A Comparison of the Qualitative Analytic Hierarchy Process and the Quantitative Frequency Ratio Techniques in Predicting Forest Fire-Prone Areas in Bhutan Using GIS

Abstract

Forest fire is an environmental disaster that poses immense threat to public safety, infrastructure, and biodiversity. Therefore, it is essential to have a rapid and robust method to produce reliable forest fire maps, especially in a data-poor country or region. In this study, the knowledge-based qualitative Analytic Hierarchy Process (AHP) and the statistical-based quantitative Frequency Ratio (FR) techniques were utilized to model forest fire-prone areas in the Himalayan Kingdom of Bhutan. Seven forest fire conditioning factors were used: land-use land cover, distance from human settlement, distance from road, distance from international border, aspect, elevation, and slope. The fire-prone maps generated by both models were validated using the Area Under Curve assessment method. The FR-based model yielded a fire-prone map with higher accuracy (87% success rate; 82% prediction rate) than the AHP-based model (71% success rate; 63% prediction rate). However, both the models showed almost similar extent of ‘very high’ prone areas in Bhutan, which corresponded to coniferous-dominated areas, lower elevations, steeper slopes, and areas close to human settlements, roads, and the southern international border. Moderate Resolution Imaging Spectroradiometer (MODIS) fire points were overlaid on the model generated maps to assess their reliability in predicting forest fires. They were found to be not reliable in Bhutan, as most of them overlapped with fire-prone classes, such as ‘moderate’, ‘low’, and ‘very low’. The fire-prone map derived from the FR model will assist Bhutan’s Department of Forests and Park Services to update its current National Forest Fire Management Strategy.

1. Introduction

Forest fire is an environmental catastrophe that threatens the safety of humans, infrastructure, and biodiversity [1,2]. Global climate change has led to the considerable decrease in precipitation and increase in the temperature, further influencing the occurrence of forest fires. There are other factors influencing forest fire increase, such as a longer arid season and contributing anthropogenic activities [3]. For example, the evidence for declining forest resilience to wildfires under climate change has been documented by Stevens-Rumann, Kemp [4], Allen, Macalady [5], and Rother and Veblen [6] (also see [7,8,9,10,11,12,13]). Abatzoglou and Williams [14] stated the increased fire activity in the western US and in the US Northern Rockies has been driven by both rising temperatures and widespread drought, particularly since 2000. These factors have altered the trend and frequency of forest fires at an alarming rate in many regions of the world [15,16,17]. It is, therefore, vital to have a reliable and precise approach to predict areas susceptible to forest fire. An accurate forest fire-prone map can assist forest management and planning authorities in allocating relevant resources, emergency responses, and early warning systems [18]. Several methods have been proposed and tested to map forest fire-prone regions. These approaches can be categorized into three major groups of physics-based techniques [19], statistical techniques [20], and machine learning techniques [21].

Many physics-based techniques existed, such as EMBYR [22], FARSITE—Fire Area Simulator [23], FIRETEC [24], FDS [25], and LANDIS-II [26]. Combinations of equations on fluid mechanics, combustion of canopy biomass, and heat transfer mechanisms are required for physics-based methods to recognize fire-prone areas including predicted forest fire periods. The main weak point of these approaches is the difficulty in measuring the amount of inherent errors [27]. Another disadvantage of the physics-based method is the requirement of having detailed data. For instance, data on locations and sizes of trees, fuel mass, soil moisture etc., have to be collected over large areas, making this a difficult task [28]. Therefore, these techniques may not be applicable in data-poor regions. Machine learning methods, such as the Artificial Neural Network [29], Support Vector Machine [30], and Decision Tree [31], are considerably time consuming and software dependent with a high computer capacity [31,32]. As such, these techniques also may not be practicable for regions with limited resources but requiring urgent actions.

