Towards Validation of DEVS-FIRE Wildfire Simulation Model

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1 Towards Validation of DEVS-FIRE Wildfire Simulation Model Feng Gu Dept. of Computer Science Georgia State University Atlanta, GA, 333 Xiaolin Hu Dept. of Computer Science Georgia State University Atlanta, GA, 333 Lewis Ntaimo Dept. of Industrial & Systems Engineering TAMU 3131 TAMU College Station, TX Keywords: validation, wildfire, cellular space model, DEVS- FIRE Abstract DEVS-FIRE is a model for discrete event simulation of wildfire spread, where fire spread is modeled as a contagion process in a cellular space of forest cells. In this paper, DEVS- FIRE is validated using FARSITE, a widely used fire spread model. Both graphical and statistical approaches are used and the results show that the output of DEVS-FIRE is comparable to that of FARSITE under a wide range of input conditions. 1. INTRODUCTION Wildfires cause tremendous loss of natural resources, endangered species, human lives and property each year. It is estimated that more than 11, communities adjacent to federal lands are at risk from wildfires[1]. It costs about a billion dollars annually in efforts to contain wildfires in the US alone[2]. The ability to understand and predict wildfire intensity, direction, location, rate of spread, and burned area as quickly as possible is important for effective wildfire management and emergency response. Towards this goal, we are developing a decision-making support tool that integrates fire spread simulation, fire fighting resources optimization, and fire suppression simulation together. DEVS-FIRE[3] is a key component of this project that allows to support discrete event simulation of wildfire spread. In DEVS-FIRE, fire spread is modeled as a diffusion process in a cellular space of forest cells. This paper presents validation of the DEVS-FIRE model by comparing its simulation output with that of FAR- SITE, a widely used fire spread model. Model validation refers to building the right model. There are several methods for model validation but the three general methods are the objective, the subjective, and the combinational method[4]. The objective method uses mathematical or statistical tools while the subjective method relies on knowledge of experts or requirements of users. The combinational method is a combination of the objective method and the subjective method. In carrying out model validation, several techniques can be used. These include animation to graphically display the results, comparison with other validated models, and hypothesis test, which utilizes statistics to verify whether the assumptions are correct or not[4]. Several wildfire spread models have been developed to date. These include BehavePlus[5], HFire[6], FARSITE[7], and DEVS-FIRE[3]. Most of the models have been validated to some degree using real data[8][9][1]. One of problems in validating wildfire models is that it is difficult to collect accurate input data from the real system. These data include real-time wind speed, wind direction, fuels, and landscape data. Precisely specifying an area with parameters such as fuel models, slope and aspect, is also difficult since a real geographical space is complicated to describe using a series of numbers. Another issue is collecting accurate real-time wildfire output data such as fire perimeters and areas burned at different time steps. In this paper we use FARSITE, which is a partially validated model[1], to validate DEVS-FIRE. This is a step towards the validation of DEVS-FIRE using real data in the near future. The rest of this paper is organized as follows. Section 2 briefly reviews closely related work. Section 3 gives an overview of the DEVS-FIRE model and highlights the major factors that affect fire spread simulation results. Section 4 gives the experimental results and analysis. The last section draws the conclusions about the validation work and points out future work. 2. RELATED WORK Wildfire spread models are used to predict fire spread patterns, including how fast the fires will spread and what areas will be ignited. This information is used in controlling and fighting the fires before and after they occur. According to[11], most wildfire growth models can be classified into three categories, which include empirical models, semiempirical models, and physical models. To create an empirical model, data are collected to statistically predict the fire behaviors, whereas in creating a semi-empirical model a global energy balance principle is utilized as the basic assumption[11]. Physical models are primarily based on the physics of fire behaviors. Rothermel s model[12], one of the most popular semi-empirical models, is the basis of many wildfire spread models, including BehavePlus[5] and FAR- SITE[7]. It is also the fire behavior model used in DEVS- FIRE[3]. There are two common approaches used for wildfire behavior simulation using semi-empirical models. The first one is the cellular approach, where fire spread is treated as a discrete process of ignitions in a cellular space. In such models (e.g.[3]), the maximum fire rate of spread and direction are

