Community Wildfire Protection Plan

For the cities of Monterey, Carmel-by-the-Sea, and Pacific Grove

A wide landscape shot showing the Point Pinos Lighthouse Reservation and Ocean View Boulevard in Pacific Grove in the forefront of the view. The built landscape and trees lie behind the view of this park, and the coastline extends east outside of frame and to the northwest, where the Monterey Coastline continues. Mountains are in view behind the Monterey Coastline. Blue ocean expands out from the coastlines.
Monterey Fire Department's logo shows a red hard hat, a wooden and metal tool, and a fire hose attachment, overlaying a red circular symbol with the text "EST 1884". Logos for all three cities (Monterey, Pacific Grove, and Carmel-by-the-Sea) are circular. The City of Monterey logo shows a horse and a bull on the left and right areas of the circle, with a rising sun on the top part of the circle and a crest with an anchor on the top left of the crest, tree on the bottom right, and a bandolier running from the top right to the bottom left of the crest. The City of Pacific Groce features the silhouette of a eucalyptus tree with a bright orange monarch butterfly overlaying the silhouette and the circular logo. City of Carmel-by-the-Sea features a mission building (Mission San Carlos Borromeo de Carmelo) within its circular logo.
Monterey Fire Department's logo shows a red hard hat, a wooden and metal tool, and a fire hose attachment, overlaying a red circular symbol with the text "EST 1884". Logos for all three cities (Monterey, Pacific Grove, and Carmel-by-the-Sea) are circular. The City of Monterey logo shows a horse and a bull on the left and right areas of the circle, with a rising sun on the top part of the circle and a crest with an anchor on the top left of the crest, tree on the bottom right, and a bandolier running from the top right to the bottom left of the crest. The City of Pacific Groce features the silhouette of a eucalyptus tree with a bright orange monarch butterfly overlaying the silhouette and the circular logo. City of Carmel-by-the-Sea features a mission building (Mission San Carlos Borromeo de Carmelo) within its circular logo.

Logos for Monterey Fire Department, City of Monterey, City of Pacific Grove, and City of Carmel-by-the-Sea.

Introduction

Welcome to the Monterey CWPP story map. Please scroll through to learn about this project including the purpose of this wildfire planning tool, the cities and communities involved in the Plan Area, public engagement opportunities, and more. The story map will feature online visuals to help interested stakeholders and the public engage and learn more about different components of the CWPP and efforts in the Plan Area to increase wildfire resilience in our communities. This website will serve as the project hub and will be updated as the project progresses.

With the increased severity and frequency of wildfires in California, community wildfire planning is increasingly important to help prepare for and adapt to wildfire. Community Wildfire Protection Plans (CWPPs) are a tool to help reduce the severity and impact of wildfires and increase community resilience. This plan is the first to cover the Plan Area, which include the Cities of Monterey, Pacific Grove, and Carmel-by-the-Sea.

Left to Right: Monterey, Pacific Grove and Carmel-by-the-Sea

A firefighter from Monterey Fire Department looks in the distance to a hovering Air Operations helicopter. The green trees from the area below the ledge that the firefighter is on peek above the ground level, but the mountains in the background and behind the Air Operations helicopter are obscured by the fire smoke. The smokiness causes the background to appear a grey-orange color.
A firefighter from Monterey Fire Department looks in the distance to a hovering Air Operations helicopter. The green trees from the area below the ledge that the firefighter is on peek above the ground level, but the mountains in the background and behind the Air Operations helicopter are obscured by the fire smoke. The smokiness causes the background to appear a grey-orange color.

Monterey Fire Department and Air Operations responding to a fire in Carmel Valley.

As a key component of the Healthy Forest Restoration Act of 2003, a Community Wildfire Protection Plan (CWPP) serves as a mechanism for community input and identification of areas presenting high wildfire risk, as well as identification of potential projects intended to mitigate such risk. Further, the CWPP process is intended to provide the community a forum for identifying values at risk from wildfire, which may include people, property, natural resources, agricultural lands, cultural resources, economic interests, and infrastructure. The identification of these values at risk strongly influences the potential wildfire hazard mitigation projects identified in this CWPP.

Two firefighters from Monterey Fire Department are standing on blackened earth, responding to a fire. Trees behind them are scorched, and the silhouette of the mountains in the background can be seen despite the smoke. The firefighter on the left is holding a McLeod while the firefighter on the right holds a hoe. Both of these tools are used to clear brush and construct fire control lines.

Monterey Fire Department responding to a fire in Carmel Valley.

This CWPP is being developed by the Monterey Fire Department, in coordination with the Cities of Monterey, Carmel-by-the-Sea, and Pacific Grove, with input and direction from stakeholders, agency representatives, and community members. This CWPP is intended to serve as a fire protection planning document that presents the community’s physical characteristics, wildfire hazard, assets at risk from wildfire, wildfire risk reduction approaches, vegetation/fuel management projects, and goals and action items intended to reduce wildfire risk in the Plan Area.