However, statistical methods are more appropriate for forest fire susceptibility modeling in the case of large study areas, particularly in combination with Geographic Information System (GIS) technology [33]. GIS and Remote Sensing (RS) techniques make it considerably easy to collect and assess spatial data on large regions with different scales and resolutions [34,35]. Statistical methods are easily comprehensible and implementable, because they do not require specific tailor-made software. Statistical methods, such as Frequency Ratio (FR), quantitatively evaluate the correlation between conditioning factors and forest fire occurrence without involving any expert opinion in the analysis [36]. Conversely, qualitative methods like the Analytical Hierarchical Process (AHP) are based on knowledge of fire experts [37], but are also easily implementable if there is adequate knowledge of previous forest fire occurrences.

In this study, FR and AHP techniques were utilized for the spatial prediction of forest fire-prone areas based on a case study in Bhutan, which represents a data-poor country. Bhutan has more than 72% forest cover [38], which is the highest in the world in terms of proportion of land covered with forest. Every year, several forest fires are reported in various parts of the country. For instance, between 1993 and 2005, a staggering 868 forest fires were reported with 128,368 hectares of forested area reported to be burnt [39]. The country’s highly rugged terrain, which is compounded by a large accumulation of fuel load, poses significant challenges and risks in preventing and containing wildfires. Almost 30% of the country is covered with coniferous forest [40], which is considered as the most flammable forest type because of an accumulation of resin and dried needles [41]. Usually, the dry undercover of pine forests during sustained dry period that lasts for more than six months makes this forest type prone to wildfires. Repeated forest fires can potentially jeopardize sustainable management of Bhutan’s forests. Currently, there are no maps of forest fire-prone areas in Bhutan. This has greatly hindered the government, particularly the Department of Forests and Park Services, in developing an effective forest fire management strategy.

The main objective of this study is to generate forest fire-prone area maps and compare the efficiency of statistical-based and knowledge-based techniques to predict fire-prone areas, using the case of forest fire incidences in Bhutan. In addition, we test if Moderate Resolution Imaging Spectroradiometer (MODIS) fire points were reliable for predicting forest fires in the case of Bhutan. Using the outcome of this study, we intend to assist the Bhutan Government in forest fire prevention and management.

2. Methodology

2.1. Study Area Description

Situated between 27° 30′ N latitude and 90°30′ E longitude and measuring approximately 38,394 km² [NSB] [42], Bhutan is a Himalayan kingdom straddled between India and China, as shown in Figure 1. This tiny nation has 5369 plant species, 129 mammal species, 736 bird species, 125 fishes, 158 amphibian and reptile species, and 3966 invertebrate species (including 3511 insect species) [NBC] [43], all of which signify its importance in global and regional biodiversity conservation.

Geomorphologically, Bhutan is a highly mountainous country with approximately 95% of the total land situated 600 m above sea level (a.s.l), with landforms gradually rising from 97 m a.s.l. in the southern foothills to 7750 m a.s.l. in the northern snow-capped peaks [MoAF] [44]. The vegetation cover changes with elevation, with sub-tropical broadleaved forest occupying elevations below 1200 m a.s.l. and temperate cool broadleaved forests occupying elevations between 1200 and 2000 m a.s.l. Pine forests (with pure stands of blue pine Pinus wallichiana and sometimes mixed with oaks and rhododendron) are found between 1500 and 3200 m a.s.l., while mixed coniferous forests with stands of fir Abies densa, hemlock Tsuga dumosa, spruce Picea spinulosa, larch Larix griffithii, and juniper Juniperus indica occur between 2500 and 3500 m a.s.l. Pure stands of chirpine Pinus roxburghii are found in dry valleys between elevations of 1520 to 1860 m a.s.l. [45]. At higher elevations, sub-alpine forests (3300 to 3800 m a.s.l.) and alpine meadows (3800 to 4800 m a.s.l.) predominate. Areas above 4800 m a.s.l. are featured by alpine rocky outcrops, and those beyond 6000 m a.s.l. are permanently covered in snow [46]. The country has four seasons: spring (February to April), summer (May to July), autumn (August to October), and winter (November to January). Precipitation is mainly attributed to the summer monsoon which lasts from mid-April to mid-September. In terms of demography, Bhutan has a population of 733,003 people [NSB] [42], which is probably the lowest in Asia.