2 computed for each cell, and then decomposed using an elliptical shape to get the spread rates in other directions. Therefore, the times needed for the fire to spread from one cell to its neighbors can easily be calculated. Another is the vector approach, in which the fire front expands as a continuous fire polygon at specified time steps. In FARSITE, for example, fire spreads as an ellipse at any given time step. Fire spread in all directions at the next time step is computed using the current elliptical information through Huygens principle[7]. Since FARSITE was developed, real data have been collected to test and evaluate using historical wildfire data. In[13], the horizon prescribed natural fire at Yosemite National Park, which has a well developed GIS data, was used to initially test the FARSITE simulator. The Howling Fire at Glacier National Park was also used to evaluate the projection method in FARSITE. In[1], a fire that occurred in North Sardinia of Italy in the summer 24, provided another case for validation of FARSITE in a Mediterranean area. BehavePlus, an expansion of Behave fire modeling system, is a wildfire model system to describe fire behaviors, fire effects, and the fire environment[5]. According to[8], five models were used to validate the Behave fire behavior in Oak Savannas, and the results show that only fuel model 2 can be used to predict the rate of spread in this area. Another wildfire spread model, HFire (Highly Optimized Tolerance Fire Spread Model), has been validated for fire spread in California s chaparral[6]. In[9], the fire history in Santa Monica Mountains verified by the fire patterns, fire return intervals, and fire size distributions provided a testbed for HFire. 3. OVERVIEW OF THE DEVS-FIRE MODEL DEVS-FIRE is an integrated simulation environment for surface wildfire spread and containment based on the Discrete EVent System Specification (DEVS). DEVS-FIRE uses a dynamic structure cellular space model for simulating fire spread and incorporates real spatial fuels data, landscape data, and weather data. DEVS-FIRE is integrated with a stochastic optimization model that uses the scenario results from the simulation to determine optimal decisions regarding firefighting resource deployment to bases, and dispatch to fires for containment. More information about DEVS-FIRE can be found in[3]. Below we highlight the major factors that affect the fire spread simulation results related to our validation work. One of the major factors that affect the simulated fire shape is the fire decomposition schema. In DEVS-FIRE, the maximum rate of speed is decomposed into eight directions (N, NE, E, SE, S, SW, W, and NW) from the ignition point according to an elliptical shape, as shown in Figure 1. This is different from that of FARSITE, in which all directions can be computed from the ellipse. However, as for the shape of Figure 1. Decomposition of DEVS-FIRE the ellipse, we use the same formula as in FARSITE to calculate its dimensions[7] as follows: LB =.936e.2566U +.461e.1548U.397 HB = (LB + LB 2 1)/(LB LB 2 1) b = (R + R/HB)/2.;c = b R/HB In the above equations, U and R stand for the midflame wind speed (m/s) and the fire spread rate (m/min), respectively. The eccentricity of the ellipse is equal to c/b. We point out that even though DEVS-FIRE and FARSITE use the same underlying fire behavior model, Rothermerl s model, and the same ellipse eccentricity, the two different decomposition schemas of DEVS-FIRE and FARSITE will cause slightly different results (see e.g., Figure 2(a) and 2(b)). Wind is another important factor that influences fire propagation. According to[14], the midflame wind which affects the surface fire, is possibly only ten percent of the wind speed measured by the National Weather Service at 2 feet above the vegetation (2 feet wind). Therefore, a Wind Adjustment Factor (WAF) (also called wind reduction factor) to convert the measured wind is needed. Obviously, WAF is a key consideration for the cellular space model in simulating fire spread more accurately. In[7] and [14], several methods to calculate wind reduction factors or wind adjustment factors are discussed, and some empirical formula and tables are proposed based on different fuel models. For these simulation models, the factors are slightly different in an adjustable range from.3 to.5 for 13 standard fuel models. In our validation, we used the empirical value of WAF for each standard fuel model (1-13) shown in Table EXPERIMENT RESULTS 4.1. Experiment Design To validate DEVS-FIRE, we used multiple methods to compare its output with that of FARSITE for the same data input cases. We also used face validity in the initial stage of

