Noisy data and distribution maps: the example of Phylan semicostatus Mulsant and Rey, 1854 (Coleoptera, Tenebrionidae) from Serra de Tramuntana (Mallorca, Western Mediterranean)

Authors

  • M. Palmer IMEDEA (CSIC-UIB), Instituto Mediterráneo de Estudios Avanzados, Miquel Marquès 21, 07190 Esporles (Mallorca)
  • L. Gómez-Pujol Department of Earth Sciences. Univ. Illes Balears. Cta. Valldemossa km 7.5, 07071 Palma de Mallorca
  • G. X. Pons Department of Earth Sciences. Univ. Illes Balears. Cta. Valldemossa km 7.5, 07071 Palma de Mallorca, Spain
  • J. Mateu CITTIB, Centre d’Investigació i Tecnologies Turístiques de les Illes Balears. Passatge Guillem de Torrella, 07002 Palma. Illes Balears.
  • M. Linde IMEDEA (CSIC-UIB), Instituto Mediterráneo de Estudios Avanzados, Miquel Marquès 21, 07190 Esporles (Mallorca)

DOI:

https://doi.org/10.3989/graellsia.2003.v59.i2-3.254

Keywords:

Distribution maps, Occurrence patterns, Genetic algorithms, GARP modelling, Invertebrates

Abstract


Distribution maps are key tools for environmental management and biogeographic analyses. However, success in predicting spatial distribution is limited when using noisy presence/absence data sets. Both false absences and presences can be related with local departures from equilibrium (for example, temporary extinctions or unsuccessful colonisations). Moreover, false absences can arise from limited sampling effort. Here we explore an analytical strategy to get additional information on the presence/absence pattern of one target species from the presence/absence of all other species in the community. The logic is simple: the target species should display higher probability of presence at a site if a sample from this site is faunistically very close to the samples from other sites where the species occurs. Therefore, we first model presence/absence of the target species as a function of between-sample faunistic similarity. Second, the observed data for the target species are readjusted as a function of the expected probability of presence: current presences at sites with extreme low probability of presence are interpreted as unstable presences, and are recoded as absences. Seemingly, absences at sites with high probability of presence are interpreted as false absences, and are recoded as presences. In the experimental case presented herein, the recoding procedure is based on the presence/absence of 174 species, covering a broad taxonomic scope (snails, beetles, spiders and isopods). 1 km2 distribution maps of presence/absence of the endemic beetle Phylan semicostatus were modelled from these recoded data. Mapping is done using GARP based on four environmental explanatory variables. These maps seem to be more stable and less prone to fail in predicting presence than those derived directly from the observed data.

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Author Biography

M. Palmer, IMEDEA (CSIC-UIB), Instituto Mediterráneo de Estudios Avanzados, Miquel Marquès 21, 07190 Esporles (Mallorca)

Secretaría científica

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Published

2003-12-30

How to Cite

1.
Palmer M, Gómez-Pujol L, Pons GX, Mateu J, Linde M. Noisy data and distribution maps: the example of Phylan semicostatus Mulsant and Rey, 1854 (Coleoptera, Tenebrionidae) from Serra de Tramuntana (Mallorca, Western Mediterranean). Graellsia [Internet]. 2003Dec.30 [cited 2025Feb.24];59(2-3):389-98. Available from: https://graellsia.revistas.csic.es/index.php/graellsia/article/view/254

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Section

Research Articles