Rapid Monitoring of the Abundance and Spread of Exotic Annual Grasses in the Western United States Using Remote Sensing and Machine Learning

Exotic annual grasses (EAG) are one of the most damaging agents of change in western North America. Despite known socio‐environmental effects of EAG there remains a need to enhance monitoring capabilities for better informing conservation and management practices. Here, we integrate field observations, remote sensing and climate data with machine‐learning techniques to estimate and assess patterns of historical (1985–2019; R2 = 0.86 ± 0.05; MAE = 6.7 ± 1.4%), present (2020), and future (2025–2040) EAG abundance (30‐m) across much of the western United States. Trend analysis revealed that ∼8% and 1% of the landscape experienced significant rises and declines in historical EAG cover, respectively, with hotspots of invasion generally occurring near roads and along low‐to‐mid elevation gradients with warmer and drier conditions. Accurate simulations of the response of EAG to changing environmental conditions, disturbances and management treatments indicate that ecosystem resistance to invasion is largely controlled by long‐term EAG abundance (surrogate for seed bank), time since and frequency of wildfire, and plant community interactions. Ecological thresholds associated with enhanced probabilities of wildfire occurrence and invasion rates indicate that relatively little (10%) EAG cover is needed to heighten these risks. Climate change is expected to push 8% of the landscape across invasion thresholds by 2040, impacting 6% of existing sage‐grouse habitat, and we identify where fuel breaks may be placed to reduce wildfire risks and invasion. Spatially detailed, timely, and accurate depictions of past, present, and future EAG abundance are vital for the protection of life and property and the continued stewardship of sagebrush ecosystems.

[1]  Trevor Hastie,et al.  Causal Interpretations of Black-Box Models , 2019, Journal of business & economic statistics : a publication of the American Statistical Association.

[2]  Xinyu Li,et al.  Mapping wetland using the object-based stacked generalization method based on multi-temporal optical and SAR data , 2020, Int. J. Appl. Earth Obs. Geoinformation.

[3]  J. Dwyer,et al.  The Landsat Burned Area algorithm and products for the conterminous United States , 2020 .

[4]  D. Roy,et al.  Spatially and temporally complete Landsat reflectance time series modelling: The fill-and-fit approach , 2020 .

[5]  Mark A. Friedl,et al.  Continental-scale land surface phenology from harmonized Landsat 8 and Sentinel-2 imagery , 2020, Remote Sensing of Environment.

[6]  G. Henebry,et al.  Development and evaluation of a new algorithm for detecting 30 m land surface phenology from VIIRS and HLS time series , 2020 .

[7]  Bruce K. Wylie,et al.  Characterizing Land Surface Phenology and Exotic Annual Grasses in Dryland Ecosystems Using Landsat and Sentinel-2 Data in Harmony , 2020, Remote. Sens..

[8]  Hua Shi,et al.  Quantifying Western U.S. Rangelands as Fractional Components with Multi-Resolution Remote Sensing and In Situ Data , 2020, Remote. Sens..

[9]  N. Horning,et al.  Fire, livestock grazing, topography, and precipitation affect occurrence and prevalence of cheatgrass (Bromus tectorum) in the central Great Basin, USA , 2019, Biological Invasions.

[10]  J. Balch,et al.  Invasive grasses increase fire occurrence and frequency across US ecoregions , 2019, Proceedings of the National Academy of Sciences.

[11]  Anuj Karpatne,et al.  Process‐Guided Deep Learning Predictions of Lake Water Temperature , 2019, Water Resources Research.

[12]  Brittany S. Barker,et al.  Pre‐fire vegetation drives post‐fire outcomes in sagebrush ecosystems: evidence from field and remote sensing data , 2019, Ecosphere.

[13]  C. Tucker,et al.  Assessing precipitation, evapotranspiration, and NDVI as controls of U.S. Great Plains plant production , 2019, Ecosphere.

[14]  C. Allen,et al.  Operationalizing Ecological Resilience Concepts for Managing Species and Ecosystems at Risk , 2019, Front. Ecol. Evol..

[15]  Robert S. Arkle,et al.  Soil characteristics are associated with gradients of big sagebrush canopy structure after disturbance , 2019, Ecosphere.

[16]  Cameron L. Aldridge,et al.  The ecological uncertainty of wildfire fuel breaks: examples from the sagebrush steppe , 2019, Frontiers in Ecology and the Environment.

[17]  D. Twidwell,et al.  Recoupling fire and grazing reduces wildland fuel loads on rangelands , 2019, Ecosphere.

[18]  C. Justice,et al.  The Harmonized Landsat and Sentinel-2 surface reflectance data set , 2018, Remote Sensing of Environment.

[19]  R. Tausch,et al.  Resilience and resistance in sagebrush ecosystems are associated with seasonal soil temperature and water availability , 2018, Ecosphere.

