Editorial Type:
Article Category: Research Article
 | 
Online Publication Date: 03 Nov 2017

Response of Lizards to High-Severity Wildfires in a Southern United States Mixed Pine/Hardwood Forest

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Page Range: 609 – 617
DOI: 10.1643/CH-16-516
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High-severity forest fires are increasing in large areas of the southern and western United States as the climate becomes warmer and drier. Natural resource managers need a better understanding of the short- and long-term effects of wildfires on lizard populations, but there is a paucity of studies focused on lizard-wildfire relationships. We used a before-after, control-impact (BACI) sample design to assess the response of three lizard species—Six-lined Racerunner (Aspidoscelis sexlineata), Prairie Lizard (Sceloporus consobrinus), and Little Brown Skink (Scincella lateralis)—to high-severity wildfires that occurred in the Lost Pines Ecoregion, Texas, USA. Specifically, we analyzed monitoring data collected across 17 trapping sessions from spring 2008 to spring 2013 using stratified N-mixture models to estimate trends in lizard abundances, while accounting for environmental parameters that might influence lizard detectability. We found no evidence of a fire-induced change in abundance for any of the lizard species we studied, but there was an increase in detectability of A. sexlineata following the wildfires. Detectability of A. sexlineata and S. lateralis increased with air temperature, detectability of S. consobrinus decreased with precipitation, and detectability was related to Julian day for all three species. Mean detection probabilities were low (<0.1), suggesting capture-mark-recapture methods at a subset of sample units should be implemented to derive more accurate estimates in future monitoring efforts. Our results provide quantitative evidence of the short-term effects of high-severity wildfires on three widely distributed lizard species. Given the wildfires did not result in decreased lizard abundances, managers should minimize their vehicle footprints off of roads during post-wildfire habitat restoration to avoid soil compaction and the potential for direct mortality.

Copyright: © 2017 by the American Society of Ichthyologists and Herpetologists
<bold>Fig. 1.</bold>
Fig. 1.

Aerial image of the Griffith League Ranch (GLR), Bastrop County, Texas, USA and its location with respect to the high-severity wildfires that occurred in the Lost Pines Ecoregion in September and October 2011. Overlain on the image are the fires and the locations of the drift-fence arrays and ponds. On the right, images of the terrestrial habitat around a drift-fence array on the GLR before (A), shortly after (B), and ca. 1 y after (C) the fires.


<bold>Fig. 2.</bold>
Fig. 2.

Fitted values of abundance and 95% credible intervals for Aspidoscelis sexlineata, Sceloporus consobrinus, and Scincella lateralis on the Griffith League Ranch (GLR), Bastrop County, Texas, USA, spring 2008–spring 2013. Trapping sessions are grouped by year and vertical dashed lines indicate when wildfires occurred.


<bold>Fig. 3.</bold>
Fig. 3.

Mean model intercept and coefficient estimates with 95% credible intervals from the selected model for Aspidoscelis sexlineata, Sceloporus consobrinus, and Scincella lateralis on the Griffith League Ranch (GLR), Bastrop County, Texas, USA, spring 2008–spring 2013. See text for further details on notation, and note the different ranges on the axes.


Contributor Notes

Associate Editor: J. W. Snodgrass.

Received: 28 Sept 2016
Accepted: 19 Jun 2017
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