Spatial and temporal variability in the effects of wildfire and drought on thermal habitat for a desert trout
Introduction
The influences of climate on Earth are often portrayed as systematic trends through time (Loarie et al., 2009), but change itself is not stationary (Milly et al., 2008). For example, as climate changes, it is broadly anticipated that the probability of episodic disturbances will also change (Running, 2008). Ecologically, this means that species will have to contend with a host of acute and chronic exposures (Foden et al., 2013) to changing climates. Such uncertainties regarding climate itself provide many challenges for anticipating ecological responses to climate change (Wenger et al., 2013). Here we focus on two common episodic, climate-driven ecological disturbances: drought (Lake, 2011) and wildfire (Westerling, 2016). Both of these disturbances are driven by the intersection of precipitation deficits and warm temperatures, and are thus likely to manifest at the same time within a given area (Diffenbaugh et al., 2015, Ganguli and Ganguly, 2016).
In this study we consider the influences of drought and wildfire on stream temperatures. Stream temperature is well-known to be sensitive to both meteorological variability (i.e. drought-related; Caissie, 2006, Diabat et al., 2013, Luce et al., 2014) and wildfires (Hitt, 2003, Dunham et al., 2007, Mahlum et al., 2011). In the northern Great Basin desert, the onset of meteorological and hydrological drought (Wilhite and Glantz, 1985) has increasingly coincided with large wildfires (Denison et al., 2014, Westerling, 2016). Wildfires often burn riparian vegetation, leading to loss of shade and warming of stream temperatures (Dunham et al., 2007, Mahlum et al., 2011), which may further warm if streams experience reduced flows during drought. Because a host of factors can influence stream temperatures and sensitivity to drought and wildfire (e.g., riparian and topographic shading, surface-subsurface heat fluxes) specific responses can be variable and difficult to predict. We used a combination of opportunistically available records of stream temperature (from temperature data loggers in operation before and after a large wildfire), a regional model of stream temperatures from before a wildfire and drought (Isaak et al., 2016a), and a network of temperature loggers deployed after a fire and during the height of an ongoing drought (i.e., 2015; Fig. 1) to evaluate how both wildfire and drought influenced temperatures across a large, desert stream network.
Specifically, our objectives were to: 1) quantify the magnitude and duration of influences of wildfire on stream temperature at sites with pre- and post-wildfire temperature data, 2) evaluate spatial variation in responses of summer stream temperature throughout the entire stream network during the latter stages of the drought to a baseline of predictions from a stream temperature model assembled with data from 1993 to 2011 (Isaak et al., 2016a), and 3) assess the ecological consequences of conditions observed during the 2015 drought year for a sensitive species (Lahontan cutthroat trout, [Oncorhynchus clarkii henshawi]; Jones et al., 1998). Collectively, results of this work provide novel insights into how aquatic ecosystems respond to the combined influences of drought and wildfire, two interactive disturbances that are more likely to occur as climate change proceeds (Lake, 2011, Diffenbaugh et al., 2015, Westerling, 2016).
Section snippets
Study area
Our study was focused in the Willow and Whitehorse creeks watershed (hereafter, Willow-Whitehorse watershed) of southeast Oregon (Fig. 2). The watershed is characteristic of Great Basin sage-steppe, consisting mostly of open rangelands with elevations of 1300–2250 m, including 200–400 m deep canyons draining northward into the endorheic Coyote Lake Basin (Grayson, 2011). The watershed contains 262 km of intermittent-classified stream channels in the National Hydrography Dataset Plus V2
Results
The NHDPlus perennial classification was incorrect at >30% of sites visited in 2014 and 2015. In 2014, 51 of 73 perennial-classified sampling points (including both GRTS and re-located ODFW points) had surface water during initial visits, while 22 were completely dry; only 3 of the 33 intermittent-classified sample points contained surface water. Similarly, only 48 of the perennial-classified sites had surface water during 2015 fieldwork. With fieldwork in 2015, we successfully relocated
Discussion
Results of this study provide unique insights into the progressive effects of drought on stream networks. Within the Willow-Whitehorse stream network, the effects of drought and wildfire were closely linked. The 2012 Holloway Fire coincided with a precipitous change in a major drought indicator, the Palmer Drought Severity Index (PDSI, Fig. 1), a relationship that is prevalent throughout the historical record in the region (Westerling, 2016). Stream temperatures warmed immediately in response
Acknowledgments
We would like to thank N. Hitt, N. Chelgren, and D. Roon for discussion and suggestions to improve this study. Fieldwork assistance was generously provided by C. Bailey, J. Blake, B. Jones, M. McGuire, J. Pearson, B. Sempert, and A. Wong.
Funding for this study was provided by the Vale office of the Bureau of Land Management, the Department of the Interior Northwest Climate Science Center, and the U.S. Geological Survey National Climate Change and Wildlife Science Center. Additional support was
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