2.2. Forest Fire Modeling Flow Chart

The FR and AHP-based modeling were performed separately using forest fire inventory points recorded from 2013 to 2015 (as shown in Figure 1) maintained at the Forest Fire Management Section of the Department of Forests and Park Services. Two forest fire-prone maps were produced, and each map was assessed using the Area Under Curve (AUC) assessment technique. MODIS fire points were overlaid on the fire-prone maps. The step-by-step modeling flowchart is shown in Figure 2.

2.3. Data Used

2.3.1. Forest Fire Inventory

Forest fire-prone areas were detected by performing a correlation analysis between previous forest fire events and forest fire conditioning factors [47]. The first mandatory stage performed was to prepare a forest fire inventory map for which 177 historical fire locations, as shown in Figure 2, from three years (2013, 2014, and 2015) were gathered. These points were used for the FR technique in performing a correlation between previous forest fire events and their conditioning factors [47]. They were also used for accuracy assessment of fire-prone maps produced by both the techniques for which they were divided into training (n = 124; 70%) and testing (n = 53; 30%) datasets [20,48,49].

2.3.2. Forest Fire Conditioning Factors

A critical influential factor in the quality and precision of the final probability map is the proper selection of forest fire conditioning factors [50]. In this study, seven conditioning factors comprising Land-Use Land Cover (LULC), distance from road, distance from human settlement, elevation, slope, aspect, and distance from the southern international border (with India) were utilized, as shown in Figure 3. The selection of these factors was based on forest fire studies in the region, local knowledge on forest fire, and the availability of spatial layers [9,51,52,53,54,55].

Some spatial layers of these conditioning factors were obtained from offices of the Royal Government of Bhutan: the LULC map of Bhutan 2010 (in vector format) was obtained from the Policy and Planning Division; the road network map of Bhutan 2014 (in vector format) from the Department of Roads; and the human settlement map of Bhutan 2005 (in vector format) from the National Statistical Bureau. Three topographical factors of slope, aspect, and elevation were extracted from a Digital Elevation Model (DEM) for Bhutan created by Jarvis, Reuter [56]. All spatial input layers, including those in vector formats, were converted to a raster format with a standard cell size of 30 m × 30 m following the lowest resolution of the DEM. These input layers were classified prior to the analysis using the popular quantile method [57,58]. This is because FR and AHP evaluate the impact of each class on the forest fire occurrence separately.

Detailed steps in preparation of the input spatial layers for the AHP and their parameterization are described below. Local expert knowledge from field forest fire managers together with published literature were used to assign fire hazard values for the different classes of the spatial layers.

A LULC—The LULC map contained details of major forest types and other land use types found in Bhutan. As reported by Dorji [39], people deliberately set fire in chirpine forests for harvesting lemon grass Cymbopogon flexuosus. Since the frequency of forest fire is the highest in chirpine forests, it was assigned the highest fire hazard value, which was then followed by hazard values of blue pine forest and mixed broadleaved-conifer forest. Other land use types were rated as per their contribution to forest fire incidences, based on expert experience and records from past events, as shown in

Table 1. Land-use and anthropogenic factors that determine an area’s proneness to forest fire in Bhutan. Higher values reflect higher proneness. The values are assigned based on empirical field observations and expert judgments.