Plan Area

The plan area encompasses the cities of Monterey, Pacific Grove, and Carmel-by-the-Sea. The Plan Area has an estimated population of 49,000 (U.S. Census 2020). The majority of people reside in the City of Monterey with an estimated population of 30,218 people, compared to 3,220 people in Carmel-by-the-Sea and 15,090 people in Pacific Grove.

coded in the map as orange (Pacific Grove), teal (Monterey), and baby blue (Carmel-by-the-Sea). Pacific Grove and Monterey boundaries are right next to each other, while Carmel-by-the-Sea is less than a mile south of Monterey.

CWPP Goals and Purpose

The goals of the CWPP have been developed with input from the project Working Group, which consists of a group of key stakeholders assembled by the Monterey Fire Department. The project Working Group meet monthly and have been tasked with providing input on the project. Overall, the guiding principles and goals of the CWPP aim to increase community resilience and protect lives, property, assets, and Plan Area resources threatened by wildland fire. The guiding principles and goals will be used to guide the CWPP action plan to identify effective, prioritized wildfire mitigation and fuel reduction projects and to assist in qualifying for state and federal grant funding. To view the Goals of this CWPP,  refer to Table 3 (Community Wildfire Protection Plan Goals) located within Section 1.3 (Community Wildfire Protection Plan Goals) of the CWPP. 

In this view, a two story white building on the left of the picture with pillars in front and a one story portion of the brick-laid building to its right. These buildings belong to Monterey City Hall. Decorative small trees and shrubs are located within 15 feet of the buildings, with green grass shown outside of the decorative area, and a decorative bear statue is facing the forefront of the picture as if it is walking toward the viewer. Smokey skies above Monterey City Hall color the sky as dusty orange.

Smoky skies above Monterey City Hall


Project Timeline

November 2022

Project Kickoff

December 2022 - February 2023

Conduct hazard risk assessment

January 2023

Begin community outreach

January 2023 – June 2023

Stakeholder Working Group meetings

February 2023 - July 2023

Preparation of CWPP

May 2023

Community Workshops

May 2023

Close public survey

June 2023

Final Stakeholder Working Group meeting

July/August 2023

Finalize CWPP


Contact

Community Wildfire Protection Plan Contact Form


Community Engagement

Get involved!

Public input and discussion is a critical component of developing a successful and implementable CWPP. To ensure that this CWPP reflects the priorities and concerns of the local community, this project has included a three-tier public outreach approach involving a public survey, a stakeholder working group, and community workshops. The public survey was open from late January through May 2023, and public workshops took place in May 2023.

Community Survey Results

Survey participants were asked to identify their top wildfire concerns, as well as desired actions to mitigate wildfire risk. Each graph displays the percentage of the survey respondents from each city that selected each concern or desired action. These subsets were chosen to help identify action items based on the worries and desires from each city. Use the arrows below to see the results for each city.


Community Workshops

In-person community workshops were held in May 2023 to foster a community-driven discussion and further learn about the wildfire concerns throughout the unique communities in the Plan Area. One workshop was held in each Plan Area city at the following dates and times. Workshops were open to the public. The workshops included an array of activities and discussion topics to get input from residents, landowners, and community stakeholders regarding your concerns related to wildfire and how the CWPP can reflect the community’s priorities for mitigating wildfire risk. For a full write-up of the community workshops and the results from the community engagement activities,  refer to Appendix B (Community Outreach) of the CWPP. 

May 23, 2023

Carmel-by-the-Sea 6:30 pm -8:30 pm  Sunset Center  – Carpenter Hall W/s Mission between 8th & 10th Carmel, CA 93921

May 24, 2023

Monterey 6:00 pm - 8:30 pm  Conference Center  1 Portola Plz. Monterey, CA 93940

May 25, 2023

Pacific Grove 6:00 pm - 8:30 pm  Community Center  515 Junipero Ave. Pacific Grove, CA 93950


Community Workshop Activity Results

The community workshops included map activity where community members could identify areas of concern, including limited evacuation routes, hazardous vegetation, and structures where structural hardening is needed.  Areas pinned by community members are shown in the map below. Many of the pins were in areas that participants lived in or were familiar with which gave great insight into those areas; however, it left a gap for areas where we did not have representation at the workshops. This is especially true for the eastern half of Monterey, including Deer and Fisherman Flats.


Fire Environment

Local Wildfire Conditions

Wildfire conditions can be described through the local fire environment and fire regimes. The fire environment describes the surrounding conditions that interact to influence wildfire behavior, and the fire regime is a general pattern of fire occurrence in a particular location or vegetation type. The Plan Area’s fire environment, fire regimes, wildland urban interface (WUI), and fire history are described in the following sections.

The main components of a location’s fire environment include weather (temperature, wind, relative humidity), fuel conditions, and topography.

Fire Behavior Triangle

A triangle displays the three main components of fire behavior. A mini triangle is in the center, which shows symbols for a tree and fire next to one another. The left side of the triangle says "weather", and shows the sun and clouds moving in one direction with the text of weather factors: "wind, temperature, and precipitation." The right side of the triangle says "Topography", with an outline of raised mountain peaks, to convey the topographical factors "slope or aspect (side) of the land." The bottom of the triangle says "Fuel", and shows an outline of three trees bunched together with the text "amount, arrangement, and more."

