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. 2014 Sep 12;9(9):e107037.
doi: 10.1371/journal.pone.0107037. eCollection 2014.

Incorporating climate change and exotic species into forecasts of riparian forest distribution

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Incorporating climate change and exotic species into forecasts of riparian forest distribution

Dana H Ikeda et al. PLoS One. .

Abstract

We examined the impact climate change (CC) will have on the availability of climatically suitable habitat for three native and one exotic riparian species. Due to its increasing prevalence in arid regions throughout the western US, we predicted that an exotic species, Tamarix, would have the greatest increase in suitable habitat relative to native counterparts under CC. We used an ecological niche model to predict range shifts of Populus fremontii, Salix gooddingii, Salix exigua and Tamarix, from present day to 2080s, under five general circulation models and one climate change scenario (A1B). Four major findings emerged. 1) Contrary to our original hypothesis, P. fremontii is projected to have the greatest increase in suitable habitat under CC, followed closely by Tamarix. 2) Of the native species, S. gooddingii and S. exigua showed the greatest loss in predicted suitable habitat due to CC. 3) Nearly 80 percent of future P. fremontii and Salix habitat is predicted to be affected by either CC or Tamarix by the 2080s. 4) By the 2080s, 20 percent of S. gooddingii habitat is projected to be affected by both Tamarix and CC concurrently, followed by S. exigua (19 percent) and P. fremontii (13 percent). In summary, while climate change alone will negatively impact both native willow species, Tamarix is likely to affect a larger portion of all three native species' distributions. We discuss these and other results in the context of prioritizing restoration and conservation efforts to optimize future productivity and biodiversity. As we are accounting for only direct effects of CC and Tamarix on native habitat, we present a possible hierarchy of effects- from the direct to the indirect- and discuss the potential for the indirect to outweigh the direct effects. Our results highlight the need to account for simultaneous challenges in the face of CC.

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Conflict of interest statement

Competing Interests: The authors have declared that no competing interests exist.

Figures

Figure 1
Figure 1. Marginal response curves for each climatic variable.
Response curves depicting the probability of suitable habitat related to each climatic variable for Populus fremontii, Salix gooddingii, Salix exigua and Tamarix. Units of precipitation variables are measured in millimeters (mm), and temperature variables are degrees Celsius times 10 (°C*10). See Table 1 for full variable names.
Figure 2
Figure 2. Maxent model outputs showing range expansion and contraction of suitable habitat predicted through time as a result of CC.
A) Suitable habitat in current time is shown in grey using a liberal threshold (T10), with the occurrence data overlaid. All occurrence data were downloaded from the Global Biodiversity Information Facility. B-C) Suitable habitat in 2050s and 2080s, predicted by four or more GCMs using a liberal threshold (T10) is also depicted. Areas of loss (red), gain (green), and stable (grey) were calculated by subtracting suitable habitat from the previous time frame.
Figure 3
Figure 3. Native species distributions affected by CC or Tamarix.
Projected distributions of the three native species (grey) showing the range predicted to be affected by either Tamarix invasion (red) between current and 2080 (A-C) or CC (black) between 2050 and 2080 (B-C).
Figure 4
Figure 4. Locations projected to be affected by CC and Tamarix concurrently.
The projected distributions of three native species depicting the areas with the potential for exotic-by-climate interactions (i.e. the effect of Tamarix and habitat loss due to CC) in A) 2050s and B) 2080s.

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