Next Article in Journal
Predictive Analysis of Hydrological Variables in the Cahaba Watershed: Enhancing Forecasting Accuracy for Water Resource Management Using Time-Series and Machine Learning Models
Previous Article in Journal
Application of an Orbital Remote Sensing Vegetation Index for Urban Tree Cover Mapping to Support the Tree Census
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Commentary

A Lens on Fire Risk Drivers: The Role of Climate and Vegetation Index Anomalies in the May 2025 Manitoba Wildfires

1
Department of Soils and Agri-Food Engineering, Université Laval, Quebec, QC G1V 0A6, Canada
2
Department of Civil Engineering, University of Ottawa, 161 Louis Pasteur Private, Ottawa, ON K1N 6N5, Canada
*
Author to whom correspondence should be addressed.
Earth 2025, 6(3), 88; https://doi.org/10.3390/earth6030088
Submission received: 23 May 2025 / Revised: 17 July 2025 / Accepted: 28 July 2025 / Published: 1 August 2025

Abstract

In early May 2025, extreme wildfires swept across Manitoba, Canada, fueled by unseasonably warm temperatures, prolonged drought, and stressed vegetation. We explore how multi-source satellite indicators—such as anomalies in snow cover, precipitation, temperature, vegetation indices, and soil moisture in April–May—jointly signal landscape preconditioning for fire, highlighting the potential of these compound anomalies to inform fire risk awareness in boreal regions. Results indicate that rainfall deficits and diminished snowpack significantly reduced soil moisture, which subsequently decreased vegetative greenness and created a flammable environment prior to ignition. This concept captures how multiple moderate anomalies, when occurring simultaneously, can converge to create high-impact fire conditions that would not be flagged by individual thresholds alone. These findings underscore the importance of integrating climate and biosphere anomalies into wildfire risk monitoring to enhance preparedness in boreal regions under accelerating climate change.