Fire Behavior Triangle Diagram


Weather

The Plan Area is generally characterized by a Mediterranean climate with dry summers followed by cool, wet winters. Average annual rainfall is roughly 20 inches, the majority falling between November and April (US Climate Data, 2023). Fog is often present during the summer months as a result of warm air from inland areas meeting cold marine air.  Peak fire season is considered to be in the fall when air temperatures are highest and relative humidity drops (CAL FIRE, 2020). This leads to the drying of vegetation and higher potential for wildfire ignition and spread. However, wildfires can occur during all times of the year due to local weather variations including drought conditions, high winds, or unusually high temperatures, all of which occur throughout California.

On average, the prevailing day time wind direction is from the northwest blowing in from the Pacific Ocean. This brings cool moist air into the region developing a pattern referred to as the “marine layer” which produces fog and low clouds over Monterey Peninsula. However, the presence of the Pacific Ocean causes a diurnal wind pattern known as the land/sea breeze system. During the day, onshore winds are from the northwest and at night, gentler offshore winds, derived from cooler air masses moving downslope, are from the east, and travel from higher elevations to the coast.

During the summer season, the diurnal winds can be slightly stronger than the winds during the winter season due to greater pressure gradient forces. These stronger onshore winds can contribute to fire hazard when appropriate conditions exist for wildfire ignition and spread as observed during the 1987 Morse Fire when strong onshore winds in combination with prolonged drought contributed to extreme wildfire behavior. Surface winds can also be influenced locally by topography and slope variations. The varied topography of the Monterey Peninsula affects wind velocity and patterns.

A high-elevation view of silhouettes of trees and treetops of varying densities and distances from one another, though many are nearby each other. These trees comprise a Monterey Pine Forest, and fog obscures some of the visibility of the trees and picture.

Fog over Monterey Pine Forest


Offshore winds

Santa Lucia Winds

The region also experiences occasional offshore wind events from the east generally referred to as Santa Lucia winds. Santa Lucia winds are caused by high-pressure systems that form over the Great Basin area of Nevada and Utah. These high-pressure systems create a gradient between the inland and coastal areas of California, leading to a rush of air from the high-pressure areas to the east to the lower-pressure area along the California coast. As the wind moves across the Santa Lucia mountains and descends to lower elevations, it becomes compressed and heated, leading to an increase in temperature and a decrease in relative humidity. This dry, warm wind can pick up speed as it moves through narrow canyons and passes, further contributing to its destructive potential. While stronger offshore wind events are more likely to occur to the south in the Big Sur region, the Monterey Peninsula is subject to infrequent periods of extreme fire weather. Santa Lucia winds are most likely to occur in the late fall and early winter, clearing out marine fog and creating dangerous fire weather conditions.

Prevailing Wind Direction

Prevailing winds are onshore and generally blow from the northwest. Onshore winds can bring in moisture from the ocean, increasing the humidity levels and potentially reducing the flammability of vegetation. However, if the wind is strong enough fire behavior can be exacerbated despite higher fuel moistures.

"Prevailing winds" are shown moving from a northwest to southeast direction--in the direction from the ocean to the land.

Offshore Wind Direction

Offshore winds blow from the northeast/east and are typically associated with low humidity and increased temperatures which can lead to drier vegetation. This combination of dry fuel and strong winds can create ideal conditions for fire spread. Strong offshore winds can also make fire suppression difficult due to an increase in spot fires occurring ahead of the main fire front.

"Offshore winds" are shown moving from a northeast to west direction--in the direction from the land to the ocean.

Topography

Terrain affects wildfire movement and spread. Flat areas typically result in slower fire spread, absent windy conditions. Topographic features such as saddles, canyons, and chimneys may form unique circulation conditions that concentrate winds and funnel or accelerate fire spread (i.e., land formations that collect and funnel heated air upward along a slope). Steep terrain typically results in faster upslope fire spread due to the pre-heating of uphill vegetation. Terrain may also buffer, shelter, or redirect winds away from some areas based on canyons or formations on the landscape. Saddles occurring at the top of drainages or ridgelines may facilitate the migration of wildfire from one canyon to the next. Various terrain features can also influence fire behavior, as summarized below.

Narrow Canyon Surface winds follow canyon direction, which may differ from the prevailing wind; wind eddies/strong upslope air movement is expected, which may cause erratic fire behavior; radiant heat transfer between slopes facilitates spotting/ignition on the opposite canyon side.

Wide Canyon Prevailing wind direction is not significantly altered; aspect is a significant contributor to fire behavior. Wide canyons are not as susceptible to cross-canyon spotting except in high winds.

Box Canyon/ Chute Air is drawn in from the canyon bottom, resulting in strong upslope drafts. No gaps or prominent saddles to let heated air escape. Fires starting at the canyon bottom can rapidly move upslope due to chimney-like preheating of the higher-level fuels and upslope winds. 

Ridge Fires may change direction when reaching the ridge/canyon edge; strong airflows are likely at ridge point; possibility for different wind directions on different sides of the ridge. Ridges experience more wind. Fires gain speed and intensity moving toward a ridge. Fires burning at a ridge can exhibit erratic behavior. Strong air flows can cause fire to whirl. Wind crossing a ridge usually has a leeward eddy where the wind rolls around and comes up the leeward side. 

