Historical Alberta Wildfire Data

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About the Data

This data set contains information on wildfires in Canada, compiled from official government sources under the Open Government Licence – Alberta.

The data was gathered to monitor, assess, and respond to wildfire risks across different regions. Wildfires have far-reaching environmental, social, and economic consequences. From an equity and inclusion perspective, analyzing wildfire data can reveal geographic and resource-based disparities in detection and containment efforts, and highlight how certain populations face greater risks due to climate change and limited infrastructure.

In particular, Alberta experiences some of the most severe and frequent wildfires in Canada due to its vast forested areas, dry climate, and increasing temperatures linked to climate change. Wildfires in Alberta can lead to widespread evacuations, destroy homes and livelihoods, and disproportionately affect rural and Indigenous communities, who may lack access to adequate emergency services and infrastructure. Understanding the patterns of wildfire occurrence and spread helps policymakers, environmental planners, and emergency services allocate resources more equitably and implement effective mitigation strategies. This data set enables data-driven approaches to reduce the impact of wildfires and support more resilient and inclusive disaster management practices across Alberta and beyond.

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Metadata

CSV Name

wildfire.csv

Data Set Characteristics

Multivariate

Subject Area

Climate Change

Associated Tasks

Classification, Time Series, Geospatial Analysis

Feature Type

Categorical, Integer

Instances

26551 records

Features

50

Has Missing Values?

Yes

Variables

Variable Name	Role	Type	Description	Units	Missing Values
year	ID	Integer	Year in which the wildfire was first detected incident	Year	No
fire_number	ID	String	Identifier for the wildfire	-	No
current_size	Feature	Numeric	Final estimated area burned by the wildfire	Hectares	No
size_class	Feature	Categorical	Size classification based on final area burned	-	No
latitude	Feature	Numeric	Latitude coordinate of the wildfire origin	Degrees	No
longitude	Feature	Numeric	Longitude coordinate of the wildfire origin	Degrees	No
fire_origin	Metadata	Categorical	Who owns or administers the land the wildfire ignited on	-	No
general_cause	Feature	Categorical	Classification of the wildfire cause	-	No
responsible_group	Metadata	Categorical	Recreational group responsible for causing the wildfire	-	No
activity_class	Feature	Categorical	Activity that was going on when the wildfire started	-	No
true_cause	Feature	Categorical	Specific reason why the wildfire started (e.g., “Arson Known”, “Hot Exhaust”, “Line Impact”, “Unattended Fire”, etc.)	-	No
fire_start_date	Time	Date	Datetime the wildfire started	YYYY-MM-DD	Yes
detection_agent_type	Feature	Categorical	Type of detection agent that discovered the wildfire (e.g., lookout (“LKT”), aircraft (“AIR”))	-	No
detection_agent	Feature	Categorical	Specific type of detection agent that discovered the wildfire	-	No
assessment_hectares	Feature	Numeric	Size of the wildfire at the time of assessment	Hectares	No
fire_spread_rate	Feature	Numeric	Rate at which the wildfire spread at the time of initial assessment	Metres/minute	No
fire_type	Feature	Categorical	Predominant wildfire behavior classification at the time of initial assessment (e.g., “Surface”, “Ground”, “Crown”)	-	No
fire_position_on_slope	Feature	Categorical	Position of the wildfire relative to the slope it is travelling on at the time of initial assessment (e.g., “Bottom”, “Middle 1/3”, “Unknown”)	-	No
weather_conditions_over_fire	Feature	Categorical	Weather conditions over the wildfire at the time of initial assessment	-	No
temperature	Feature	Numeric	Temperature at the wildfire location at the time of initial assessment	°C	Yes
relative_humidity	Feature	Numeric	Relative humidity at the wildfire location at the time of initial assessment	%	Yes
wind_direction	Feature	Categorical	Wind direction at the wildfire location at the time of initial assessment	-	No
wind_speed	Feature	Numeric	Wind speed at the wildfire location in km/h at the time of initial assessment	km/h	Yes
fuel_type	Feature	Categorical	Dominant fuel type (vegetation cover) in which the wildfire is burning at the wildfire location at the time of initial assessment	-	No
initial_action_by	Metadata	Categorical	Group that initiated suppression efforts	-	No
ia_arrival_at_fire_date	Time	DateTime	Datetime when the initial action group arrived at the wildfire	YYYY-MM-DD	Yes
ia_access	Feature	Categorical	Method of access that the initial action group used	-	No
fire_fighting_start_date	Time	DateTime	Datetime when the initial action group began firefighting activities	YYYY-MM-DD	Yes
fire_fighting_start_size	Feature	Numeric	Wildfire size at the time firefighting began	Hectares	No
bucketing_on_fire	Feature	Binary	Whether aerial bucketing was used on the wildfire	Yes/No	No
first_bh_date	Time	DateTime	Datetime when wildfire was first declared being held	YYYY-MM-DD	No
first_bh_size	Feature	Numeric	Wildfire size when wildfire was first declared being held	Hectares	No
first_uc_date	Time	DateTime	Datetime when wildfire was first declared under control	YYYY-MM-DD	No
first_uc_size	Feature	Numeric	Wildfire size when first declared under control	Hectares	No
first_ex_size_perimeter	Feature	Numeric	Wildfire size when first declared extinguished	Hectares	No