1. Introduction

In early May 2025, severe wildfires broke out in various parts of Manitoba, Canada, and spread rapidly. By the end of May 2025, three of the most intense fires had collectively burned approximately 8667 square kilometers of land and forest (Figure 1). This wildfire caused the deaths of two people and led to the evacuation of approximately 1000 residents from Lac du Bonnet and surrounding areas [1]. These fires emerged under conditions of ongoing drought and unseasonably warm weather, contributing to the rapid spread of fires and extensive damage to the landscape. The disaster occurred amid an exceptional heat wave in Manitoba, with temperatures in Winnipeg reaching 37 °C (99 °F) — the highest recorded in 125 years [2]. A national map, based on data from the Canadian Drought Monitor, illustrates drought intensity across Canada at the end of April 2025, with parts of Manitoba marked as abnormally dry (D0) and under moderate drought (D1) conditions (Figure 1a). This event highlights the importance of enhanced wildfire preparedness and more comprehensive monitoring of drought trends across Canada, particularly in provinces such as Manitoba, where the combination of extensive boreal forests, increasing fire weather, and remote communities increases wildfire vulnerability.
Severe wildfires erupted in various locations across Manitoba in May 2025, showing rapid progression over a short period (Figure 1b). A Landsat 8 image acquired on 4 May 2025 shows the burned area one day after ignition, with initial fire scars and smoke clearly visible (Figure 1c, left). By 10 May, Sentinel-2 imagery reveals that the fire had expanded dramatically to cover 381.5 km2, indicating rapid spread over less than a week (Figure 1c, right). Further east, a fire that started on 12 May had already grown to 952.7 km2 by 14 May, with a clear smoke plume along its southern boundary indicating ongoing fire activity and wind-driven transport (Figure 1d). Another fire that began on 10 May in southeastern Manitoba reached 64.8 km2 by 14 May, exhibiting a compact burn pattern within a forest–agriculture interface (Figure 1e). The rate of fire spread during these events was notably rapid compared to typical recent fire seasons in Manitoba. For instance, wildfires in Manitoba burned approximately 7898 km2 in 2013 and 9525 km2 in 2021. However, it took several weeks for the fires to reach such extents. In contrast, the 2025 fires expanded rapidly within the first weeks of May, highlighting an unusual early-season behavior that may reflect changing fire dynamics under compound climate stressors.
Advancements in remote sensing technologies have greatly enhanced our ability to monitor and detect wildfires [3]. Optical satellite imageries, such as Landsat and Sentinel-2, allow for precise delineation of wildfire boundaries and the extent of their spread [4]. For instance, by applying the Needleleaf Index [5] to satellite imagery, we estimate that approximately 3206 km2 of needleleaf forest burned in Manitoba by the end of May 2025, demonstrating how such vegetation metrics can support post-fire impact assessment. Analysis of the Moderate Resolution Imaging Spectroradiometer (MODIS) land cover product (MCD12Q1) indicates that approximately 7033 km2 burned within sparsely to moderately forested regions (10–60% canopy cover), with an additional 287.9 km2 affecting agricultural lands. These distributions suggest that many fires were concentrated in forest–agriculture transition zones, where fire susceptibility is often underestimated in early spring. Furthermore, remote sensing provides valuable insights into the underlying causes, dynamics, and characteristics that drive wildfire intensification, enabling more effective fire management and mitigation strategies. Understanding how these environmental factors interact with wildfire dynamics is crucial, particularly in the context of a changing climate and altered land surface conditions that are reshaping fire regimes in boreal ecosystems [6,7]. Recent shifts in climatic parameters and land surface conditions have significantly altered fire regimes in boreal ecosystems [8]. This study aims to provide a focused analysis of the early-spring 2025 wildfire outbreak in Manitoba by examining the combined influence of multiple environmental anomalies that occurred in April, including snow cover depletion, precipitation deficits, soil moisture reduction, temperature shifts, and vegetation stress. We analyzed anomalies in six environmental variables: January–May 2025 soil moisture anomaly (ERA5-Land), April values of air temperature and precipitation (ERA5-Land), snow cover extent (MODIS), leaf area index (MODIS LAI), and vegetation greenness (MODIS NDVI), covering the period of 2003–2025. All variables were standardized using Z-scores to allow for intercomparison. We used linear regression to identify trends, Pearson correlation to examine inter-variable relationships, and multiple linear regression to assess the combined effects of anomalies on burned area. Spatial overlap between environmental stress patterns and fire activity was also evaluated. Unlike many prior studies that focus on peak summer fire seasons, our work highlights how moderate but temporally coincident anomalies outside the traditional fire window can precondition landscapes for severe wildfire outbreaks. By integrating satellite-derived datasets, we seek to improve understanding of early-season fire risk dynamics in boreal ecosystems.