Saddle Potential for rapid rates of fire spread; fires pushed through saddles faster during upslope runs. Winds can increase when blowing through saddles due to the funneling effect of the constricted pass. On the other side, winds will slow, but erratic winds potentially occur at the saddle due to eddies.

The topographical features described above are shown in a terrain-view screenshot taken near the Plan Area. The top left half of the screenshot features a flat plateau area with various canyons, while flat area is prominent in the bottom right half. The Ridge shows a very steep slope from high elevation plateau to a flat area; the Saddle exhibits a much gentler slope. Box canyon exhibit a larger gap between its steep ridges, whereas the Narrow Canyon has a much smaller gap. The Wide Canyon example in this picture shows a much bigger gap in between its slopes, which have gentler slopes than that of the Saddle in this example.

Examples of these features near the Plan Area.

This map illustrates slopes within the plan area. Areas colored red are steeper slopes and areas colored green represent flatter areas.

Monterey Wildfire Protection Plan Methodology Map


Vegetation

Vegetation in the Plan Area is dominated by Monterey pine forest, one of three remaining native stands in California. Monterey pines often grow tall and straight and can reach heights of 100 feet at maturity (60-80 years). Associated vegetation with this forest type include Coast live oak, coastal scrub, and native and non-native grasses. Herbaceous and shrub vegetation is also present, either as dominant or understory vegetation.

Monterey Vegetation

The City of Monterey includes an extensive greenbelt dominated by Monterey pine and Coast live oak forests. Non-native herbaceous species including Rattlesnake grass and French broom are common throughout the city’s open space areas. Forest health varies throughout the greenbelt areas, and many collapsed pines and oaks are present. The largest areas of continuous natural vegetation include the Old Capitol Site, Skyline Forest, The Presidio of Monterey, La Mesa Village, and public parks including Iris Canyon and Don Dhavee Park. The city also borders extensive open spaces including the Del Monte Forest in Pebble Beach and Jacks Peak County Park.

Predominant Land Cover Monterey

This bar chart is color-coded to match the legend colors in the Vegetation Map. 80% of land is Developed (grey); 13% is Evergreen Forest (dark green); 3% is Coastal Shrub (sandy orange brown); 3% is Herbaceous (Yellow); and 1% is Barren (brown).

Pacific Grove

The City of Pacific Grove is largely urbanized and includes small patches of natural vegetation. George Washington Park in the central region of the city is the largest area of natural vegetation, at approximately 20 acres. The park is dominated by Coast live oak and Monterey Pine trees with a considerable annual grass understory. The city also includes the eastern portion of Rip Van Winkle open space, a densely forested open space park largely within Pebble Beach. The Del Monte forests exists adjacent to the city near the Del Monte Park community. 

Predominant Land Cover Pacific Grove

This bar chart is color-coded to match the legend colors in the Vegetation Map. 94% of land is Developed (grey); 3% is Evergreen Forest (dark green); 1% is Herbaceous (Yellow); and 1% is Barren (brown).

Carmel-by-the-Sea

Carmel-by-the-Sea is known for its Monterey cypress urban forest which covers the downtown and coastal areas of the city. Natural vegetation in the city is limited to Mission Trails Park, an approximately 34-acre open space park in the southeast region of the city. The park includes riparian areas, and pine and oak trees with grass and shrub understory. The northwest portion of the city is adjacent to Pescadero Canyon, which includes natural vegetation and steep slopes. 

Predominant Land Cover Carmel-by-the-Sea

This bar chart is color-coded to match the legend colors in the Vegetation Map. 94% of land is Developed (grey); 4% is Evergreen Forest (dark green); 2% is Herbaceous (Yellow); and 2% is Barren (brown).

Canopy Cover

Urban areas in the Plan Area are well known for their robust urban forests comprised of species such as Monterey cypress, Monterey Pine, and Coast live oak. Community members take pride in the aesthetics and health of large street trees which contribute to significant canopy cover in developed areas giving the region a unique forested feel. 

Fire Behavior Fuel Models

Fuel models identify the surface fuels present based on vegetation type and composition. Fuel models are utilized to model fire behavior based on vegetation characteristics across the landscape. Surface fuel models were mapped for the plan area using Scott and Burgan’s 2005 Standard Fire Behavior Fuel Models. 

Fuel model data was obtained from the LANDFIRE data distribution site and edited to account for errors and to reflect local fuel conditions based on professional recommendations and field assessments.