3 Table 1. WAF of Standard Fuel Models Wind Adjustment Factor Standard Fuel Models.3 8, , 3, 5, 6, 7, 1, 11, , 13 Table 2. Input Sets Set Slope Aspect Fuel WSP WDR Set Set ,,15 18,, 4,7,9 5 Set 3 15,,15 18,, 4,7, Set 4 defined defined defined defined defined the validation process. This involved a lot of testing to judge that the system behaviors were according to expected fire behaviors. Table 2 gives four input sets (corresponding to four experiments) that we use in this paper to validate DEVS-FIRE. In the table, WSP and WDR refer to the wind speed and the wind direction respectively. Based on these inputs, we compare two key output parameters, fire spread perimeter and burned area of DEVS-FIRE at given time steps with those of given by FARSITE. Set 1 was used to test under conditions of uniform fuel, unchanged wind speed and wind direction, and zero slope landscape. Set 2 has fuel model, unchanged wind speed and wind direction with different aspects and slopes for the landscape. Set 3 has non-uniform cases with three different combinations of fuel models and landscapes, but with unchanged wind speed and wind direction. Set 4 has real GIS landscape data with changing wind conditions. In this case, a wind model is defined to describe the wind speeds and the wind directions at different time steps. Based on these input sets, we compare the outputs of DEVS-FIRE with those of FARSITE, and then draw the conclusions. For the first two input sets, the graphical method, one of the subjective methods, was used to justify DEVS-FIRE as listed in Table 2. Because their perimeters increase uniformly, we also used hypothesis test, one of the objective methods to compare the models. For the hypothesis test, we define a statistical variable IPEHH (Increased Perimeter Every Half an Hour), and assume it follows the normal distribution. We utilize χ 2 test, F test, and T test to verify that the IPEHHs of two models follow the same distribution. (a) Fuel=7 of FARSITE (c) Fuel=2 of DEVS-FIRE (b) Fuel=7 of DEVS-FIRE (d) WDR=3 of DEVS-FIRE Figure 2. Uniform Case without Slope and Aspect 4.2. The Fuel and The Wind Factors In this experiment, we ran simulations in DEVS-FIRE and FARSITE for ten hours based on input set 1 (shown in Table 2) to validate the factors of the fuel model and the wind under the condition of zero slope landscape. We first used fuel model 7 and set the wind speed at 5 mph, and the wind direction at degree (from north), and then changed the fuel model from 7 to 2. We also changed the wind direction from to 3 degrees. In order to validate against the wind speed factor, we varied the wind speed from to 8 mph. According to these settings, the corresponding results are reported as follows. Figure 2 shows the fire propagation areas of the two models after ten hours. In the figure, the background colors of the window represent the different fuel models. As shown in Figure 2(a), the elliptical shapes refer to the fire perimeters every two hours from the beginning in FARSITE. Figure 2(b), 2(c), and 2(d) show the fire perimeters of DEVS-FIRE at the end of the simulation of ten hours of fire spread. From Figure 2(a) and Figure 2(b), we can see that the fire spread of DEVS- FIRE is consistent with that of FARSITE (see also Figure 3). However, the head of the fire spread in DEVS-FIRE is in a triangle shape, which is different from the FARSITE s elliptical arc. This is because of the decomposition schema of DEVS-FIRE (see Figure 1), while the head of the fire has less decomposition directions as compared to the tail of the fire. Figure 2(c) shows the fire perimeter when using a different fuel model (fuel model=2). This results in slow fire spread as compared to the first fuel model (fuel model=7) in Figure 2(b). Figure 2(d) shows the fire perimeter (fuel model=7)

4 Perimeter(km) DEVSP(Fuel=7) FARSITEP(Fuel=7) DEVSP(Fuel=2) FARSITEP(Fuel=2) DEVSA(Fuel=7) FARSITEA(Fuel=7) DEVSA(Fuel=2) FARSITEA(Fuel=2) Time(hours) Perimeter(km) DEVSP FARSITEP DEVSA FARSITEA Wind Speed(miles/hour) Figure 3. Uniform Cases without Aspect and Slope Figure 4. Uniform Case with Different Wind Speeds when changing the wind direction to 3 degrees. This figure also shows the expected results, and consistent with those of FARSITE. Figure 3 plotted the time-indexed (every half an hour) fire perimeters and areas of DEVS-FIRE and FARSITE for the two fuel models described above. In the figure, DEVSP and FARSITEP refer to perimeters of DEVS-FIRE and FARSITE respectively. Similarly, DEVSA and FARSITEA mean areas of DEVS-FIRE and FARSITE. In DEVS-FIRE, the