library(reticulate)
if (Sys.getenv("GITHUB_ACTIONS") == "true") {
  # for running in GitHub Actions (otherwise reticulate can't find diverse_web_env)
  reticulate::use_python(Sys.getenv("RETICULATE_PYTHON"), required = TRUE)
} else {
  # for running locally
  reticulate::use_condaenv("diverse_web_env", required = TRUE)
}

Key Features of the Data Set

Each row represents a single wildfire incident and includes information such as:

• Environmental conditions (temperature, wind_speed, relative_humidity) – Air temperature (°C), wind speed (km/h) and relative humidity (%) near the fire; influence fire intensity and spread.

• Fire behavior metrics (fire_spread_rate, fire_type, fuel_type) – Fire expansion rate (ha/h), behavior class (surface, crown) and dominant fuel; determine growth and management.

• Access difficulty (ia_access) – Ease of crew access; low access delays response.

• Location coordinates (latitude, longitude) – Decimal degrees of fire origin; used for mapping and spatial analysis.

Purpose and Use Cases

This data set is designed to support analysis of:

• Factors contributing to the spread, intensity, and size of wildfires

• The impact of weather conditions and fuel types on fire behavior

• Geographic and seasonal patterns in wildfire occurrence

• The effectiveness and timeliness of initial suppression efforts

• Relationships between fire causes, detection methods, and responsible parties

Case Study

Objective

Large wildfires pose serious environmental, social, and economic challenges, especially as climate conditions become more extreme. Identifying the key environmental and human factors linked to these fires can help guide more effective prevention and response strategies.
So, our main question is:

Can we identify the environmental and human factors most associated with large wildfires?

According to Natural Resources Canada, wildfires exceeding 200 hectares in final size are classified as “large fires.” While these fires represent a small percentage of all wildfires, they account for the majority of the total area burned annually.
The goal is to explore potential predictors of fire size, such as weather, fire cause, and detection method, and provide insights that could inform early interventions and resource planning.

