Abstract
Many attempts to explain the species-abundance distribution (SAD) assume that it has a universal functional form which applies to most assemblages. However, if such a form does exist, then it has to be invariant under changes in the area of the study plot (the addition of neighboring areas or subdivision of the original area) and changes in taxonomic composition (the addition of sister taxa or subdivision to subtaxa). We developed a theory for such an area-and-taxon invariant SAD and derived a formula for such a distribution. Both the log-normal and our area-and-taxon invariant distribution fitted data well. However, the log-normal distributions of two adjoined sub-assemblages cannot be composed into a log-normal distribution for the resulting assemblage, and the SAD composed from two log-normal distributions fits the SAD for the assemblage poorly in comparison to the area-and-taxon invariant distribution. Observed abundance patterns therefore reveal area-and-taxon invariant properties absent in log-normal distributions, suggesting that multiplicative models generating log-normal-like SADs (including the power-fraction model) cannot be universally valid, as they necessarily apply only to particular scales and taxa.
Similar content being viewed by others
References
Akaike H (1974) A new look at the statistical model identification. IEEE Trans Automat Contr 19:716–723. doi:10.1109/TAC.1974.1100705
Baker TC, Preston FW (1946) Fatigue of glass under statistic loads. J Appl Phys 17:170–178. doi:10.1063/1.1707702
Bibby CJ, Burgess ND, Hill DA (1992) Bird census techniques. Academic, London
Borda-de-Água L, Hubbell SP, He F (2007) Scaling biodiversity under neutrality. In: Storch D, Marquet PA, Brown JH (eds) Scaling biodiversity. Cambridge University Press, Cambridge, pp 347–375
Chave J (2004) Neutral theory and community ecology. Ecol Lett 7:241–253. doi:10.1111/j.1461-0248.2003.00566.x
Connolly SR, Hughes TP, Belwood DR et al (2005) Community structure of corals and reef fishes at multiple scales. Science 309:1363–1365. doi:10.1126/science.1113281
Death RG (1996) The effect of habitat stability on benthic invertebrate communities: the utility of species abundance distributions. Hydrobiologia 317:97–107. doi:10.1007/BF00018733
Dewdney AK (2000) A dynamical model of communities and a new species-abundance distribution. Biol Bull 198:152–165. doi:10.2307/1542811
Engen S (2001) A dynamic and spatial model with migration generating the log-Gaussian field of population densities. Math Biosci 173:85–102. doi:10.1016/S0025-5564(01)00077-3
Engen S, Lande R (1996) Population dynamic models generating the lognormal species abundance distribution. Math Biosci 132:169–183. doi:10.1016/0025-5564(95)00054-2
Etienne RS, Olff H (2004) A novel genealogical approach to neutral biodiversity theory. Ecol Lett 7:170–175. doi:10.1111/j.1461-0248.2004.00572.x
Fisher RA, Corbet AS, Williams CB (1943) The relation between the number of species and the number of individuals in a random sample of an animal population. J Anim Ecol 12:42–58. doi:10.2307/1411
Golicher DJ, O’Hara RB, Ruiz-Montoya L et al (2006) Lifting a veil on diversity: a bayesian approach to fitting relative abundance models. Ecol Appl 16:202–212. doi:10.1890/04-1599
Gray JS, Bjorgesaeter A, Ugland KI (2005) The impact of rare species on natural assemblages. J Anim Ecol 74:1131–1139. doi:10.1111/j.1365-2656.2005.01011.x
Green JL, Plotkin JB (2007) A statistical theory for sampling species abundances. Ecol Lett 10:1037–1045. doi:10.1111/j.1461-0248.2007.01101.x
Green J, Harte J, Ostling A (2003) Species richness, endemism and abundance patterns: test of two fractal models in a serpentine grassland. Ecol Lett 6:919–928. doi:10.1046/j.1461-0248.2003.00519.x
Gregory RD (2000) Abundance patterns of European breeding birds. Ecography 23:201–208. doi:10.1111/j.1600-0587.2000.tb00276.x
Harte J, Conlisk E, Ostling A et al (2005) A theory of spatial structure in ecological communities at multiple spatial scales. Ecol Monogr 75:179–197. doi:10.1890/04-1388
