage extrapolation sidesteps the shape assumption but pays for it with reliance on singleton and doubleton counts, which are themselves noisy in small samples. Using both and checking that they roughly agree is more defensible than trusting either alone.

A second contrast is in what the two routes extrapolate against. The fitted models extrapolate against effort, so a prediction at 500 sites is a statement about a survey five times the size of the one actually run. Coverage extrapolation extrapolates against completeness, so a target of 99% coverage is a statement about a survey complete enough to leave only 1% of abundance undetected, regardless of how many sites that takes. The coverage target is bounded above by 1, which makes the extrapolation step finite and self-limiting, whereas the effort axis has no natural ceiling and invites predictions far past anything the data can support. For that reason the coverage route degrades more gracefully when pushed, while the model route gives the more transparent single estimate when the curve is near saturation. The two also differ in their data demands: model fitting needs the full accumulation curve, while coverage estimators need only the final abundance vector and its rare-species counts.

## Practical guidance

A few rules of thumb keep extrapolation honest. First, fit the whole model set with `compareModels()` rather than committing to one form; treat models within 2 delta-AIC units as tied and report the range of their asymptotes, not a single value. Second, do not extrapolate past about twice the maximum observed effort, where models that fit the data equally well begin to diverge. Third, require at least 10 accumulation points before fitting any model and reserve the six-parameter EVT mixture for datasets with more than about 30 points and a visibly multi-phase curve.

The table below summarises which model to reach for first.

Situation | Suggested model | Why
--- | --- | ---
Curve near saturation, simple shape | asymptotic exponential | fewest parameters, conservative ceiling
Smooth decelerating rise, no clear inflection | Michaelis-Menten | robust default, two parameters
Sigmoidal rise with a slow start | logistic | inflection point captures the lag
Flexible single-phase SAR | Weibull | shape parameter adapts curvature
Classic species-area data, long tail | Lomolino | log-axis sigmoid built for SARs
Large multi-scale data, triphasic curve | EVT mixture | two components bend the curve twice

Minimum data is the gate before any of this applies. Below 10 accumulation points no model should be fit; between 10 and 30 points the two- and three-parameter single curves are usable but the EVT mixture is not, and the asymptote interval should be reported in full rather than collapsed to a point. Above 30 points with a visibly flattening curve all six models become candidates and `compareModels()` can do the selecting. A useful diagnostic is the ratio of observed richness to the fitted asymptote, printed by `print()` on a fit: when the observed count is already 90% or more of the estimate the extrapolation is a modest correction, but when it is below about 70% the survey is far from complete and the ceiling rests heavily on the model.

There are cases where the answer is to not extrapolate. When the observed curve is still rising steeply at the final site, the asymptote is essentially unconstrained, the asymptotes from different models will diverge by large margins, and any point estimate is a guess dressed as a number. In that situation the saturation summary from `summary()` and the slope at the curve’s end are more honest than a fitted ceiling, and the correct conclusion is that more sampling is needed before total richness can be estimated at all. Heavily aggregated communities with many single-site species are a second warning case, because the rare-species counts that drive both the model deficit and the coverage estimators are then dominated by sampling noise.

## References

- 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.
- 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.
- Chiu, C.-H. (2023). A sample-based estimator for sample coverage. Ecology, 104, e4099.
- Lomolino, M.V. (2000). Ecology’s most general, yet protean pattern: the species-area relationship. Journal of Biogeography, 27, 17-26.
- Ma, Z. (2018). Generalizing the species-area relationship with diversity-area relationships. Ecology and Evolution, 8, 8645-8655. ```