Analysis

Loading Libraries

# Data
library(diversedata)      # Diverse Data Hub data sets

# Core libraries
library(tidyverse)        
library(lubridate)      

# Spatial & mapping
library(sf)               
library(terra)            
library(ggmap)            
library(ggspatial)        
library(maptiles)         
library(leaflet)          
library(leaflet.extras)   

# Visualization & color
library(viridis)          

# Tables & reporting
library(gt)               
library(kableExtra)       

# Modeling & interpretation
library(marginaleffects)  
library(broom)           

1. Data Cleaning & Processing

• Converted fire size to numeric
• Created a binary variable large_fire (TRUE if >200 ha)
• Filtered out incomplete records

# Reading Data  
wildfire_data <- wildfire

# Clean and prepare base data
wildfire_clean <- wildfire_data |>
  filter(!is.na(assessment_hectares), assessment_hectares > 0) |>
  mutate(
    large_fire = current_size > 200,
    true_cause = as.factor(true_cause),
    detection_agent_type = as.factor(detection_agent_type),
    temperature = as.numeric(temperature),
    wind_speed = as.numeric(wind_speed)
  )

# Drop unused levels for modeling
wildfire_clean <- wildfire_clean |>
  filter(!is.na(true_cause), !is.na(detection_agent_type)) |>
  mutate(
    true_cause = droplevels(true_cause),
    detection_agent_type = droplevels(detection_agent_type)
  )

2. Exploratory Data Analysis

Map of Wildfire Size and Location in Alberta

This interactive map displays the geographic distribution and relative size of wildfires across Alberta, using red circles sized by fire area. Each point represents a wildfire event, with larger circles indicating more extensive burns. The map reveals regions with concentrated wildfire activity and visually emphasizes differences in fire magnitude across the province.

Note
To provide geographic context for our wildfire data, we added a shapefile representing Alberta’s boundaries.
This shapefile was sourced from the Alberta Government Open Data Portal and specifically corresponds to the Electoral Division Shapefile (Bill 33, 2017).
The data was processed and transformed to the appropriate geographic coordinate system to enable mapping alongside our wildfire data set.

# map
leaflet() |>
  addProviderTiles("CartoDB.Positron") |> 
  setView(lng = -115, lat = 55, zoom = 5.5) |> 
  addPolygons(data = alberta_shape, 
              color = "#CCCCCC",     
              weight = 0.5,         
              fillOpacity = 0.02,   
              group = "Alberta Boundaries") |>
  addCircles(data = wildfire_sf,
             radius = ~sqrt(current_size) * 30,  
             fillOpacity = 0.6,
             color = "red",
             stroke = FALSE,
             group = "Wildfires") |>
  addLayersControl(overlayGroups = c("Alberta Boundaries", "Wildfires"),
                   options = layersControlOptions(collapsed = FALSE)) |>
  addLegend(position = "bottomright", 
            title = "Wildfire Size (approx.)",
            colors = "red", 
            labels = "Larger = Bigger fire")

Proportion of Large Fires by Cause

wildfire_clean |>
  group_by(true_cause) |>
  summarize(prop_large = mean(large_fire, na.rm = TRUE)) |>
  filter(prop_large > 0) |>
  ggplot(aes(x = reorder(true_cause, prop_large), y = prop_large, fill = prop_large)) +
  geom_col() +
  coord_flip() +
  scale_fill_gradient(low = "skyblue1", high = "skyblue4") +  
  labs(
    title = "Proportion of Large Fires by True Cause",
    x = "True Cause",
    y = "Proportion of Fires > 200 ha",
    fill = "Proportion"
  ) +
  theme_minimal() +
  theme(
    plot.title = element_text(size = 14, face = "bold"),
    axis.text.y = element_text(size = 10),
    axis.title = element_text(size = 12)
  )

3. Logistic Regression Model

Governments and emergency planners often care about whether a fire becomes large, not necessarily exactly how large. This makes a binary classification more interpretable and actionable for planning responses. Logistic regression predicts probability of exceeding a threshold, such as “Will this fire exceed 200 hectares?” Modeling the probability of exceeding such a threshold is often more operationally useful than modeling exact hectares.