Spatial Layers	Classes	Hazard Value
LULC	Glaciers/Snow/Rock outcrops/ Water spreads/landslips/Marshy areas	1
	Meadows	2
	Scrub forest/Settlements/Agriculture/Improved pasture/horticulture	3
	Plantations	4
	Broadleaf	5
	Fir	6
	Broadleaf with conifer	7
	Mixed Conifer	8
	Blue pine	9
	Chirpine	10
Settlement (Distance from human settlement in meters)	0–1927.6	10
	1927.7–3426.9	9
	3427–5140.4	8
	5140.5–6853.9	7
	6854–8781.5	6
	8781.6–11,138	5
	11,139–13,922	4
	13,923–17,991	3
	17,992–24,845	2
	24,846–54,617	1
Road (Distance from road in meters)	0–236.61	10
	236.62–1183.1	9
	1183.2–2602.8	8
	2602.9–4259.1	7
	4259.2–6152	6
	6152.1–8518.1	5
	8518.2–11,357	4
	11,358–16,090	3
	16,091–25,791	2
	25,792–60,337	1
Border (Distance from the southern international border with India in meters)	0–3742.6	10
	3742.7–8349	9
	8349.1–13,243	8
	13,244–18,425	7
	18,426–24,183	6
	24,184–30,229	5
	30,230–36,851	4
	36,852–44,912	3
	44,913–54,412	2
	54,413–73,413	1

. Human land use activities could be ignition sources that induce forest fire susceptibility [59], and hence, agricultural lands were assigned higher hazard values compared to other non-forest land-use types.

B Settlement—Based on historical records of forest fires in Bhutan, most fires originated from agricultural lands and areas near human settlements. Thus far, more forest fires in the country have resulted from accidental escape from burning agricultural fields [DoFPS] [60]. Since forested areas located near settlements were highly vulnerable to fire [61], they were assigned high hazard values than those farther away, similar to the method employed by Opie, March [62] and Sivrikaya, Sağlam [63], as shown in Table 1.

C Roads—Most roads in Bhutan pass through highly forested areas. Roads influence forest fires during black-topping or surfacing by tar, which is conducted for new road construction and maintenance. Forest fires also occur when road travelers, either on foot or in vehicles, throw igniting substances such as un-extinguished cigarette butts [64]. Therefore, the presence of roads was deemed as increasing an area’s vulnerability to forest fire, and thus areas closer to roads were assigned higher hazard values, as shown in Table 1, similar to the approach used by Sowmya and Somashekar [65].

D International border—Frequent forest fires have been observed in areas near the international border with India, particularly in areas adjoining the Indian states of Assam, Arunachal Pradesh, and West Bengal [DoFPS] [60]. Wildlife managers and poachers deliberately light fires in these states to facilitate the growth of grasses for wild herbivores (Pers. Comm., Sonam Wangdi). Due to contiguous forest cover along many sections of the international border, such fires spread into Bhutan’s forests. Therefore, higher values were assigned to areas closer to the southern international border, as shown in Table 1.

E Aspect—Aspect has been widely used for forest fire modeling, because slope direction influences soil moisture and wind speeds that, in turn, affect fire behavior [66]. Moreover, in the northern hemisphere where Bhutan is located, south facing areas receive more sunlight which renders an area dry and prone to forest fire during dry seasons [67]. Hence, the highest hazard value was assigned to areas with a southerly aspect and the lowest to areas with a northerly aspect, as shown in

Table 2. Geophysical factors that determine an area’s proneness to forest fire in Bhutan. Higher values reflect higher proneness.

Spatial Layers	Classes	Hazard Value
Aspect (directions)	Flat	6
	North	1
	Northeast	4
	East	5
	Southeast	7
	South	9
	Southwest	8
	West	3
	Northwest	2
Elevation (meters above sea level)	5–891	1
	891.001–1406	2
	1406.01–1856	3
	1856.01–2295	4
	2295.01–2714	5
	2714.01–3111	6
	3111.01–3556	7
	3556.01–4090	8
	4090.01–4654	9
	4654.01–7519	9
Slope (Degree)	0–11.758	1
	11.759–16.6	2
	16.601–20.404	3
	20.405–23.516	4
	23.517–26.629	5
	26.63–29.741	6
	29.742–32.854	7
	32.855–36.658	8
	36.659–41.845	9
	41.846–87.84	9

.