Typical fuel models observed in the Plan Area

Types of fuel models observed in the Plan Area, as shown in the Fire Behavior Fuel Models Map previously featured, are explained in this chart. NB1 - Urban / Developed: Consists of land covered by urban and suburban development. TL4 - Small downed logs. Primary fire carrier is moderate-load fine litter and coarse fuels; includes small-diameter downed logs. TL2 - Low load, broadleaf litter - Primary fire carrier is broadleaf (hardwood) litter. TL6 - Moderate load, broadleaf litter: Primary fire carrier is moderate-load broadleaf litter, less compact than TL2. GS2 - Moderate load, dry climate grass-shrub: Primary fire carrier is grass and shrubs combined. Shrubs are 1 to 3 feet high; grass is moderate. SH2 - Moderate load, dry climate shrub. Primary fire carrier is woody shrubs and shrub litter. Moderate fuel load, depth about 1 foot, and no grass fuel present. GR2 - Low load, dry climate grass: primary fire carrier is grass, though small amounts of fine dead fuel may be present. Load is greater than GR1, and the fuel bed may be more continuous. Shrubs, if present, do not affect fire behavior. TU4 - very high load, dry climate timber-shrub: primary fire carrier is heavy forest litter with a shrub or small tree understory. TL3 - Moderate load, conifer litter: Primary fire carrier is moderate-load conifer litter, light load of coarse fuels.


CAL FIRE Fire Hazard Severity Zones (FHSZ)

CAL FIRE’s FRAP database includes map data documenting areas of significant fire hazards in the state. These maps categorize geographic areas of the state into different fire hazard severity zones (FHSZs). The classifications include Moderate, High, and Very High FHSZs. CAL FIRE uses FHSZs to classify anticipated fire-related hazards for the entire state, and includes classifications for State Responsibility Areas, Local Responsibility Areas, and Federal Responsibility Areas. Fire hazard severity classifications consider vegetation, topography, weather, crown fire production, and ember production and movement.

CAL FIRE is currently in the process of updating the FHSZ map for SRA lands, with an updated LRA mapping effort to follow. The upcoming LRA mapping effort will include Moderate, High, and Very High wildfire hazard designations. You can learn more about CAL FIRE’s fire hazard severity zones  by visiting the CAL FIRE website deicated to descibing FHSZs,  including its history, the science and methodology for creating these zones, regulatory information, and the maps themselves.


Fire Regimes

Wildfire intensity, frequency, timing, and spatial patterns constitute the fire regime of a particular ecosystem. A fire regime outlines the historical role of wildfire in the landscape absent of modern human intervention but inclusive of indigenous burning.

The fire regime in the Plan Area and adjacent areas is largely comprised of Monterey pine forests and Oak woodlands in addition to limited areas of Chaparral, Coastal scrub, and grassland vegetation. Invasive and high-risk vegetation also occurs throughout the Plan Area. 

Monterey Pine Forest

Example Monterey pine forest fire regime

Oak Woodlands

Example of oak woodlands fire regime

Coastal Scrub

Example of coastal scrub fire regime

Grassland

Tall, brown, and dry grasslands are in full view in front and out toward the back of the view, which appears to be hill and features spread-out clusters of trees in the background. Behind this view is a mountain range shown with the colors of early sunset and dusk.

Example of grassland fire regime

Invasive French Broom

Example of invasive French Broom

Invasive Rattlesnake Grass

Example of Invasive Rattlesnake Grass


Wildland Urban Interface

The wildland urban interface (WUI) includes areas of urban and suburban development within the vicinity of wildland vegetation. The wildland fire risk associated with WUI areas includes propagation of fire via house-to-house fire spread, landscaping-to-house fire spread, or ember intrusion.

The CWPP process provides the opportunity for cities to define their own WUI areas. A regionally specific WUI map was created for the Plan Area to account for fine-scale features not captured in the statewide WUI database. Vegetation and urban development data used to create the WUI map was obtained from the National Land Cover Database and edited to account for local variations. The extent of the WUI was clipped to existing boundaries including community boundaries and major roadways.

Examples of WUI

This WUI example pic shows two houses perched at the top of a steep slope on the left, with tall trees and shrubs matching the height of the houses and some towering over. Vegetation and trees are flush up against both houses.
While this picture shows flat area, and trees here have a little more space in between them, a fence separates this area between trees and houses. The area with the houses also contains and has tall thin trees and tall vegetation scattered around.
This entrance to a property, which shows only a brown wooden or painted gate, shows a tall and dense stand of trees right behind it.

Monterey

  • 3,520 acres of WUI
  • 63% of City

Communities within the WUI

  • Presidio West
  • Skyline
  • Monterey Vista South
  • Monterey Vista North
  • Old Town South
  • Alta Mesa
  • Glenwood
  • La Mesa Village
  • Aquajito Oaks
  • Deer Flats North
  • Deer Flats South
  • Fisherman Flats
  • Cassanova Oak Knoll
  • Ryan Ranch West
  • Ryan Ranch East

Pacific Grove

  • 691 acres of WUI
  • 38% of City

Communities within the WUI

  • Pacific Grove Acres East
  • Pacific Grove Acres West
  • Asilomar Dunes
  • Sunset Drive
  • Fifth Addition West
  • Third Addition West
  • Second Addition
  • Forest Grove
  • Del Monte Park
  • Glen
  • Seaview

Carmel-by-the-Sea

  • 334 acres of WUI
  • 49% of City

Communities within the WUI

  • Southeast
  • Northeast
  • Northwest

Building Density

Building density influences community wildfire risk in multiple ways. In the Wildland Urban Interface, structure ignitions are more likely in areas of low to intermediate building based on the presence of flammable vegetation between structures. However, house to house fire spread is more likely in areas with high building density due to the proximity of structures. In these dense areas, flames, radiant heat, and embers facilitate fire moving from one structure to the next. This can lead to a more extensive fire incident referred to as an urban conflagration. The potential for house-to-house fire spread in densely developed communities is strongly influenced by the materials and techniques used in building construction. For example, houses constructed with wooden materials that have large vents and single pane windows are more easily ignited compared to those constructed with ignition-resistant materials (as identified in Chapter 7A of the California Building Code).