In Decision Making for Wildfires: A Guide for Applying a Risk Management Process at the Incident Level, the authors outline a risk-based decision-making framework. A key concept is identifying risk thresholds to guide decisions. This aligns with the broader goals of wildfire risk management, which emphasize anticipating fire severity and planning appropriate responses. Logistic regression is well-suited to this context because it models the probability of crossing such thresholds, such as a fire becoming large, enabling a clear, interpretable basis for making timely, risk-informed decisions.

We built a logistic regression model to predict the likelihood of a fire becoming large based on a set of environmental and operational factors that are consistently measurable, statistically significant, and operationally relevant.

In our logistic regression model, we selected key environmental and contextual variables from the wildfire_clean data set that are well-established drivers of wildfire behavior. These include:

• temperature: Higher temperatures increase evaporation, dry out vegetation, and promote ignition and fire spread.

• wind_speed: Strong winds feed oxygen to the fire and can carry embers over long distances, accelerating spread.

• relative_humidity: Low humidity conditions dry fuels, increasing the probability and intensity of fire ignition.

• fire_spread_rate: Reflects how quickly a fire expands; a dynamic indicator of fire behavior.

• fire_type: Indicates how the fire behaves (e.g., surface vs. crown fire), which affects controllability and risk.

• fuel_type: Different vegetation types burn at different intensities and rates; fuels like grass or timber respond differently under the same conditions.

• ia_access: Stands for Initial Attack Access. Limited access can delay suppression efforts, allowing fires to grow larger.

These variables were chosen because they each represent core determinants of ignition likelihood, fire intensity, and suppression difficulty. As explained in Introduction to Wildland Fire by Pyne, Andrews, and Laven, this theoretical foundation supports our inclusion of both meteorological and environmental variables in the model.

Mathematical Definition of the Logistic Regression Model

We aim to estimate the probability that a wildfire becomes large (i.e., burns more than 200 hectares), using logistic regression.

Let:

\[ Y_i = \begin{cases} 1, & \text{if fire } i \text{ is large (area > 200 ha)} \\ 0, & \text{otherwise} \end{cases} \]

\[ \mathbf{x}_i = \left( \text{temperature}_i, \text{wind\_speed}_i, \text{relative\_humidity}_i, \text{fire\_spread\_rate}_i, \text{fire\_type}_i, \text{fuel\_type}_i, \text{ia\_access}_i \right) \]

Then the model is defined as:

\[ \Pr(Y_i = 1 \mid \mathbf{x}_i) = \frac{1}{1 + \exp(-\eta_i)} \]

where the linear predictor is:

\[ \eta_i = \beta_0 + \beta_1 \cdot \text{temperature}_i + \beta_2 \cdot \text{wind\_speed}_i + \beta_3 \cdot \text{relative\_humidity}_i + \beta_4 \cdot \text{fire\_spread\_rate}_i + \boldsymbol{\beta}_{\text{cat}}^\top \mathbf{x}_{i,\text{cat}} \]

Here:

\[ \begin{aligned} \beta_0 & \text{ is the intercept} \\ \boldsymbol{\beta}_{\text{cat}} & \text{ is the vector of coefficients for the categorical predictors} \\ \mathbf{x}_{i,\text{cat}} & \text{ is the vector of dummy variables representing those categorical predictors} \end{aligned} \]

model <- glm(
  large_fire ~ temperature + wind_speed + relative_humidity +
    fire_spread_rate + fire_type + fuel_type + ia_access,
  data = wildfire_clean,
  family = "binomial"
)

tidy_model <- tidy(model) |>
  mutate(
    estimate = round(estimate, 3),
    std.error = round(std.error, 3),
    statistic = round(statistic, 2),
    p.value = round(p.value, 4)
  )

kable(tidy_model
      , caption = "Logistic Regression Results: Predicting Large Fires (> 200 ha)") |>
  kable_styling(bootstrap_options = c("striped", "hover", "condensed", "responsive"), full_width = FALSE)