F Elevation—Elevation is also considered as a factor influencing forest fire, as it indirectly influences evapotranspiration, temperature, humidity, and precipitation [50]. These conditions, in turn, determine an area’s susceptibility to forest fire. In Bhutan, most forest fires are known to occur frequently at lower elevations compared to higher elevations, and hence, higher hazard values were assigned to lower elevated areas, as shown in Table 2.

H Slope—Slope is a well-known contributing factor in forest fire susceptibility mapping. According to [61], fire travels faster up slope and slowly down slope, meaning the steeper the slopes, the faster the fire travels [68]. Therefore, steeper slopes were accorded higher hazard values, as shown in Table 2, similar to the methods applied by [67].

2.4. Modeling Forest Fire-Prone Areas

2.4.1. Analytic Hierarchy Process (AHP) Modeling

The AHP is a weight estimation technique that generates weights or ratio scales from paired comparisons [69]. It is widely used in Multi-Criteria Decision Analysis (MCDA), resource planning, and conflict resolution. AHP-based modeling has been used for forest fire hazard mapping in the south Asian region [37,70,71,72]. The AHP method basically employs a square matrix with ones on the (main) diagonal, weights on one side of the diagonal and reciprocal weights on the reverse side. In such a pair-wise comparison matrix, weightage of one factor over the other is assigned using a fundamental scale with numerical values ranging from 1/9 to 9 in the order of least comparative importance to highest comparative importance. It is during this step that expert knowledge on the subject matter becomes extremely useful. Expert knowledge was gathered from published literature, forest fire managers, field personnel, and field reports of forest fire incidences. Several rounds of consultations were held with forest fire managers to assign weights for an AHP matrix. Consistency of the weight matrix was measured by a Consistency Ratio (CR), which measures divergence of the weights from a principal eigenvalue. Recalibration of the weights was needed whenever the CR was greater than 0.10 (or 10%). Once a consistent matrix was obtained, a vector of relative weights for each factor was produced. In this study, a 7 × 7 AHP matrix was used, as shown in

Table 3. A 7 × 7 Analytic Hierarchy Process (AHP) matrix showing pairwise comparison of forest fire conditioning factors with respect to perceived influence on forest fire susceptibility using expert knowledge in Bhutan. Unity of diagonal represents equality of weights, which range from 1/9 (extremely low importance) to 9 (extremely high importance).

Factors	LULC	Settlement	Road	Boundary	Elevation	Aspect	Slope
LULC	1	3	4	5	6	7	8
Settlement	1/3	1	2	3	4	5	6
Road	1/4	1/2	1	2	3	4	5
Boundary	1/5	1/3	1/2	1	2	3	4
Elevation	1/6	1/4	1/3	1/2	1	2	3
Aspect	1/7	1/5	1/4	1/3	1/2	1	2
Slope	1/8	1/6	1/5	1/4	1/3	1/2	1

. A highly consistent CR value of 0.05 was obtained, and the relative weights were subsequently produced, as shown in

Table 4. The weights for the seven conditioning factors in Bhutan with respect to influence on forest fire susceptibility derived from an Analytical Hierarchy Process with a consistency ratio of 0.05.

Factors	Derived Ratio Scale	Percentage of Influence
LULC	0.451	45
Settlement	0.188	19
Road	0.124	12
Boundary	0.086	9
Elevation	0.063	6
Aspect	0.049	5
Slope	0.04	4

. The highest weightage (45%) was assigned to the LULC layer, followed by the settlement layer (19%) and road layer (12%). The lowest weightage (4%) was assigned to the slope layer. These weights were used as the percentages of influence of each layer in the ‘weighted overlay’ process in ArcGIS to produce a map of forest fire-prone areas.