2. Results and Discussion

The spatial anomalies in April 2025 across Manitoba indicate a combination of environmental stressors that are conducive to wildfire ignition and spread (Figure 2). Negative anomalies in leaf area index (LAI) (−0.0241) and precipitation (−7.6 mm) reflect suppressed vegetation activity and dry atmospheric conditions, respectively. Notably, the soil moisture anomaly for early 2025 was among the most negative in the historical record (–0.013), indicating significant subsurface dryness. This pronounced deficit likely contributed to cumulative vegetation stress and reduced moisture availability in the root zone. When combined with concurrent negative anomalies in precipitation, normalized difference vegetation index (NDVI), and LAI, these conditions created a landscape highly susceptible to ignition and fire propagation.
The province exhibited a mean LAI anomaly of −0.024, indicating a general reduction in vegetative greenness and canopy density (Figure 2a). This decline in LAI reflects early signs of vegetation stress or dieback, potentially driven by water scarcity and temperature conditions during the pre-fire season. The precipitation anomaly averaged −7.6 mm, suggesting a province-wide deficit in rainfall relative to the climatological norm. The central and southern regions were particularly affected, as evident in the anomaly map, which shows extensive zones in brown and yellow, signaling significantly drier-than-normal conditions (Figure 2b). Such early-season dryness leads to rapid fuel desiccation, particularly in fine fuels like grasses and small shrubs, which are critical to initial fire ignition and spread. Although not extreme across the province, air temperature anomalies display positive deviations, particularly in southern Manitoba (Figure 2c). These warmer-than-average patches are crucial, as they likely accelerated snowmelt and evaporative losses in April, reducing residual soil moisture ahead of the critical fire-prone period in May. In contrast, the soil moisture anomaly was among the most negative in the historical record for early 2025 (–0.013), indicating subsurface moisture levels were considerably below the long-term average. A negative anomaly in this context reflects a relative deficit in soil water content compared to the 2003–2025 climatology. The spatial distribution reinforces the fact that vast areas of southern and central Manitoba—where most of the fires occurred—exhibited strongly negative anomalies (Figure 2d). This suggests that cumulative soil moisture deficit played a major role in preconditioning the landscape for ignition and fire spread. Despite localized patches of neutral or slightly positive values in the far north and east, the overall spatial pattern clearly reflects widespread dry conditions in fire-prone zones.