fire perimeter is calculated based on the sum of outer edges of border cells multiplying the factor of.8. This factor of.8 is because the sum of the outer edges overestimated the perimeter according to the formula of computing perimeters of an ellipse and its circum-rectangle. Figure 4 shows the fire perimeters and areas of ten hours simulation for fuel model 7 when wind speed changed from to 8 mph. Results from both DEVS-FIRE and FARSITE are shown and compared. From Figure 4, we can see that the perimeters and areas of fire propagation increase with wind speed. From Figure 3 and Figure 4, we can see that the fire perimeters and areas of DEVS- FIRE show the same trends as those of FARSITE. Specifically, the fire perimeters of DEVS-FIRE are almost the same as those of FARSITE, and the burned areas of DEVS-FIRE may be smaller than those of FARSITE as the fire grows. This is because the two different fire shapes (see Figure 2(a) and 2(b))result from the decomposition schema The Slope and The Aspect Factor The slope and the aspect (which is defined as the direction the slope is facing-downslope) are two important factors to affect the area and direction of the fire spread. Figure 5 indicates the fire propagation in DEVS-FIRE and FARSITE for ten hours with different cases (aspect=, slope=15; aspect=12, slope=15). From the figures, we can see that the fire spreads slower along southwest when the aspect changes (a) Aspect= and Slope=15 of FARSITE (c) Aspect=12 and Slope=15 of FARSITE (b) Aspect= and Slope=15 of DEVS-FIRE (d) Aspect=12 and Slope=15 of DEVS-FIRE Figure 5. Uniform Case with Aspect and Slope from to 12 degrees. This is because of the downhill slope. According to Figure 5, we can conclude the the aspect and the slope influence the direction, increase or decrease of the rate of spread (Figure 5(b) and Figure 2(b)). In both cases, DEVS-FIRE has very similar results to FARSITE. Figure 6 and Figure 7 show the fire perimeters and areas of DEVS-FIRE and FARSITE at the end of ten hours simulation when the aspect and slope change (with fuel model 7, wind speed 5 mph, and wind direction degree). In Figure 6, the slope is fixed at 15 degrees, and the aspect varies from

5 Perimeter(km) 11.5 DEVSP FARSITEP 11. DEVSA FARSITEA Table 3. Hypothesis Test Results Test GF DEVS-FIRE GF FARSITE F T Aspect(degrees) 2 Figure 6. Data with Different Aspect (a) WDR= of FARSITE (b) WDR= of DEVS-FIRE 14 DEVSP FARSITEP 13 DEVSA FARSITEA Perimeter(km) (c) WDR=45 of FARSITE Figure 8. Non-uniform Cases (d) WDR=45 of DEVS-FIRE Slope(degrees) Figure 7. Data with Different Slope to 36 degrees. In Figure 7, the aspect is, and the slope varies from to 25 degrees. From Figure 7, we observe that when the wind blows uphill, the larger the slope is, the faster the fire spreads. This is expected. Figure 6 shows how the aspects change the fire spread direction and rate of spread. Specifically, the rate of spread is the fastest when the wind blows uphill (aspect=, 36 in Figure 6). The rate of spread is the slowest when the wind blows downhill (aspect=18 in Figure 6). The fire rate of spread is symmetric with respect to the aspect 18 degrees. Table 3 shows the results of hypothesis tests for input set 1 and set 2. In the table, 1-5 stand for five different input combinations used in Table 2; GF is the abbreviation of Goodness of Fit test; F and T refer to the values of F test and T test. According to Table 3, the values of χ 2 for all the cases of DEVS-FIRE and FARSITE are less than the critical value of χ 2 (1,.975)=5.2, which means the IPEHH of every case fol- lows the normal distribution with the significance level.25. Because F.975 (19,19) =.29,F.25 (19,19) = 3.43, all F values in Table 3 fall in this critical region. Therefore, they accept the assumptions σ 2 1 = σ2 2. Finally, according to Table 3, all the absolute values of t are larger than t.975 (38) = 2.24, and it can be said that the means of the IPEHH are the same at the significance level.5. Therefore, we can conclude that DEVS-FIRE has the same perimeters as those of FARSITE under the same conditions for uniform cases Non-uniform Fuel/Slope/Aspect In this experiment, we define an area with three zones as shown in Figure 8(a). The top zone has fuel model of 4 with slope 15 degrees and aspect 18 degrees; the middle zone has fuel model of 7 with slope degree and aspect degree; the bottom zone has fuel model of 9 with slope 15 degrees and aspect degree. Two simulations were run. The first one has wind speed 5 mph and wind direction degree. The second one has wind speed 5 mph and wind direction 45 degrees. Figure 8(a) and 8(b) show the results of FARSITE and DEVS-FIRE respectively of ten hours s fire spread in the first