2.4.2. Frequency Ratio (FR) Modeling

The FR can be defined as the probability of occurrence of a specific attribute [73]. Higher FR weights illustrate a high relationship among that class and forest fire occurrence [74]. For modeling of forest fire-prone areas, an FR was used to extract the quantitative relationship between forest fire occurrence points and the seven forest fire conditioning factors. The FR-based modeling is a popular approach for computing the probabilistic relationship between a specific phenomenon and a set of contributing factors involved in the creation of a spatial layer of that phenomenon [75].

The following equation for the FR was used:

$$F{R}_i=\left(A_i/B_i\right)/\left(H_i/L\right)=P_i/K$$

(1)

where:

• $F{R}_i$ = frequency ratio of a class for the $i^{th}$ conditioning factor;
• $A_i$ = area of a class for the $i^{th}$ conditioning factor;
• $B_i$ = total area of the $i^{th}$ conditioning factor;
• $H_i$ = number of pixels in each class of the $i^{th}$ factor;
• $L$ = number of total pixels in the study area;
• $P_i$ = the percentage for area with respect to a class for the $i^{th}$ factor; and
• $K$ = is the percentage for the entire domain.

2.5. Accuracy Assessment of Model Outputs

The Area Under Curve (AUC) is an intuitive and comprehensive tool to evaluate the reliability and precision of the model outcomes [76]. The AUC method has been broadly applied in several studies to evaluate the efficiency of susceptibility mapping. It starts with dividing the forest fire probability map into equal area categories and then ranking them from a minimum to a maximum value. Curve creation is implemented by plotting the cumulative percentage of forest fire susceptible areas on the ‘x’ axis and the cumulative percentage of forest fire events on the ‘y’ axis. Prediction and success rate are two outputs of the AUC method [77]. The success and prediction curves determine the percentage of fire occurrence points in each probability category. The validation process was undertaken by comparing the existing forest fire inventory data with the model derived forest fire-prone areas maps. The AUC values range from 0.5 to 1.0 such that values closer to or equal to 0.5 indicate very poor fit or classification by chance, whereas those closer to or equal to 1 indicate perfect fit or perfect classification [78]. The success rate outcome was attained using the forest fire training dataset (70% of the inventory forest fire points). The real proficiency of the model output can be tested using the prediction rate, which was implemented using the test dataset (30% of the inventory forest fire points). This is because the prediction capability of the model cannot be achieved using the training data. The prediction rate shows how well the model can predict the forest fire proneness or susceptibility of an area.

2.6. Validation of MODIS Fire Points with Model Outputs

MODIS is a remote sensing sensor with fire detection capability mounted on two satellites that were launched in December 1999 and May 2002 by the National Aeronautics and Space Administration (NASA), USA. Each of these satellites records two fire observations daily, resulting in four daily observations [79]. The MODIS system carries out automated data acquisition, processing, reporting, and feedback on fire locations. It provides location information at 1 km × 1 km resolution on active fires present during the satellite’s hover across an area, twice in a day. The International Center for Mountain Development (ICIMOD), based in Nepal, has the ground receiving station, launched in January 2011, which is convenient for the south Asian countries to acquire data when required. The MODIS fire points from 2000 to 2013 for Bhutan were obtained from the ICIMOD. The detection algorithm identifies pixels with one or more actively burning fires that are commonly referred to as “fire pixels”. Each detected fire represents the center of a 1 km pixel that contains one or more fire hotspots. The actual pixel size varies depending on the location of an observation in the swath [80]. In this study, the MODIS points were overlaid on each of the forest fire-prone maps produced by the FR and AHP-based models. The number of points overlapped with each of the fire-prone categories were measured to determine the reliability of MODIS satellites and fire points in predicting forest fire-prone areas.