Analysis of April Anomalies Related to Fire Conditions in Manitoba

The LAI anomaly data (2003–2025) exhibit stronger interannual deviations compared to NDVI, with a notably negative anomaly in 2025 (−0.0241), consistent with limited leaf development during April (Figure 3a). Peaks in LAI (e.g., 2006, 2010, and 2015) correspond to years with higher spring greenness, while significant troughs (2013, 2014, and 2022) are associated with dry Aprils, reinforcing the sensitivity of LAI to spring precipitation and temperature regimes. The NDVI anomaly time series (2003–2025) reveals moderate interannual variability, with pronounced vegetation stress events notably in 2013, 2014, and 2022 (Figure 3b). The 2025 anomaly (−0.0032) is close to neutral but follows several years of fluctuating productivity, suggesting possible cumulative vegetation stress or delayed recovery from previous droughts. The precipitation anomaly series (2003–2025) highlights frequent negative anomalies in recent decades, with particularly dry Aprils in 2008, 2018, and 2023 (Figure 3c). The 2025 anomaly (−7.67 mm) aligns with these dry episodes, indicating a persistent trend of April dryness that may have long-term implications for vegetation regeneration and fire susceptibility in spring. Furthermore, snow cover anomalies (2003–2025) demonstrate significant variability, with large deficits in 2005, 2009, and 2020, and surpluses in 2007, 2016, and 2018 (Figure 3d). In 2025, a snow cover anomaly of approximately −39,939 km2 points to limited snow retention into April, likely accelerating ground exposure and preheating of fuels before the fire season. This reduced snow insulation, combined with dry and stressed vegetation, likely amplified the vulnerability of Manitoba’s landscape to ignition. Fluctuations in the El Niño–Southern Oscillation (ENSO) may be one of the factors contributing to the recent decline in snow cover extent [9]. Soil moisture anomalies exhibit high interannual variability with several negative outliers (e.g., 2013, 2018, and 2025). Notably, the anomaly for 2025 (−0.0127) is among the most negative in the entire record. This suggests that soil conditions in early 2025 were unusually dry, likely contributing to increased fire susceptibility. This pronounced soil moisture deficit appears to be primarily driven by two key factors: an exceptional precipitation shortfall and unusually low snow cover or early snowmelt during April 2025, both of which limited soil water recharge at the start of the fire season. Although the regression line has a low coefficient of determination (R2 = 0.002) and is not statistically significant (p > 0.1), the presence of repeated negative anomalies in recent years may indicate more frequent dry springs. These dry soil conditions could play an important role as cumulative predisposing factors for early-season wildfire activity in boreal landscapes [10]. Although individual vegetation indicators such as NDVI do not show significant long-term declining trends, the convergence of moderate negative anomalies in NDVI, LAI, precipitation, and soil moisture during early 2025 suggests a form of cumulative environmental stress. This form of stress arises not from a persistent trend in one variable but rather from the simultaneous occurrence of multiple below-average conditions during a critical pre-fire window. Such compounding effects may not be evident in single-variable time series but can still elevate fire susceptibility [11,12,13], particularly in boreal ecosystems during early spring. Taken together, these indicators suggest that the fire outbreak in May 2025 occurred within a broader climatic context marked by recurring spring drought, declining snow cover, and vegetation stress—factors that collectively predispose the region to increasingly severe and earlier fire seasons.
To investigate whether long-term anomalies in environmental variables are linked to increased fire activity, we conducted a multiple linear regression analysis using precipitation, soil moisture, snow cover, NDVI, and LAI anomalies as predictors of burned area for the period 2003–2025. The model demonstrated limited explanatory power (R2 = 0.271; Adjusted R2 = 0.056) and was not statistically significant (F (5, 17) = 1.26, p = 0.325). None of the individual variables were significant predictors (all p > 0.1). Residual diagnostics showed no major violations of assumptions: residuals were approximately normally distributed (Omnibus p = 0.164), independent (Durbin–Watson = 2.02), and visually homoscedastic. However, the high condition number (13,700,000) indicated potential multicollinearity among predictors.
These results suggest that variations in annual burned area are influenced more by short-term interannual variability than by persistent trends in individual environmental variables. While the regression results do not support a strong linear relationship, they highlight the challenges in detecting gradual or compound effects through single-variable models.