6 Table 4. Data of Aspects and Slopes DR F P D F A D F P D F A D (a) FARSITE Table 5. GIS Data with Wind Model Time F P D F A D iment, random wind speeds (around 5 mph) and wind directions are generated every one hour for the first eight hours. For testing purpose, we also manually increase the wind speed to around 16 mph in the last two hours. Figure 9(a) and 9(b) show the simulation results of FARSITE and DEVS-FIRE respectively. Table 5 shows the perimeters and areas of FAR- SITE and DEVS-FIRE respectively. According to the figures, the fire fronts spread from the center of the space to northwest, and DEVS-FIRE and FARSITE have the similar spread patterns. As can be seen from the table, the outputs greatly increase from the ninth hour to the tenth hour because the wind speed changed from 5 to 18 mph. From both the figure and the table, we can draw the conclusion that DEVS-FIRE has the similar simulation results as FARSITE for GIS data. (b) DEVS-FIRE Figure 9. GIS Data with Wind Model simulation. Figure 8(c) and 8(d) show the corresponding results of the second simulation. Table 4 listed the data of fire perimeters and burned areas hourly from 5 to 9 hours. In the table, A, D, F, P, and DR refer to area (ha), DEVS-FIRE, FARSITE, perimeter (km), and wind direction (degrees) respectively. From the figures, we can see that the fire shapes of DEVS-FIRE and FARSITE are very much similar. The data in the table also confirm that the two simulation models give the consistent results GIS Data and Varying Wind Condition This is the case that is close to reality where fuel model, aspect, and slope vary from cell to cell, and wind conditions change in a timely manner. This experiment uses the GIS data from the Ashley project (an example provided by FARSITE 4.), and we run the simulations for ten hours. In the exper- 5. CONCLUSIONS In this paper, we validate DEVS-FIRE, a discrete event cellular space model for wildfire spread simulation, by comparing its results with those of FARSITE under the same input conditions. Both graphical and statistical approaches are used to compare the fire perimeters and burned areas in DEVS- FIRE and FARSITE. The comparisons show that simulation results from DEVS-FIRE are consistent with those of FAR- SITE, including fire spread direction. The work builds a solid ground for validation of DEVS-FIRE using real historical fire data. Through this work, the DEVS-FIRE model will be improved by adjusting the model coefficients, exploring the precise wind adjustment factors for different fuel models, and optimizing the fire spread decomposition schema. REFERENCES [1] USDA Testimony to Congress, 24, accessed from [2] NIFC, 26, Wildland Fire Statistics, National Interagency Fire Center, accessed from [3] L. Natimo, X. Hu, and Y. Sun, DEVS-FIRE: Towards An Integrated Simulation Environment for Surface Wildfire Spread and Containment, SIMULATION: Transactions of The Society for Modeling and Simulation International. [4] Robert G. Sargent, 1998, Verification and Validation of Simulation Models, Proceedings of The 1998 Winter Simulation Conference, pp

7 [5] Andrews, P.L., C.D. Bevins, R.C. Seli, 25, BehavePlus Fire Modeling System, version 3.: User s Guide Gen. Tech. Rep. RMRS-GTR-16WWW Revised, Ogden, UT: Department of Agriculture, Forest Service, Rocky Mountain Research 26 Station, pp [6] Morais, M., 21, Comparing Spatially Explicit Models of Fire Spread through Chaparral Fuels: A New Model Based upon The Rothermel Fire Spread Equation, MA Thesis, University of California, Santa Barbara. [7] Mark A. Finney, 1998, FARSITE: Fire Area Simulator Model Development and Evaluation, United States Department of Agriculture Forest Service Rocky Mountain Research Station Research Paper, RMRS-RP-4 Revised March 1998, revised February 24. [8] Grabner, K.G., J.P. Dwyer, B.E. Cutter, 1997, Validation of BEHAVE Fire Behavior Predictions in Oak Savannas Using Five Fuel Models, Proc. Eleventh Central Hardwood Conf., Univ. of Missouri, Columbia, pp [9] Max Alan Moritz, Department of Physics, UCSB, accessed from complex/max/hfiresamo.html#output. [1] Arca et al., 27, Evaluation of Farsite Simulator in A Mediterranean Area, The 4th International Wildland Fire Conference, Seville, Spain. [11] Ljiljana et al., 25, Fire Modeling in Forest Fire Management, Proc.of Int. Conf. CEEPUS Spring School, Engineering for the Future, Katarzyna Ciosk, Malgorzata Suchanska. [12] Rothermel, R., 1972, A Mathematical Model for Predicting Fire Spread in Wildland Fuels, Research Paper INT-115, U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station, Ogden, UT. [13] Finney, MA. Andrews, PL., 1994, The FARSITE Fire Area Simulator: Fire Management Applications and Lessons of Summer 1994, Proceedings of the 1994 Interior West Fire Council Meeting and Program, pp [14] Missoula Fire Sciences Laboratory, accessed from

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