[20]  Jeremy D. Maestas,et al.  Innovation in rangeland monitoring: annual, 30 m, plant functional type percent cover maps for U.S. rangelands, 1984–2017 , 2018, Ecosphere.

[21]  Robert S. Arkle,et al.  Thresholds and hotspots for shrub restoration following a heterogeneous megafire , 2018, Landscape Ecology.

[22]  K.,et al.  A conservation planning tool for Greater Sage-grouse using indices of species distribution, resilience, and resistance. , 2018, Ecological applications : a publication of the Ecological Society of America.

[23]  J. Abatzoglou,et al.  Defoliation severity is positively related to soil solution nitrogen availability and negatively related to soil nitrogen concentrations following a multi-year invasive insect irruption , 2020, AoB PLANTS.

[24]  Tomislav Hengl,et al.  Improving performance of spatio-temporal machine learning models using forward feature selection and target-oriented validation , 2018, Environ. Model. Softw..

[25]  D. Pyke,et al.  Fire and Grazing Influence Site Resistance to Bromus tectorum Through Their Effects on Shrub, Bunchgrass and Biocrust Communities in the Great Basin (USA) , 2018, Ecosystems.

[26]  Michael Dixon,et al.  Google Earth Engine: Planetary-scale geospatial analysis for everyone , 2017 .

[27]  Robert S. Arkle,et al.  Refining the cheatgrass–fire cycle in the Great Basin: Precipitation timing and fine fuel composition predict wildfire trends , 2017, Ecology and evolution.

[28]  John A. Silander,et al.  Invasion Dynamics , 2017 .

[29]  Kristofer D. Johnson,et al.  Historical and projected trends in landscape drivers affecting carbon dynamics in Alaska. , 2017, Ecological applications : a publication of the Ecological Society of America.

[30]  Jennifer K. Balch,et al.  Human-started wildfires expand the fire niche across the United States , 2017, Proceedings of the National Academy of Sciences.

[31]  D. Apley,et al.  Visualizing the effects of predictor variables in black box supervised learning models , 2016, Journal of the Royal Statistical Society: Series B (Statistical Methodology).

[32]  Nagiza F. Samatova,et al.  Theory-Guided Data Science: A New Paradigm for Scientific Discovery from Data , 2016, IEEE Transactions on Knowledge and Data Engineering.

[33]  Seth R Flaxman,et al.  Improved prediction accuracy for disease risk mapping using Gaussian process stacked generalization , 2016, Journal of The Royal Society Interface.

[34]  Bradley C Fedy,et al.  Importance of regional variation in conservation planning: a rangewide example of the Greater Sage‐Grouse , 2016 .

[35]  B. Wylie,et al.  Near-Real-Time Cheatgrass Percent Cover in the Northern Great Basin, USA, 2015 , 2016, Rangelands.

[36]  Brian J. Harvey,et al.  Changing disturbance regimes, ecological memory, and forest resilience , 2016 .

[37]  L. Ziska,et al.  Cheatgrass is favored by warming but not CO2 enrichment in a semi‐arid grassland , 2016, Global change biology.

[38]  Eric F. Wood,et al.  POLARIS: A 30-meter probabilistic soil series map of the contiguous United States , 2016 .

[39]  Yaxing Wei,et al.  Daymet: Daily Surface Weather Data on a 1-km Grid for North America, Version 3 , 2016 .

[40]  Bruce K. Wylie,et al.  Cheatgrass Percent Cover Change: Comparing Recent Estimates to Climate Change — Driven Predictions in the Northern Great Basin☆,☆☆ , 2016, Rangeland Ecology and Management.

[41]  James M. Omernik,et al.  Ecoregions of the Conterminous United States: Evolution of a Hierarchical Spatial Framework , 2014, Environmental Management.

[42]  P. Adler,et al.  Warming, competition, and Bromus tectorum population growth across an elevation gradient , 2014 .

[43]  M. Joseph Hughes,et al.  Automated Detection of Cloud and Cloud Shadow in Single-Date Landsat Imagery Using Neural Networks and Spatial Post-Processing , 2014, Remote. Sens..

[44]  M. Moritz,et al.  Large wildfire trends in the western United States, 1984–2011 , 2014 .

[45]  C. Aldridge,et al.  Human Infrastructure and Invasive Plant Occurrence Across Rangelands of Southwestern Wyoming, USA , 2014 .

[46]  Stuart P. Hardegree,et al.  Resilience to Stress and Disturbance, and Resistance to Bromus tectorum L. Invasion in Cold Desert Shrublands of Western North America , 2013, Ecosystems.

[47]  P. Weisberg,et al.  Influence of climate and environment on post-fire recovery of mountain big sagebrush , 2014 .

[48]  Ramakrishna R. Nemani,et al.  Downscaled Climate Projections Suitable for Resource Management , 2013 .