Logistic Regression Results: Predicting Large Fires (> 200 ha)

term	estimate	std.error	statistic	p.value
(Intercept)	-2.016	0.401	-5.03	0.0000
temperature	0.048	0.010	4.66	0.0000
wind_speed	0.050	0.004	11.03	0.0000
relative_humidity	-0.031	0.004	-7.64	0.0000
fire_spread_rate	0.104	0.010	10.30	0.0000
fire_typeGround	-1.354	0.184	-7.37	0.0000
fire_typeSurface	-1.093	0.129	-8.48	0.0000
fire_typeUnknown	-13.012	3683.753	0.00	0.9972
fuel_typeC2	-0.945	0.175	-5.40	0.0000
fuel_typeC3	-1.024	0.276	-3.71	0.0002
fuel_typeC4	0.454	0.337	1.35	0.1775
fuel_typeC6	-16.192	4492.954	0.00	0.9971
fuel_typeC7	-16.211	1258.218	-0.01	0.9897
fuel_typeD1	-16.322	274.554	-0.06	0.9526
fuel_typeM1	-1.798	0.362	-4.97	0.0000
fuel_typeM2	-2.272	0.279	-8.13	0.0000
fuel_typeM3	-15.610	3734.948	0.00	0.9967
fuel_typeM4	-15.179	6522.639	0.00	0.9981
fuel_typeO1a	-2.912	0.289	-10.08	0.0000
fuel_typeO1b	-3.514	0.456	-7.70	0.0000
fuel_typeS1	-2.189	0.486	-4.51	0.0000
fuel_typeS2	-2.242	0.546	-4.11	0.0000
fuel_typeUnknown	-4.148	0.481	-8.62	0.0000
ia_accessGround	-0.861	0.410	-2.10	0.0356
ia_accessHover Exit	-0.083	0.412	-0.20	0.8407
ia_accessRappel	-14.797	554.243	-0.03	0.9787
ia_accessUnknown	0.428	0.107	3.99	0.0001

Higher wind speed (0.050, p < 0.001), temperature (0.048, p < 0.001), and fire spread rate (0.104, p < 0.001) significantly increase the odds of a large wildfire, while relative humidity (-0.031, p < 0.001) decreases it. Compared to crown fires, ground fires (-1.354, p < 0.001) and surface fires (-1.093, p < 0.001) are much less likely to result in large fires.

This logistic regression model estimates the factors influencing the likelihood of a large wildfire. Higher temperature, wind speed, and fire spread rate significantly increase the odds of a large fire, while higher relative humidity decreases it. Certain fire types (e.g., Ground, Surface) and fuel types (e.g., M1, M2, O1a, O1b) are associated with significantly lower odds compared to their respective reference categories. The model shows that higher wind speed, lower humidity, and faster fire spread significantly increase the risk of large wildfires.

Let’s dig into our model further by examining how different environmental and operational factors interact to influence fire outcomes.

4. Interpretation of our Model using marginaleffects

The Role of Wind Across Fire Causes

As you’ve likely noticed, we did not include true_cause as a predictor in our logistic regression model because it contains many categories, some of which have very few observations. This can lead to large standard errors, unstable coefficient estimates, and a higher risk of overfitting.

However, true_cause remains an important variable for exploratory analysis. Certain ignition causes may be more sensitive to wind. For example, sparks from power lines can spread quickly in high winds, embers from debris burning can travel farther, and unattended fires can escalate rapidly under windy conditions. We chose wind speed for this analysis because it is a well-documented environmental amplifier of fire behavior particularly when interacting with certain ignition causes.

Given these interactions, it’s valuable to visualize and investigate how the effect of wind speed on large wild fire development varies across different causes. Let’s explore this further through faceted marginal effect plots.

This plot shows how wind speed affects the probability of a large wildfire, and how that effect varies across different true causes of fire.

• The x-axis shows the different values of true_cause (fire ignition source categories).

• The y-axis shows the marginal effect of wind speed on the predicted probability (i.e., on the response scale) of a fire becoming large.