He F (2005) Deriving a neutral model of species abundance from fundamental mechanisms of population dynamics. Funct Ecol 19:187–193. doi:10.1111/j.0269-8463.2005.00944.x
Hubbell SP (2001) The unified theory of biodiversity and biogeography. Princeton University Press, Princeton
Kammesheidt L (1998) The role of tree sprouts in the restorations of stand structure and species diversity in tropical moist forest after slash-and-burn agriculture in Eastern Paraguay. Plant Ecol 139:155–165. doi:10.1023/A:1009763402998
Kempton RA, Taylor LR (1974) Log-series and log-normal parameters as diversity discriminants for the lepidoptera. J Anim Ecol 43:381–399. doi:10.2307/3371
Loehle C, Hansen A (2005) Community structure and scaling relations for the avifauna of the US pacific and inland northwest. Ecol Complex 2:59–70. doi:10.1016/j.ecocom.2004.09.001
Magnussen S, Boyle TJB (1995) Estimating sample-size for inference about the Shannon-Weaver and the Simpson index of species-diversity. For Ecol Manage 78:71–84. doi:10.1016/0378-1127(95)03596-1
Magurran AE (1988) Ecological diversity and its measurement. Croom Helm Australia, New South Wales
Magurran AE, Henderson PA (2003) Explaining the excess of rare species in natural species abundance distributions. Nature 422:714–716. doi:10.1038/nature01547
Mandelbrot BB (1963) New methods in statistical economics. J Polit Econ 71:421–440. doi:10.1086/258792
Marquet PA, Keymer JE, Cofré H (2003) Breaking the stick in space: of niche models, metacommunities and patterns in the relative abundance of species. In: Blackburn TM, Gaston KJ (eds) Macroecology: Concepts and consequences. British Ecological Society and Blackwell Science, Oxford, pp 64–81
May R (1975) Patterns of species abudance and diversity. In: Cody ML, Diamond JM (eds) Ecology and evolution of communities. The Belknap Press of Harvard University Press, Cambridge, pp 81–120
May RM, Crawley JM, Sugihara G (2007) Communities: Patterns. In: May RM, McLean A (eds) Theoretical ecology. Oxford University Press, Oxford, pp 111–131
McGill BJ (2003) Strong and weak tests of macroecological theory. Oikos 102:679–685. doi:10.1034/j.1600-0706.2003.12617.x
McGill BJ, Etienne RS, Gray JS et al (2007) Species abundance distributions: moving beyond single prediction theories to integration within an ecological framework. Ecol Lett 10:995–1015. doi:10.1111/j.1461-0248.2007.01094.x
Motomura I (1932) A statistical treatment of associations. Zool Mag Tokyo 44:379–383 in Japanese
Nee S, Harvey PH, May RM (1991) Lifting the veil on abundance patterns. Proc R Soc Lond B Biol Sci 243:161–163. doi:10.1098/rspb.1991.0026
Preston FW (1948) The commonness, and rarity, of species. Ecology 29:254–283. doi:10.2307/1930989
Preston FW (1981) Pseudo-lognormal distributions. Ecology 62:355–364. doi:10.2307/1936710
Pueyo S (2006) Diversity: between neutrality and structure. Oikos 112:392–405. doi:10.1111/j.0030-1299.2006.14188.x
Pueyo S, He F, Zillio T (2007) The maximum entropy formalism and the idiosyncratic theory of biodiversity. Ecol Lett 10:1017–1028. doi:10.1111/j.1461-0248.2007.01096.x
Salvador-Van-Eysendore D, Bogaert J, Zak-Mnacek V et al (2003) Sapling diversity in canopy gaps in an Equadorian rain forest. For Sci 49:909–917
Sichel HS (1997) Modelling species-abundance frequencies and species-individual functions with the generalized inverse Gaussian-Poisson distribution. South African Statist J 31:13–37
Šizling AL, Storch D (2007) Geometry of species distributions: Random clustering and scale invariance. In: Storch D, Marquet PA, Brown JH (eds) Scaling biodiversity. Cambridge University Press, Cambridge, pp 77–100
Storch D, Šizling AL (2008) The concept of taxon invariance in ecology: Do diversity patterns vary with changes in taxonomic resolution? Folia Geobot. doi:10.1007/s12224-008-9015-8
Storch D, Gaston KJ, Cepák J (2002) Pink landscapes: 1/f spectra of spatial environmental variability and bird community composition. Proc R Soc Lond B Biol Sci 269:1791–1796. doi:10.1098/rspb.2002.2076
