Abstract

Fire has historically played an important role in shaping the structure and composition of Sonoran semi-desert grassland vegetation. Yet, human use and land management activities have significantly altered arid grassland ecosystems over the last century, often producing novel fuel conditions. The variety of continuously updated satellite remote sensing systems provide opportunities for efficiently mapping combustible fine-fuels and fuel-types (e.g., grass, shrub, or tree cover) over large landscapes that are helpful for evaluating fire hazard and risk. For this study, we compared field ceptometer leaf area index (LAI) measurements to conventional means for estimating fine-fuel biomass on 20, 50 m × 20 m plots and 431, 0.5 m × 0.5 m quadrats on the Buenos Aires National Wildlife Refuge (BANWR) in southern Arizona. LAI explained 65% of the variance in fine-fuel biomass using simple linear regression. An additional 19% of variance was explained from Random Forest regression tree models that included herbaceous plant height and cover as predictors. Field biomass and vegetation measurements were used to map fine-fuel and vegetation cover (fuel-type) from plots on BANWR comparing outcomes from multi-date (peak green and dormant period) Worldview-3 (WV3) and Landsat Operational Land Imager (OLI) imagery. Fine-fuel biomass predicted from WV3 imagery combined with terrain information from a digital elevation model explained greater variance using regression tree models (65%) as compared to OLI models (58%). Vegetation indices developed using red-edge bands as well as modeled bare ground and herbaceous cover were important to improve WV3 biomass estimates. Land cover classification for 11 cover categories with high spatial resolution WV3 imagery showed 80% overall accuracy and highlighted areas dominated by non-native grasses with 87% user’s class accuracy. Mixed native and non-native grass and shrublands showed 59% accuracy and less common areas dominated by native grasses on plots showed low class accuracy (23%). Digital data layers from WV3 models showed a significantly positive relationship (r2 = 0.68, F = 119.2, p < 0.001) between non-native grass cover (e.g., Eragrostis lehmanniana) and average fine-fuel biomass within refuge fire management units. Overall, both WV3 and OLI produced similar fine-fuel biomass estimates although WV3 showed better model performance and helped characterized fine-scale changes in fuel-type and continuity across the study area.

Highlights

  • Fuel and fire hazard estimates from remotely sensed data are frequently sought because of the prevalence of wildland fires in the western US and the need to assess potential fire behavior [1].While a great deal of attention has been paid to characterizing forest canopy fuels [2], fewer efforts have focused on estimating arid grassland fuel conditions [3,4]

  • The final model resulted in 84% of the variation explained and a root mean squared error (R3M.1.SIEn)-Soiftu0.B97iomg/amss 2R. eFsruoltms variable importance plots, we found that ceptometer leaf area index (LAI) was the most imporHtaenrtbparceedoiuctsobrivoamriaasbsleclwiphpeendcformompanre=d 4to31alqluoathderratqsuoandr2a0t-pscloaltes prarendgiecdtofrrso. mBo0th.0pge/rmce2nttoM18S5E.4 ang/dmn2oadnedpuavrietyraignecdre2a5se.8d gsi/mmi2la±rl2y5.w5.itUh sLinAgI h1e0l-dfooldutcorfosRsFvmaloiddaetlsio(nFigasuroeu4rAR.BF)E

  • We found that in this landscape, field ceptometer measurements combined with WV3 or Operational Land Imager (OLI) image data produced biomass estimates well within the range of anticipated values for semi-desert grasslands

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Summary

Introduction

Fuel and fire hazard estimates from remotely sensed data are frequently sought because of the prevalence of wildland fires in the western US and the need to assess potential fire behavior [1].While a great deal of attention has been paid to characterizing forest canopy fuels [2], fewer efforts have focused on estimating arid grassland fuel conditions [3,4]. Fuel and fire hazard estimates from remotely sensed data are frequently sought because of the prevalence of wildland fires in the western US and the need to assess potential fire behavior [1]. Fine-fuels and fuel-type (e.g., grass, grass-shrub, tree, woody debris) are principal vegetation parameters needed to assign fuel model types used as inputs to fire behavior models [8]. Fire behavior models such as FlamMap, FARSITE, and BEHAVE require fuel model types representative of fuel conditions to help determine potential fire behavior such as rates of spread, minimum travel time, and transition from a surface to crown fire [9,10,11,12]. Fuel characteristics are frequently obtained from remote sensing which offers an increasingly diverse set of tools for mapping surface and canopy fuels [4,13,14]

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