Editorial Type:
Article Category: Research Article
 | 
Online Publication Date: 11 Mar 2022

Evidence for Negative Impacts on Terrestrial Salamanders following Invasive Plant Removal

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Page Range: 92 – 98
DOI: 10.1670/21-018
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ABSTRACT

Invasive species are widely believed to be a major threat to biodiversity. Therefore, invasive species control is a common practice among land managers. However, the impacts of invasive species control on nontarget organisms are often unknown. To examine the impact of invasive plant removal on a functionally important, but often overlooked, group of organisms, we carried out a field experiment focusing on terrestrial salamanders. Using coverboards, we monitored the occurrence of terrestrial salamanders (primarily Northern Ravine Salamanders, Plethodon electromorphus) in forest plots where invasive plants had been experimentally removed compared with control plots where removal did not occur. We replicated this design at three study sites and sampled coverboards over 3 yr (2016–2018; 2,187 sampling events). We also undertook a laboratory experiment exposing Northern Two-Lined Salamanders (Eurycea bislineata) to native and invasive plant root extracts compared with a plain water control. Results from occupancy modeling and other analytical techniques indicated strongly reduced occupancy of P. electromorphus in plots where invasive plants were removed, compared with controls. This pattern varied among study sites but was strongest at the most heavily invaded sites. Results from the laboratory exposure study showed no significant differences in response to root extracts from native versus invasive plants. Together, these data suggest that some terrestrial salamanders may not be negatively impacted by invasive plants and that invasive plant removal, when not accompanied by native plant restoration, may have unanticipated negative effects on terrestrial salamander populations.

Copyright: Copyright 2022 Society for the Study of Amphibians and Reptiles 2022
Fig. 1.
Fig. 1.

Mean annual observed proportion of coverboards occupied by Northern Ravine Salamanders (Plethodon electromorphus) in control and treatment (invasive plant removal) plots at three study sites, 2016–2018 (n = 2,187) ± 2 SE. There was a significant difference in the frequency of coverboards occupied between treatments (F = 41.21, df = 1,2, P = 0.023) and between study sites (F = 44.58, df = 1,2, P = 0.022) as well as a significant treatment-study site interaction (F = 45.84, df = 1,2, P = 0.021). The College of Wooster Golf Course forest and Walton Woods were heavily invaded by invasive plants, Fern Valley was not.


Fig. 2.
Fig. 2.

Comparison of abiotic conditions in control and invasive plant removal plots at three study sites. No statistically significant differences were found between treatment and control plots in soil surface temperature (panel A; F = 0.003, df = 1, P = 0.954) or leaf litter depth (panel C; F = 0.93, df = 1, P = 0.336). However, soil moisture was significantly higher in treatment plots (panel B; F = 29.36, df = 1, P < 0.001). Means are presented ± 2 SE.


Fig. 3.
Fig. 3.

Mean proportion of time spent by Northern Two-Lined Salamanders (Eurycea bislineata) on filter paper in petri dishes infused with native plant root extracts, invasive plant root extracts, or plain water (control) in 30-min trials (n = 63 trials). Significantly more time was spent on the control filter paper (W = 2.05, n = 63, P = 0.040) but time spent on filter papers with plant extracts did not differ from random (all P > 0.10). Means are presented ± 2 SE.


Contributor Notes

Corresponding Author. Email: rlehtinen@wooster.edu
Accepted: 18 Aug 2021
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