Nevertheless, the convergence of moderate negative anomalies across NDVI, LAI, precipitation, and soil moisture during early 2025 suggests a form of compound environmental stress. This stress does not arise from persistent trends in individual indicators but from the simultaneous occurrence of multiple below-average conditions during a critical pre-fire period. Although not statistically significant in isolation, such compounding anomalies may still increase fire susceptibility in boreal ecosystems, particularly during the early spring. To better understand the relationships between the observed anomalies and the fire activity in April 2025, a Pearson correlation analysis was performed using environmental variables and fire occurrence. For this analysis, anomalies in precipitation, snow cover, NDVI, and LAI were calculated for April 2025, while the soil moisture anomaly represents the average anomaly over the first five months of 2025 (January–May) to better capture cumulative moisture deficits leading up to the fire event. The results indicate that soil moisture anomaly exhibits the strongest negative correlation with burned area (r = −0.33, p = 0.11), suggesting that prolonged soil dryness played a particularly important role in increasing fire susceptibility. Other variables, such as precipitation (r = −0.21, p = 0.30), NDVI (r = −0.14, p = 0.51), and LAI (r = −0.13, p = 0.54), also showed weak negative correlations, although not statistically significant, indicating potential additive effects. The snow cover anomaly showed only a minimal correlation (r = −0.08, p = 0.72), which may reflect spatial variability or a delayed influence. These results highlight the role of cumulative moisture deficit as a key factor preconditioning the landscape for wildfire ignition and spread.
In addition to descriptive anomaly analysis, we performed a multiple linear regression to evaluate the combined effect of precipitation, soil moisture (averaged over January–May), snow cover, NDVI, and LAI anomalies on the observed burned area. The model showed a moderate level of correlation (R = 0.52), although the overall R2 value was 0.27 and not statistically significant (F (5, 17) = 1.26, p = 0.325). None of the predictors reached statistical significance individually (all p > 0.1). Diagnostic tests indicated no major violations of normality (Omnibus p = 0.164) or independence (Durbin–Watson = 2.02); the condition number (1.37 × 107) suggested potential multicollinearity among predictors. These findings suggest that while no single variable offers a strong predictive signal, the co-occurrence of moderate anomalies across multiple variables in 2025 may have contributed to increased fire risk. This model is exploratory in nature and highlights the need for larger datasets and more sophisticated approaches to better understand compound environmental influences on wildfire activity. The limited sample size (n = 25) and natural variability in wildfire drivers likely constrained statistical power. Nonetheless, this analysis supports our qualitative findings and highlights the need for longer-term datasets and higher-resolution modeling to capture early-season fire risk.
Although the 2025 environmental anomalies appeared impactful in relation to fire activity, standardized Z-score analysis shows that these values were within expected interannual variability. Calculated Z-scores for LAI (−0.243), NDVI (−0.285), precipitation (−0.717), and snow cover (−0.994) all fall within ±1 standard deviation from the long-term mean, indicating that none of the variables represent statistical outliers. This suggests that even moderate anomalies, when occurring simultaneously, can significantly elevate fire risk in boreal regions during spring [14]. Among all variables assessed, soil moisture in 2025 exhibited the most extreme standardized deviation (Z = −1.729), suggesting unusually dry subsurface conditions despite only moderate anomalies in vegetation and precipitation indices. Although not a formal statistical outlier, this level of soil dryness likely contributed significantly to early-season fire susceptibility, reinforcing the importance of cumulative moisture conditions in fire risk assessments.
To evaluate the spatial correspondence between environmental stress and wildfire occurrence, we extracted the mean anomaly values for the 27 burned area polygons using zonal statistics. The results indicate that fire-affected areas exhibited consistently negative anomalies in key variables, including precipitation (−8.25 mm), LAI (−1.61), and soil moisture (−0.014). The negative soil moisture anomaly suggests pre-fire dryness. These values confirm that the wildfires occurred within areas experiencing below-average environmental conditions, supporting the hypothesis that moderate, spatially coincident stressors can collectively increase fire susceptibility, even when individual anomalies are not extreme [15,16]. Our findings align with prior work emphasizing the role of spring snowmelt timing and vegetation recovery in modulating fire season onset [17,18]. However, the 2025 case demonstrates that compound moderate anomalies across multiple domains can also produce highly flammable conditions [19]. Future research should explore how other relevant meteorological and biological factors interact with moderate anomalies to influence fire ignition and spread. Incorporating these variables into compound stress frameworks could improve our understanding of early-season wildfire risk.