The plot helps us compare the sensitivity of different fire causes to wind speed. For example, if one cause shows a higher marginal effect, it means that increasing wind speed has a stronger impact on the likelihood of large fires for that cause.

p <- plot_comparisons(
  model,
  variables = "wind_speed",
  by = "true_cause",
  type = "response"
)

p +
  scale_color_manual(values = rep("darkgreen", length(unique(p$data$by)))) +
  scale_fill_manual(values = rep("darkgreen", length(unique(p$data$by)))) +
  labs(
    title = "Effect of Wind Speed on Large Fire Probability by True Cause",
    x = "True Cause",
    y = "Marginal Effect of Wind Speed"
  ) +
  theme_minimal() +
  theme(axis.text.x = element_text(angle = 45, hjust = 1))

The marginal effects analysis suggests that wind speed may have a relatively stronger impact on the probability of a fire becoming large when the ignition cause is related to Unknown, Insufficient Buffer, Incendiary Device, Hot Exhaust, or Line Impact. However, the overall changes in predicted probabilities are quite small, and the error bars across causes show substantial overlap. This indicates a high degree of uncertainty and suggests that these differences should be interpreted with caution. While the findings may not yet be strong enough to inform operational decisions, they do highlight areas for further exploration. In particular, when wind is forecasted in regions with a history of certain ignition causes, fire managers could use this exploratory insight to guide risk monitoring strategies, while recognizing that more robust evidence is needed before drawing firm conclusions.

Interaction Effects via Marginal Effects

We can also use marginal effects to explore interactions without explicitly adding them to the model, by conditioning on another variable.

This plot shows the marginal effect of relative_humidity on the predicted probability of large fire, calculated separately for each level of fire_type, based on your fitted model.

plot_comparisons(model, variables = "relative_humidity", by = "fire_type")

When comparing the marginal effect of relative humidity across fire types, we found that three fire types showed almost no change in large fire probability as humidity increased. However, one fire type exhibited a noticeably stronger negative effect. This suggests that humidity plays a more meaningful role in suppressing fire growth for certain fire types likely those that are more sensitive to moisture availability, such as crown fires—while having minimal effect on others.

Discussion

This analysis aimed to uncover the key environmental and operational factors associated with the development of large wildfires in Alberta. Using logistic regression and marginal effects, we modeled the probability of a wildfire exceeding 200 hectares, which is a meaningful operational threshold for fire managers.

We found that higher temperature, stronger wind speed, and faster spread rates significantly increase the likelihood of a large wildfire. Conversely, higher relative humidity consistently reduced fire size probability, highlighting its protective role in fire suppression.

In addition to main effects, we explored interaction patterns using marginal effects. While we did not include true_cause directly in the model due to its high cardinality and sparse categories, we used it in conjunction with wind_speed to explore how ignition causes might modulate wind’s influence on fire growth. The marginal effect plots suggest that certain causes—such as incendiary devices, line impacts, or insufficient buffer zones are more sensitive to wind speed, potentially due to the nature of how these fires spread under wind-driven conditions.

Similarly, by plotting the effect of relative_humidity across different fire_type categories, we observed that humidity suppresses large fire development more strongly in certain fire types, particularly crown fires. This implies that moisture-based mitigation strategies may be more effective in forests prone to crown fire behavior, while having less impact on surface or ground fires.

While some observed differences in marginal effects were small in magnitude and had overlapping confidence intervals, these nuanced insights still provide value. They highlight where future research or localized fire management protocols could focus, especially under climate scenarios with increasing temperature and wind extremes.

Overall, this case study illustrates how statistical modeling paired with domain-informed exploratory tools like marginal effects can support risk-informed, data-driven wildfire management.

Attribution

Data sourced from the Government of Alberta via the Government of Canada’s Open Government Portal, available under an Open Government Licence - Alberta. Original data set: Historical wildfire data: 2006-2024.