3. Results

3.1. Model Outputs: Forest Fire-Prone Area Maps

Both AHP and FR models were performed, and two forest fire probability maps were initially produced. For a proper one-to-one comparison, both probability maps were normalized with probability values ranging from 0 to 1, as shown in Figure 4a,c. These probability maps were then classified into five different forest fire-prone classes: ‘very low’, ‘low’, ‘moderate’, ‘high’, and ‘very high’, using the quantile method of classification to produce the final forest fire-prone areas maps, as shown in Figure 4b,d.

The percentage of total land area encompassed by each fire-prone category generated by AHP and FR-based models can be seen in Figure 5. The AHP model depicted large areas for ‘moderate’ and ‘high’ prone classes, and together they covered 16,893 km² (44%) of Bhutan’s total land area. The FR model showed the areas of each fire-prone class in a decreasing trend from ‘very low’ (22,268 km²; 58%) to ‘very high’ (1535 km²; 4%).

Most of the very high fire-prone areas detected by both the models were situated along the middle belt of the country, corresponding to areas dominated by pure stands of chirpine and blue pine forests, ranging between the 100 to 4962 m a.s.l. and between 0° to 75° slope, and areas close to the southern international border with India.

Figure 3. Spatial layers representing the seven conditioning factors: (a) Land-Use Land Cover (LULC), (b) distance from settlement, (c) distance from road, (d) distance from the southern international border, (e) aspect, (f) elevation, and (g) slope, for modeling forest fire-prone areas in Bhutan. All spatial input layers were classified prior to the analysis using the popular quantile method [57,58].

Figure 3. Spatial layers representing the seven conditioning factors: (a) Land-Use Land Cover (LULC), (b) distance from settlement, (c) distance from road, (d) distance from the southern international border, (e) aspect, (f) elevation, and (g) slope, for modeling forest fire-prone areas in Bhutan. All spatial input layers were classified prior to the analysis using the popular quantile method [57,58].

Figure 4. Forest fire probability maps for Bhutan derived from (a) AHP and (c) FR; forest fire-prone area maps for Bhutan derived from (b) AHP and (d) FR.

Figure 4. Forest fire probability maps for Bhutan derived from (a) AHP and (c) FR; forest fire-prone area maps for Bhutan derived from (b) AHP and (d) FR.

Figure 5. Graphical comparison of relative difference in percentage of total land area in Bhutan encompassed by each fire-prone category yielded by AHP and FR-based models.

Figure 5. Graphical comparison of relative difference in percentage of total land area in Bhutan encompassed by each fire-prone category yielded by AHP and FR-based models.

3.2. Accuracies of Model Outputs

While assessing the efficiency of each method using AUC, the AHP model produced a 70.61% success rate and a 62.46% prediction rate, whereas the FR model produced 87% success rate and 82% prediction rateas shown in Figure 6.

3.3. Validation of MODIS Fire Points

Upon overlay of 2769 MODIS fire points on the forest fire-prone maps, only 353 points (13%) overlapped with ‘very high’ and 340 points (12%) with ‘high’ classes on the fire-prone map yielded by the AHP model, as shown in Figure 7 and Figure 8. Similarly, only 260 points (9%) occurred on ‘very high’ and 346 points (13%) on ‘high’ classes of the FR-based fire-prone map. On the contrary, the highest number of MODIS points overlapped with ‘moderate’ class (n = 981; 35%) on the AHP-based map and ‘low’ class (n = 861; 31%) on the FR-based map.