Sugihara G (1980) Minimal community structure: an explanation of species abundance patterns. Am Nat 116:770–787. doi:10.1086/283669
Syrek D, Weiner WM, Wojtylak M et al (2006) Species abundance distribution of collembolan communities in forest soils polluted with heavy metals. Appl Soil Ecol 31:239–250. doi:10.1016/j.apsoil.2005.05.002
Tokeshi M (1999) Species coexistence: Ecological and Evolutionary perspectives. Blackwell, Oxford
Ulrich W, Ollik M (2005) Limits to the estimation of species richness: the use of relative abundance distributions. Divers Distrib 11:265–273. doi:10.1111/j.1366-9516.2005.00127.x
Visser S (1995) Ectomycorrhizal fungal succession in jack pine stands following wildfire. New Phytol 129:389–401. doi:10.1111/j.1469-8137.1995.tb04309.x
Volkov I, Banavar JR, Hubbell SP et al (2003) Neutral theory and relative species abundance in ecology. Nature 424:1035–1037. doi:10.1038/nature01883
Walla TR, Engen S, DeVries PJ et al (2004) Modeling vertial beta-diversity in tropical butterfly communities. Oikos 107:610–618. doi:10.1111/j.0030-1299.2004.13371.x
Wasserman LA (2004) All of statistics: A concise course in statistical inference. Springer, Berlin
Whittaker RH (1970) Communities and Ecosystems. Macmillan, New York
Wilson JB (1993) Would we recognise a broken-stick community if we found one? Oikos 67:181–183. doi:10.2307/3545108
Williamson M, Gaston KJ (2005) The lognormal distribution is not an appropriate null hypothesis for the species-abundance distribution. J Anim Ecol 74:409–422. doi:10.1111/j.1365-2656.2005.00936.x
Yin ZY, Peng SL, Ren H et al (2005) LogCauchy, log-sech and lognormal distributions of species abundances in forest communities. Ecol Modell 184:329–340. doi:10.1016/j.ecolmodel.2004.10.011
Acknowledgement
We thank J. Mourková and J. Cepák for their help with the fieldwork. We are grateful to M. Williamson, J. Nekola, B. J. McGill, F. He and anonymous referees for their comments. A.L.Š. was supported by the Marie Curie Fellowship no. 039576-RTBP-EIF. K.J.G. holds a Royal Society-Wolfson Research Merit Award. This work was supported by grants from the Czech Ministry of Education No. LC06073 and MSM0021620845, and Grant agency of the AS CR (IAA601970801).
Author information
Authors and Affiliations
Corresponding author
Electronic Supplementary Material
Below is the link to the electronic supplementary material.
Appendices
Appendix I: Composition of two SADs with correlated abundances
If abundances of the assemblages to be composed are correlated with each other, the SADs of the two assemblages interact in a particular way, which must be reflected in the definition of the mathematical operation that models a composition of the SADs. This operation was marked as *c in Eq. 2, which refers to convolution (*) accounting for a correlation (index c).
If there is no correlation between abundances, the SADs f 1(a) and f 2(a) are convoluted as
This formula is based on the fact that the probability density of each abundance, a, is given by the sum (integral) of densities for all combinations of abundances, {a 1;a 2}, along a line of possible combinations of abundances, a 2 = a−a 1 (Fig. 1a). The reason is that (1) each point along the line represents one independent combination of abundances which gives the resulting abundance, a, and (2) the product of f 1(a 1) and f 2(a−a 1) is the probability (density) that the abundances a 1 and a 2 (=a−a 1), which give the abundance a, occur simultaneously (i.e. each abundance applies to one assemblage). If abundances are not correlated, the line of the combinations is bounded by abundances of zero and a (\(0 <a_1 <a\) and \(0 <a_2 <a\); full line in Fig. 1a).
The simplest way to model correlation of abundances is by constraining the lines representing the possible combination of abundances which produce resulting abundance a by two increasing lines (a 2 = σ min a 1, a 2 = σ max a 1) intersecting the origin (Fig. 1b,c). If abundances are perfectly correlated, the abundances of the plots are proportional to each other — i.e. both lines approach each other.