Depending on community layout and design, building density can also hinder access for firefighting vehicles and personnel. Narrow streets, limited parking, and congested areas within high-density communities limit the ability for fire agency access, making it difficult for fire suppression equipment to reach impacted areas. Additionally, areas of high building density can present challenges for evacuation, as large numbers of people may need to exit simultaneously, potentially congesting roadways and slowing overall evacuation progress.

Fire History

Fire history is an important component in understanding fire frequency, fire type, significant ignition sources, and vulnerable areas. The topography, vegetation, and climatic conditions associated with the Plan Area combine to create a unique situation capable of supporting large-scale, high-intensity, and sometimes damaging wildfires, such as the 1987 Morse Fire.

Monterey County has experienced multiple large wildfires in the past decade including the 2020 River Fire, 2022 Colorado Fire, and the 2016 Soberanes Fire.

A tall and rising smoke plume towers above the hills and into the sky, with wispier smoke clouds in front of it. The area in immediate view appears to have been previously dried and burned, as indicated by the scorched trees with browned leaves or leafless trees.

Soberanes Fire

Wildfire suppression, human development patterns, and the absence of indigenous burning practices have led to limited fire history within the Plan Area. According to CAL FIRE’s Fire History Database which includes timber fires 10 acres or greater and brush fires 30 acres or greater, no wildfires meeting these criteria have occurred within the Plan Area. However, the Morse Fire in 1987 burned up to the Monterey City Limits after burning 190 acres in Pebble Beach and destroying 36 homes.  Additional details about the 1987 Morse Fire in Pebble Beach are written in the United States Fire Administration's Technical Report Series.  Additionally, an unnamed wildfire occurred within the Plan Area near the Huckelberry Hill Nature Preserve in 1990 after igniting along Highway 68.

Historical wildfire data within the Plan Area is limited. However, small wildfires have occurred but have been quickly extinguished. Wildfire ignition points since 2019 are shown in the interactive map.

The Aguajito Fire occurred on October 3, 2020 on the western slope of Aguajito Road between Gentry Road and Mulholland Drive after a vehicle struck a utility pole igniting nearby vegetation. The fire was held at less than 6 acres and no structures were damaged.

Smoke makes up most of the background of this picture, with burnt-brown shrubs and a few burned trees shown outside of the smoke.

Aguajito Fire (source: Monterey Herald)


Wildfire Hazard and Risk Assessment

Hazard vs Risk

A Quantitative Wildfire Risk Assessment (QWRA) was conducted for the Plan Area using the Interagency Fuel Treatment Decision Support System (IFTDSS). The QWRA was conducted in two basic stages: the first stage modeled wildfire hazard and the second stage modeled wildfire risk. For a detailed write up of the QWRA methodology,  review Section 1.1 (Wildfire Hazard Assessment) and Section 1.2 (Wildfire Risk Assessment) of Appendix A of the CWPP. 

In this map, the wildfire hazard areas are shown in orange: the Rip Van Winkle Open Space, Huckleberry Hill Nature Preserve, and SFB Morse Botanical Preserve, along with other notable strands of vegetation not associated with those spaces. The wildfire risk areas are shown in green, and appear as the built environment surrounding, outside, and within proximity to these wildfire hazard areas. Definitions of "wildfire hazard" and "wildfire risk" are provided below the map / alternative text section.

Wildfire Hazard vs. Risk Areas

Wildfire hazard represents the existing wildfire environment and potential wildfire behavior. Wildfire risk is the intersection of wildfire hazard, identified assets and high-valued resources, and the resulting potential impact on those assets and resources. The model results can be used to identify and prioritize projects intended to reduce wildfire risk.

Wildfire Hazard Results

Wildfire hazard in the Plan Area was modelled under two different weather scenarios: average (50th percentile) and peak (97th percentile) weather conditions. Average weather conditions represent typical summer onshore conditions, whereas peak weather conditions represent reflecting extremely low fuel moisture and very high wind speeds associated with Santa Lucia conditions. Peak weather conditions are intended to represent the predicted worst case wildfire behavior in the Plan Area.

Flame Length Flame lengths correspond to wildfire intensity and identify the capacity for fire suppression efforts. As flame lengths increase, the capacity to suppress wildfire is limited and threats to firefighters increase. Swipe the map below to show differences in flame length during average (left) and peak weather conditions (right).


How Flame Length Corresponds to Suppression Capabilities


Rate of Spread

Wildfire rate of spread describes the speed of the flaming front. Terrain, fuels, and weather combine to influence wildfire spread rates. The rate of spread is measured in meters per minute (m/min) and is defined as the speed with which the fire is moving away from its origin. Swipe the map to the right to show differences in wildfire spread during average (left) and peak weather conditions (right).