3. Conclusions

The May 2025 wildfires in Manitoba resulted from multiple interacting environmental stressors, including reduced April precipitation, early snowmelt, soil moisture deficits, vegetation stress, and declining greenness, all of which contributed to a highly flammable landscape. While each anomaly alone appeared moderate, the observed spatial and temporal overlap of moderate anomalies suggests a potential synergistic effect that significantly preconditioned the environment for ignition. This effect was particularly pronounced in forest–agriculture transition zones, where fire susceptibility is often underestimated in early spring. By quantifying these relationships using multi-source satellite and reanalysis datasets, this study provides new empirical support for the role of compound biosphere–climate anomalies as early warning signals. These findings underscore the crucial need to incorporate satellite-derived environmental indicators into operational fire risk assessments, enabling better anticipation and management of spring wildfire outbreaks in boreal ecosystems. This is particularly important in a changing climate, where such compound conditions are expected to become more frequent, subtle, and hazardous.

Author Contributions

Conceptualization, A.A. and H.B.; methodology, A.A. and H.B.; software, A.A.; validation, A.A.; formal analysis, A.A.; investigation, A.A. and H.B.; resources, A.A.; data curation, A.A.; writing—original draft preparation, A.A. and H.B.; writing—review and editing, A.A., H.B. and S.G.; visualization, A.A.; supervision, H.B. and S.G.; project administration, H.B. and S.G.; funding acquisition, H.B. and S.G. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

The datasets used and/or analyzed during the current study are available from the corresponding author upon reasonable request.