4. Discussion

Due to the non-linear and complex nature of a forest fire, rapidly modeling this catastrophe at the regional scale is a challenge. In this study, two simple yet robust models for predicting forest fire-prone areas in Bhutan were presented and compared. The FR model was shown to produce a more accurate fire-prone map than the AHP model, based on the higher AUC values. Therefore, the use of the FR model is recommended. The weakness of the AHP model is due to potential errors in pair-wise comparisons of the conditioning factors. The AHP model is highly reliant on expert judgment that is prone to error in the sense that its accuracy can be greatly altered by divergent views from the fire experts. Such a possibility was also acknowledged by Rathore, Dubey [81] while creating an expert-based least-cost corridor for tigers Panthera tigris in Madhya Pradesh, India. Therefore, considerable attention is required in assigning values in an AHP matrix with repeated iterations, until a desired CR is attained. The FR modeling, on the other hand, produces outcomes based on mathematical analysis; hence, it does not require any expert judgments and is, therefore, less prone to errors emanating from expert opinion. In recent times in Bhutan, forest fires have been caused by electrical short circuits along the power transmission lines traversing coniferous forests. Due to the non-availability of a spatial layer on distance from power lines, it was not used as a conditioning factor in the modeling. However, it should be used in future studies if the spatial layer becomes available. One of the advantages of GIS-based modeling is that new spatial layers can be added, and the model repeatedly generated.

We have found that the MODIS fire points are not reliable in predicting forest fires, as most of the points overlapped with ‘moderate’ and ‘low’ prone classes on the AHP and FR model outputs, respectively. The low predictability of MODIS fire points in predicting forest fire-prone areas in Bhutan could be due to cloudy weather conditions in the Himalayan ranges that could shield forest fires from the satellites. It could also be possible that the timing of forest fires may not have coincided with the timing of satellite passes. Similar explanations are reported by Müller, Suess [82] in Lao People’s Democratic Republic. Additionally, in Thailand, there were false alarms observed during ground validation of fires in the hilly areas, although MODIS detection accuracy was 97% [83]. In the case of Bhutan, Pemagatshel Dzongkhag (‘district’ in Bhutanese national language) in the southeast was classified as a ‘moderate’ or ‘low’ fire-prone area by our models despite the large concentration of MODIS fire points (n = 327). In fact, most of these fire points represented fires from the burning of agricultural debris and from shifting cultivation, which is still being practiced at a small scale despite officially being banned. One should, therefore, exercise caution while developing any forest fire-prone maps using MODIS fire points.

This study has created the first ever forest fire-prone map for Bhutan (based on the FR model), which will be forwarded to the Department of Forests and Park Services for adoption. Such forest fire-prone area maps will be highly valuable to Bhutanese area managers and also to policy makers at regional and national levels for effective planning of resources to prevent and manage forest fires. This map is highly relevant and timely for the current situation in Bhutan, which still does not have an officially recognized forest fire-prone area map. Fire-prone classes, such as ‘very high’ and ‘high’, are predicted in the central districts of Bhutan. Mongar Dzongkhag has the highest percentage of fire-prone areas (combination of ‘very high’ and ‘high’ classes), followed by Wangduephodrang, Trashigang, Bumthang, Thimpu, and Paro Dzongkhags. These are areas with a corresponding high percentage of blue pine and chirpine forests along with high human populations and a comprehensive road network. Therefore, these areas need to be prioritized for any future fire prevention and management programs in Bhutan.

5. Conclusions

In this study, quantitative FR and qualitative AHP techniques were applied to map forest fire-prone areas in Bhutan and were compared in terms of accuracy of mapping. Seven forest fire conditioning factors, comprising LULC, distance from human settlement, distance from road, distance from the southern international border, aspect, elevation, and slope, were utilized for predicting fire-prone areas in Bhutan. The map produced by the FR model was found to be more accurate (with an 82% prediction rate). Therefore, we suggest using this to reliably predict forest fires and allocate resources to fire-prone areas for any prevention and suppression activities. MODIS forest fire points were found to be not reliable in predicting forest fires in Bhutan due to a high percentage of overlap with ‘low’ fire-prone areas. Hence, we caution their use for predicting forest fires. The forest fire-prone area maps generated in this research will be useful for the Bhutan Government to improve its current National Forest Fire Management Strategy.