In this case, we integrate probability densities (simply said, we sum the probabilities) not along the whole line between 0 and a (Fig. 1a), but only between two extreme abundances (\({a \mathord{\left/ {\vphantom {a {\left( {\sigma _{\max } + 1} \right)}}} \right. \kern-\nulldelimiterspace} {\left( {\sigma _{\max } + 1} \right)}}\) and \({a \mathord{\left/ {\vphantom {a {\left( {\sigma _{\min } + 1} \right)}}} \right. \kern-\nulldelimiterspace} {\left( {\sigma _{\min } + 1} \right)}}\)), which are imposed by the correlation (Fig. 1b). The composition of two SADs for species common to both subassemblages then obeys
where ν is a normalization constant.
Appendix II: A solution of the Eq. 2
Having the analytical form of the composition of two functional forms of SADs (Eq. 2 where *c is defined by Eq. 5), we can check whether a multi-diffonential distribution (Eq. 3) is area-and-taxon invariant, i.e. whether the form composed from two multi-diffonentials is a multi-diffonential distribution. The evidence has been done by substituting the solution to Eq. 5. which gives
which is, after substitution and reindexation, the multi-diffonential form (Eq. 3) as well (with different parameter N). The multi-diffonential distribution is obviously robust against proportional summation (linear combination), and thus follows the entire composition (Eq. 2) and is both taxon and area invariant. Note that in the cases in which the differences between respective As and/or αs approach zero the additive terms, whose denominators (see Eq. 6) are affected by these small values, turn into gamma distributions (\(\gamma _i a^{\nu _i } e^{ - \beta _i a} \); \(\nu _i \in {\mathbf{N}}\)), and the area-and-taxon invariant distribution becomes more complicated. However, there is only a very low probability that this happens by chance, and thus here we present only the simpler solution. The cumulative distribution function of the multi-diffonential distribution obeys
and the expectation is
For the range of shapes see Fig. 2, for fitting procedure see Šizling and Storch (2007) or supplement SIII, and for fitting utility http://www.cts.cuni.cz/wiki/ecology:start.
Appendix III: Possible formal mechanism producing multi-diffonential SADs
First we show that a variety of distributions can be modelled as a sum of exponential distributions. According to the Taylor theorem almost any function f can be approached by \(f\left( y \right) = \sum\limits_{k = 0}^N {c_i y^i } \). Denote abundance a as ln1/y (\(y \in \left( {0;1} \right)\)). Then a variety of shapes can be expressed as \(f\left( {e^{ - a} } \right) = \sum\limits_{i = 0}^N {c_i e^{ - ia} } \). Because the result of the transformation is assumed to be a distribution (i.e. with finite integral between zero and infinity), we exclude all functions with i = 0. As a result, a variety of distributions can be approached by a sum of exponential forms
where \(\lambda _{\min } \leqslant \lambda _j \left( {0 <\lambda _{\min } \leqslant 1} \right)\) for all j.
Now we show that the composition of two sums of exponential forms produces diffonential terms, which imposes additional constraints on a resulting distribution (e.g. an existence of indices m, n so that c m = −c n , which cannot happen by chance). Assume two distributions expressed as \(\phi _{10} \left( a \right) = \sum {c_j e^{ - \lambda _j a} } \) and \(\phi _{01} \left( a \right) = \sum {c_l e^{ - \lambda _l a} } \). Their composition follows
(Eq. 2; c-convolution is defined as in Appendix I). If either of the component distributions comprises diffonential terms, the evidence does not change, because composition of two diffonentials remains diffonential (Appendix II). A gamma distribution results if both parameters λ happen to be equal to each other (Appendix II), which we consider unlikely.
If we express each additive term as a normalized distribution (terms in brackets ‘[]’ in Eq. 11) multiplied with its dominance δ, we get
where δ = c/λ. This suggests that a high Jaccard index (the proportion of species common to both plots π 11; note that \(\pi _{11} = 1 - \pi _{10} - \pi _{01} \) and all π ≥ 0) can make the diffonential terms dominant when composing SADs of several subplots.
Rights and permissions
About this article
Cite this article
Šizling, A.L., Storch, D., Reif, J. et al. Invariance in species-abundance distributions. Theor Ecol 2, 89–103 (2009). https://doi.org/10.1007/s12080-008-0031-3
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s12080-008-0031-3