Acknowledgments

We gratefully acknowledge NASA for providing MODIS and Landsat satellite data, and the European Space Agency (ESA) for access to Sentinel-2 imagery, which were essential for wildfire monitoring and vegetation assessment. Drought data used in this study were obtained from the Canadian Drought Monitor, made available by Agriculture and Agri-Food Canada. We also acknowledge the Copernicus Climate Change Service (C3S) and the European Centre for Medium-Range Weather Forecasts (ECMWF) for providing ERA5-Land climate reanalysis data.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Isai, V. Canada’s Wildfire Season Is Off to a Deadly Start. The New York Times. 2025. Available online: https://www.nytimes.com/2025/05/15/world/canada/canada-wildfires-manitoba-deaths.html?smid=url-share (accessed on 22 May 2025).
  2. WeatherStats.ca. Daily Weather Records for Winnipeg, Manitoba—Maximum Temperature. Available online: https://winnipeg.weatherstats.ca/records_daily.html (accessed on 13 July 2025).
  3. Barmpoutis, P.; Papaioannou, P.; Dimitropoulos, K.; Grammalidis, N. A review on early forest fire detection systems using optical remote sensing. Sensors 2020, 20, 6442. [Google Scholar] [CrossRef] [PubMed]
  4. Quintano, C.; Fernández-Manso, A.; Fernández-Manso, O. Combination of Landsat and Sentinel-2 MSI data for initial assessing of burn severity. Int. J. Appl. Earth Obs. Geoinf. 2018, 64, 221–225. [Google Scholar] [CrossRef]
  5. Amiri, A.; Soltani, K.; Gumiere, S.J.; Bonakdari, H. Forest fires under the lens: Needleleaf index—A novel tool for satellite image analysis. npj Nat. Hazards 2025, 2, 9. [Google Scholar] [CrossRef]
  6. Scholten, R.C.; Veraverbeke, S.; Chen, Y.; Randerson, J.T. Spatial variability in Arctic–boreal fire regimes influenced by environmental and human factors. Nat. Geosci. 2024, 17, 866–873. [Google Scholar] [CrossRef] [PubMed]
  7. Zhao, J.; Yue, C.; Wang, J.; Hantson, S.; Wang, X.; He, B.; Li, G.; Wang, L.; Zhao, H.; Luyssaert, S. Forest fire size amplifies postfire land surface warming. Nature 2024, 633, 828–834. [Google Scholar] [CrossRef] [PubMed]
  8. Sayedi, S.S.; Abbott, B.W.; Vannière, B.; Leys, B.; Colombaroli, D.; Romera, G.G.; Słowiński, M.; Aleman, J.C.; Blarquez, O.; Feurdean, A.; et al. Assessing changes in global fire regimes. Fire Ecol. 2024, 20, 18. [Google Scholar] [CrossRef]
  9. Amiri, A.; Gumiere, S.; Bonakdari, H. White blanket, blue waters: Tracing El Niño footprints in Canada. Int. J. Appl. Earth Obs. Geoinf. 2024, 135, 104267. [Google Scholar] [CrossRef]
  10. Jain, P.; Barber, Q.E.; Taylor, S.W.; Whitman, E.; Acuna, D.C.; Boulanger, Y.; Chavardès, R.D.; Chen, J.; Englefield, P.; Flannigan, M.; et al. Drivers and Impacts of the Record-Breaking 2023 Wildfire Season in Canada. Nat. Commun. 2024, 15, 6764. [Google Scholar] [CrossRef] [PubMed]
  11. Rao, K.; Williams, A.P.; Diffenbaugh, N.S.; Yebra, M.; Konings, A.G. Plant-water sensitivity regulates wildfire vulnerability. Nat. Ecol. Evol. 2022, 6, 332–339. [Google Scholar] [CrossRef] [PubMed]
  12. Chaleplis, K.; Walters, A.; Fang, B.; Lakshmi, V.; Gemitzi, A. A Soil Moisture and Vegetation-Based Susceptibility Mapping Approach to Wildfire Events in Greece. Remote Sens. 2024, 16, 1816. [Google Scholar] [CrossRef]
  13. Zhang, G.; Wang, M.; Liu, K. Deep neural networks for global wildfire susceptibility modelling. Ecol. Indic. 2021, 127, 107735. [Google Scholar] [CrossRef]
  14. Scholten, R.C.; Coumou, D.; Luo, F.; Veraverbeke, S. Early snowmelt and polar jet dynamics co-influence recent extreme Siberian fire seasons. Science 2022, 378, 1005–1009. [Google Scholar] [CrossRef] [PubMed]
  15. Whitman, E.; Parisien, M.A.; Thompson, D.K.; Flannigan, M.D. Short-interval wildfire and drought overwhelm boreal forest resilience. Sci. Rep. 2019, 9, 18796. [Google Scholar] [CrossRef] [PubMed]
  16. Wang, S.S.C.; Wang, Y. Quantifying the effects of environmental factors on wildfire burned area in the south central US using integrated machine learning techniques. Atmos. Chem. Phys. 2020, 20, 11065–11087. [Google Scholar] [CrossRef]
  17. Westerling, A.L.; Hidalgo, H.G.; Cayan, D.R.; Swetnam, T.W. Warming and Earlier Spring Increase Western U.S. Forest Wildfire Activity. Science 2006, 313, 940–943. [Google Scholar] [CrossRef] [PubMed]
  18. Lv, Q.; Chen, Z.; Wu, C.; Peñuelas, J.; Fan, L.; Su, Y.; Yang, Z.; Li, M.; Gao, B.; Hu, J.; et al. Increasing severity of large-scale fires prolongs recovery time of forests globally since 2001. Nat. Ecol. Evol. 2025, 9, 980–992. [Google Scholar] [CrossRef] [PubMed]
  19. Amiri, A.; Gumiere, S.J.; Bonakdari, H. Firestorm in California: The new reality for wildland-urban interface regions. Urban Clim. 2025, 62, 102528. [Google Scholar] [CrossRef]