[49]  Peter M. Atkinson,et al.  Downscaling in remote sensing , 2013, Int. J. Appl. Earth Obs. Geoinformation.

[50]  J. Balch,et al.  Introduced annual grass increases regional fire activity across the arid western USA (1980–2009) , 2013, Global change biology.

[51]  Jan Pergl,et al.  A global assessment of invasive plant impacts on resident species, communities and ecosystems: the interaction of impact measures, invading species' traits and environment , 2012, Global Change Biology.

[52]  Karl E. Taylor,et al.  An overview of CMIP5 and the experiment design , 2012 .

[53]  R. Scott,et al.  Invasion of shrublands by exotic grasses: ecohydrological consequences in cold versus warm deserts , 2012 .

[54]  M. Reeves,et al.  Extent of Coterminous US Rangelands: Quantifying Implications of Differing Agency Perspectives , 2011 .

[55]  R. Neilson,et al.  Impacts of climate change on fire regimes and carbon stocks of the U.S. Pacific Northwest , 2011 .

[56]  K. Calvin,et al.  The RCP greenhouse gas concentrations and their extensions from 1765 to 2300 , 2011 .

[57]  Gaël Varoquaux,et al.  Scikit-learn: Machine Learning in Python , 2011, J. Mach. Learn. Res..

[58]  Christopher M. McGlone,et al.  Invasion resistance and persistence: established plants win, even with disturbance and high propagule pressure , 2011, Biological Invasions.

[59]  B. Bradley Assessing ecosystem threats from global and regional change: hierarchical modeling of risk to sagebrush ecosystems from climate change, land use and invasive species in Nevada, USA , 2010 .

[60]  B. Bradley Regional analysis of the impacts of climate change on cheatgrass invasion shows potential risk and opportunity , 2009 .

[61]  R. Nowak,et al.  Variation in the establishment of a non-native annual grass influences competitive interactions with Mojave Desert perennials , 2007, Biological Invasions.

[62]  B. Roundy,et al.  WHAT MAKES GREAT BASIN SAGEBRUSH ECOSYSTEMS INVASIBLE BY BROMUS TECTORUM , 2007 .

[63]  John F. Mustard,et al.  Invasive grass reduces aboveground carbon stocks in shrublands of the Western US , 2006 .

[64]  J. Mustard,et al.  Characterizing the landscape dynamics of an invasive plant and risk of invasion using remote sensing. , 2006, Ecological applications : a publication of the Ecological Society of America.

[65]  L. Jost Entropy and diversity , 2006 .

[66]  Rich Caruana,et al.  Predicting good probabilities with supervised learning , 2005, ICML.

[67]  John F. Mustard,et al.  Identifying land cover variability distinct from land cover change: Cheatgrass in the Great Basin , 2005 .

[68]  Dylan Keon,et al.  Equations for potential annual direct incident radiation and heat load , 2002 .

[69]  D. Simberloff,et al.  BIOTIC INVASIONS: CAUSES, EPIDEMIOLOGY, GLOBAL CONSEQUENCES, AND CONTROL , 2000 .

[70]  P. Vitousek,et al.  Biological invasions by exotic grasses, the grass/fire cycle, and global change , 1992 .

[71]  David H. Wolpert,et al.  Stacked generalization , 1992, Neural Networks.

[72]  Brady W. Allred,et al.  Operationalizing Resilience and Resistance Concepts to Address Invasive Grass-Fire Cycles , 2019, Front. Ecol. Evol..

[73]  Zhe Zhu,et al.  Mapping forest change using stacked generalization: An ensemble approach , 2018 .

[74]  Cynthia S. Brown,et al.  Exotic Annual Bromus Invasions: Comparisons Among Species and Ecoregions in the Western United States , 2016 .

[75]  Jeffrey L. Beck,et al.  Land Uses, Fire, and Invasion: Exotic Annual Bromus and Human Dimensions , 2016 .

[76]  B. Bradley,et al.  Bromus Response to Climate and Projected Changes with Climate Change , 2016 .

[77]  Megan K. Creutzburg,et al.  Climate Change and Land Management in the Rangelands of Central Oregon , 2014, Environmental Management.

[78]  Jeremy D. Maestas,et al.  Using resistance and resilience concepts to reduce impacts of invasive annual grasses and altered fire regimes on the sagebrush ecosystem and greater sage-grouse: A strategic multi-scale approach , 2014 .

[79]  Damaris Zurell,et al.  Collinearity: a review of methods to deal with it and a simulation study evaluating their performance , 2013 .

[80]  George Sugihara,et al.  Thresholds of Climate Change in Ecosystems: Final Report, Synthesis and Assessment Product 4.2 , 2009 .

[81]  Michael J. Oimoen,et al.  The National Elevation Dataset , 2002 .

[82]  W. D. Billings The Earth in Transition: Bromus tectorum , a Biotic Cause of Ecosystem Impoverishment in the Great Basin , 1991 .