Journal of Animal EcologyVolume 85, Issue 4 p. 1131-1131 CorrigendumFree Access Corrigendum This article corrects the following: Influences of sampling effort on detected patterns and structuring processes of a Neotropical plant–hummingbird network Jeferson Vizentin-Bugoni, Pietro K. Maruyama, Vanderlei J. Debastiani, L. da S. Duarte, Bo Dalsgaard, Marlies Sazima, Daniel Stouffer, Volume 85Issue 1Journal of Animal Ecology pages: 262-272 First Published online: November 30, 2015 First published: 10 May 2016 https://doi.org/10.1111/1365-2656.12520AboutSectionsPDF ToolsRequest permissionExport citationAdd to favoritesTrack citation ShareShare Give accessShare full text accessShare full-text accessPlease review our Terms and Conditions of Use and check box below to share full-text version of article.I have read and accept the Wiley Online Library Terms and Conditions of UseShareable LinkUse the link below to share a full-text version of this article with your friends and colleagues. Learn more.Copy URL Vizentin-Bugoni, J., Maruyama, P.K., Debastiani, V.J., da S. Duarte, L., Dalsgaard, B. & Sazima, M. (2016) Influences of sampling effort on detected patterns and structuring processes of a Neotropical plant-hummingbird network. Journal of Animal Ecology, 85, 262-272. An error has been identified by the authors in the plant abundance data published in Vizentin-Bugoni et al. (2016). The correction results in a slight alteration to the trajectories of models including abundances (Figure 2 in Vizentin-Bugoni et al. 2016). However, the order of the best models remained the same. The corrected Fig. 2 is provided below. Figure 2Open in figure viewerPowerPoint Ability of eight models to predict observed frequency of interaction between pairwise species over increasing sampling effort in a plant–hummingbird network. Models are probability matrices based on species abundance (A), phenological overlap (P), morphological matching (M) and all possible combinations among them. The Null model is a benchmark model that assumes all interactions have the same probability to occur. Note that after 5 h of sampling effort, the model PM, which includes both phenological overlap and bill-corolla (morphological) matching, had the best ability to predict pairwise interaction, while those models including A had worst fits, even worse than the Null model. This means that the higher importance of forbidden links in detriment of abundances was identified even under low sampling. We also show the change in coefficient of correlation between the observed frequency of pairwise interactions and the frequency predicted by the best model PM (right axe, black line with dots in the plot). Note that the correlation coefficient tends to increase with sampling effort (up to c. 15 h). All correlations were P < 0·001. Corrections have also been made to the Supporting Information Tables A1 and A10 in Vizentin-Bugoni et al. (2016). Reference Vizentin-Bugoni, J., Maruyama, P.K., Debastiani, V.J., da S. Duarte, L., Dalsgaard, B. & Sazima, M. (2016) Influences of sampling effort on detected patterns and structuring processes of a Neotropical plant-hummingbird network. Journal of Animal Ecology, 85, 262– 272. doi: 10.1111/1365-2656.12459. Volume85, Issue4July 2016Pages 1131-1131 FiguresReferencesRelatedInformation
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