Crown Fire Potential

Crown fire is a form of extreme wildfire behavior and occurs when wildfire passes into the tree canopy. Crown fires are the most difficult form of wildfire to control due to long flame lengths and rapid rates of spread.  Crown fires can be facilitated by “ladder fuels”, which consist of live or dead vegetation that facilitates the spread of fire from surface fuels into the tree canopy. Crown fires can be generally described through the following classifications. The map to the right shows crown fire activity during peak weather conditions.

Passive Crown Fire: A crown fire in which individual or small groups of trees torch out, but solid flaming in the canopy cannot be maintained except for short periods. Passive crown fire encompasses a wide range of crown fire behavior from the occasional torching of an isolated tree to a nearly active crown fire. Also called torching (Scott and Reinhardt 2001).

Active Crown Fire: A crown fire in which the entire fuel complex becomes involved, but the crowning phase remains dependent on heat released from the surface fuels for continued spread. Also called running and continuous crown fire (Scott and Reinhardt 2001).

Independent Crown Fire: A crown fire that spreads without the aid of a supporting surface fire (Scott and Reinhardt 2001).

Three small graphics are shown to display the progression of Crown Fire stages. 1) Passive (torching): fire on the ground is shown climbing up the bottom and middle portion of a tree, with smoke coming up. An unburned tree is to the right of this tree-on-fire. 2) Active (dependent): fire on the ground is burning through the lower canopies of a few trees crowded together and climbing up all of them. The surface fire helps to provide heat and help crown fires spread. 3) Independent (very rare): fire has completely torcher one tree and spread onto neighboring trees that are crowded nearby, but surface fuel is not present.

Stages of Crown Fire

This two part graphic shows different factors that affect ember lofting (top portion of graphic) and ember distance (bottom portion of graphic). Five clusters of trees are shown in separate small squares, both on the top (for ember lofting) and bottom (for ember distance). The first of these tree clusters is on fire, and squiggly arrows moving to the right are shown to represent wind. Wind carries small and various shaped size circles to represent ember. Ember lofting factors noted in the top graphic include the following: fire intensity, terrain / slope, fuel type, tree height / species / size, and tree canopy density. Ember distance factors noted in the bottom graphic are affected by wind speed / direction, ember size, and tree height.

Factors Affecting Spotting

Ember Exposure

Another component of fire behavior is spotting, the transfer of fire brands (embers) ahead of a fire front, which can ignite smaller vegetation fires (SKCNP 2017). These smaller fires can burn independently or merge with the main fire. Spotting can also result in structural ignitions when transported embers reach a receptive fuel bed (e.g., combustible roofing), especially in wind-driven fires. Structure fires as well as vegetation-fueled fires can generate fire brands. Additionally, landscape features like ridges can dramatically affect fire behavior by influencing wind patterns, funneling air, and increasing wind speeds, thereby intensifying fire behavior and the likelihood for spotting. The map to the right shows ember spotting density during peak weather conditions. Areas of higher spotting density are associated with greater ember exposure.

Quantitative Wildfire Risk Assessment (QWRA)

Following the hazard assessment, a Quantitative Wildfire Risk Assessment (QWRA) was conducted to evaluate wildfire risk to communities in the plan area. The QWRA was modelled assuming peak weather conditions. A QWRA characterizes the predicted benefits and threats from a wildfire on values across a landscape. Results from a QWRA can be used to identify and prioritize potential vegetation treatment areas.

The QWRA considers both the threats and benefits of wildfire. Some resources may benefit from fire (e.g., fire-dependent plant species and landscapes that have departed from the historical fire regime) and others may be threatened by fire (e.g., communities). The QWRA first looks at the level of exposure of the high-value resources and assets (HVRAs) to wildfire across the analysis area. The analysis then calculates the likelihood of a fire occurring and the potential intensity of a fire to the susceptibility of the HVRA to determine risk. Areas likely to experience high intensity wildfires in close proximity to communities are assigned negative scores to reflect their negative impacts on communities.

This map shows the Expected Net Value Change (EwNVC) to communities.

Areas likely to experience high intensity wildfires in close proximity to communities are assigned negative scores to reflect their negative impacts on communities.

EwNVC analyzes the likelihood of a fire occurring and the effect on HVRAs. The expected weighted value is a product of the CwNVC and burn probability. It determines the risk to the HVRA by intersecting the wildfire hazard with the likelihood of occurrence and the potential impact on the HVRA. EwNVC is used for planning scenarios where the likelihood of a fire occurring needs to be considered (as opposed to CwNVC, which assumes a fire will occur).

This map shows the Conditional Net Value Change (CnNVC) to communities.

Conditional Net Value Change quantifies impacts to HVRAs assuming a wildfire will or has occurred.

CnNVC is a product of fire intensity, susceptibility, and importance. It highlights the likely effects of fire on HVRAs, with the assumption that a fire will or has occurred. CwNVC aids in planning scenarios where the presence of fire is assumed, and the goal is to understand the anticipated threats and benefits from a fire.