Figure 1. (a) Drought intensity across Canada showing areas ranging from abnormally dry (D0) to moderate drought (D1) as of the end of April 2025. Data were extracted from the Canadian Drought Monitor. (https://open.canada.ca/data/en/dataset/292646cd-619f-4200-afb1-8b2c52f984a2. accessed on 10 May 2025). (b) Manitoba burned areas were extracted from Landsat 8 and Sentinel-2 satellite images. The boundaries of the wildfires from May 2025 are marked in black, with the area of each wildfire labeled on the map. (c) Landsat 8 imagery from 4 May 2025 shows the initial fire ignition site with an early burned area delineated using Sentinel-2 imagery on 10 May 2025. (d) A significant wildfire expansion is evident in central-eastern Manitoba, as revealed by Sentinel-2 imagery from 14 May 2025. (e) Fire event in southeastern Manitoba with a smaller burned area, also mapped from Sentinel-2 data acquired on 14 May 2025. Yellow polygons indicate fire perimeters. The imagery uses a false-color composite with shortwave infrared 2 (SWIR-2), near-infrared (NIR), and blue bands.
Figure 1. (a) Drought intensity across Canada showing areas ranging from abnormally dry (D0) to moderate drought (D1) as of the end of April 2025. Data were extracted from the Canadian Drought Monitor. (https://open.canada.ca/data/en/dataset/292646cd-619f-4200-afb1-8b2c52f984a2. accessed on 10 May 2025). (b) Manitoba burned areas were extracted from Landsat 8 and Sentinel-2 satellite images. The boundaries of the wildfires from May 2025 are marked in black, with the area of each wildfire labeled on the map. (c) Landsat 8 imagery from 4 May 2025 shows the initial fire ignition site with an early burned area delineated using Sentinel-2 imagery on 10 May 2025. (d) A significant wildfire expansion is evident in central-eastern Manitoba, as revealed by Sentinel-2 imagery from 14 May 2025. (e) Fire event in southeastern Manitoba with a smaller burned area, also mapped from Sentinel-2 data acquired on 14 May 2025. Yellow polygons indicate fire perimeters. The imagery uses a false-color composite with shortwave infrared 2 (SWIR-2), near-infrared (NIR), and blue bands.
Earth 06 00088 g001
Figure 2. Spatial anomalies of key environmental variables across Manitoba during April 2025: (a) leaf area index (LAI) derived from the Moderate Resolution Imaging Spectroradiometer (MODIS) product MCD15A3H, (b) precipitation (mm) obtained from the European Centre for Medium-Range Weather Forecasts (ECMWF) ERA5-Land dataset, (c) air temperature (°C) obtained from ERA5-Land, and (d) January–May 2025 soil moisture anomaly (m3/m3) sourced from the ERA5-Land. The burned areas are shown as polygons with black outlines.
Figure 2. Spatial anomalies of key environmental variables across Manitoba during April 2025: (a) leaf area index (LAI) derived from the Moderate Resolution Imaging Spectroradiometer (MODIS) product MCD15A3H, (b) precipitation (mm) obtained from the European Centre for Medium-Range Weather Forecasts (ECMWF) ERA5-Land dataset, (c) air temperature (°C) obtained from ERA5-Land, and (d) January–May 2025 soil moisture anomaly (m3/m3) sourced from the ERA5-Land. The burned areas are shown as polygons with black outlines.
Earth 06 00088 g002
Figure 3. Interannual anomalies for April in Manitoba for four key environmental variables: (a) leaf area index (LAI), (b) normalized difference vegetation index (NDVI), (c) precipitation, (d) snow cover extent, and (e) soil moisture. LAI anomalies are derived from the MODIS MCD15A3H product; NDVI anomalies are calculated using the MODIS MOD09GQ product; precipitation and soil moisture data are from ERA5-Land; and snow cover anomalies are based on MODIS MOD10A1.
Figure 3. Interannual anomalies for April in Manitoba for four key environmental variables: (a) leaf area index (LAI), (b) normalized difference vegetation index (NDVI), (c) precipitation, (d) snow cover extent, and (e) soil moisture. LAI anomalies are derived from the MODIS MCD15A3H product; NDVI anomalies are calculated using the MODIS MOD09GQ product; precipitation and soil moisture data are from ERA5-Land; and snow cover anomalies are based on MODIS MOD10A1.
Earth 06 00088 g003aEarth 06 00088 g003b
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Amiri, A.; Gumiere, S.; Bonakdari, H. A Lens on Fire Risk Drivers: The Role of Climate and Vegetation Index Anomalies in the May 2025 Manitoba Wildfires. Earth 2025, 6, 88. https://doi.org/10.3390/earth6030088

AMA Style

Amiri A, Gumiere S, Bonakdari H. A Lens on Fire Risk Drivers: The Role of Climate and Vegetation Index Anomalies in the May 2025 Manitoba Wildfires. Earth. 2025; 6(3):88. https://doi.org/10.3390/earth6030088

Chicago/Turabian Style

Amiri, Afshin, Silvio Gumiere, and Hossein Bonakdari. 2025. "A Lens on Fire Risk Drivers: The Role of Climate and Vegetation Index Anomalies in the May 2025 Manitoba Wildfires" Earth 6, no. 3: 88. https://doi.org/10.3390/earth6030088

APA Style

Amiri, A., Gumiere, S., & Bonakdari, H. (2025). A Lens on Fire Risk Drivers: The Role of Climate and Vegetation Index Anomalies in the May 2025 Manitoba Wildfires. Earth, 6(3), 88. https://doi.org/10.3390/earth6030088

Article Metrics

Back to TopTop