Community Relative Wildfire Risk Ranking

A Community Relative Risk Ranking was conducted for the Plan Area to identify high risk communities where wildfire risk mitigation should be prioritized. This assessment also aims to enhance resident awareness of the relative risks associated with their community. The evaluation of community wildfire risk involved quantifying key variables within the designated community areas, including:

Community Proximity to High Hazard Vegetation To evaluate the proximity of a community to hazardous vegetation, we determined the percentage of the community and its immediate surroundings that were categorized as having a Higher or Highest threat level. Higher and Highest threat areas were based on the outputs from the Conditional Weighted Net Value Change analysis discussed previously.

Dominant Vegetation Type The dominant vegetation type within the community’s immediate vicinity was quantified to account for the potential for severe wildfire behavior. Vegetation types listed from most to least hazardous include Timber, Shrub, Herbaceous, and Urban.

Potential Ember Exposure The assessment of community ember exposure involved determining the proportionate area within the community that was estimated to be affected by airborne embers. This also took into consideration the severity of airborne embers as indicated by the total count of projected embers.

Terrain Steep slopes are likely to exacerbate wildfire behavior and facilitate accelerated rates of fire spread through communities.  Terrain was quantified by determining the average slope of development areas and the immediately adjacent terrain.

Urban Vegetation Urban vegetation can contribute to the transmission of wildfires from natural vegetation to developed regions. During intense wildfires, embers that land in urban vegetation can result in additional fire outbreaks within communities, even if they are located a significant distance away from the primary fire front.

Emergency Response Time The assessment of the time required for emergency responders to reach the community relied on a prior study conducted by Citygate Associates in 2022. This study identified specific regions where the expected emergency response time exceeded 4 minutes. Those areas located beyond the 4-minute response threshold were assigned a higher risk score.

Road Network Rank The road network ranking evaluates characteristics of community roads that impact the ability of emergency personnel to enter and exit the community, as well as the capacity for community evacuation. Essential road features considered in this assessment include road width, the presence or absence of dead-end roads, and whether the community has one or multiple access points.

Each variable was assigned a relative weighting to account for its influence on community wildfire risk. For a more detailed description of the Community Relative Risk Ranking approach, click  review Section 2 (Community Relative Risk Ranking Assessment) of Appendix A of the CWPP. 


Action Plan

The goal of this CWPP is to identify priority projects and action items that can be implemented to serve and protect lives, property, critical infrastructure, and Plan Area resources threatened by wildland fire. The Monterey Fire Department recognizes the potential for severe and damaging wildfires within the Monterey Peninsula. This CWPP is intended to reduce wildfire hazards and risk through implementation of the action items outlined in the Action Plan.  Section 3 of the CWPP (the Action Plan) details recommended actions and projects to be implemented in the Plan Area that would minimize wildfire impacts to the community.  

Community Relative Risk Ranking


Priority Wildfire Risk Mitigation Projects

Existing Projects: The map below displays existing vegetation management programs within the Plan Area. Click on the map features to learn more about these programs.

Priority Projects: The map below displays priority projects that are included as action items of this CWPP. Click on the map features to learn more. To view the complete list of projects including those not featured on the map,  refer to Table D-1 (Priority Vegetation Management Projects) within Appendix D (Prioritized Vegetation Management Projects. )

Existing Projects

Proposed Priority Projects


Community Resources

Creating Defensible Space


Defensible Space Zones

Click the Zone buttons below to learn more about defensible space measures you can take to protect your property.


Minimum Horizontal and Vertical Clearance


Structural Hardening


Built Environment

From left to right shows a stack a firewood, a propane tank, and a large lengthwise two story house. Text bubbles notate how to deal with individual components of the house, propane tank, and firewood in a way that would help with reducing fire risk around the home. For firewood, stacks should be kept at least 30 feet away from the house on the uphill side if possible. Propane Tanks should be kept at least 30 feet away from the house. For roofs, homes with wood-shake shingle roots are much more likely to be destroyed during a wildfire than homes with fire resistant. Consider replacing wood shake or shingle roofs with Class-A fire resistance type (composition, metal or tile). Rain gutters: gutters can trap flying embers. Always keep rain gutters free of leaves, needles, and other debris. Check and clean them several times a year. Decks: decking materials are often combustible. All decking material should be kept in good condition. Combustible debris such as pine needles, twigs, and leaves should be removed and kept from gaps between deck boards. Deck enclosure: where possible, enclose the base of decks with a non-combustible material. Do not store items underneath decks. Wood siding: wood products (boards, panels, and shingles) are common siding materials. However, they are combustible and not a good choice for homes in fire prone areas. Stucco, brick, cement board, and steel are better non-combustible siding choices. If using non-combustible siding is not feasible, keep siding in good condition. Windows: Single pane and large windows are the most vulnerable. Install windows that are double-paned and utilize tempered glass on the exterior pane.

Source:  West Region Wildfire Council | Working together to reduce wildfire risk (cowildfire.org) 


Evacuation and Emergency Preparedness


Interactive Map

We invite you to use this map to browse the various datasets used in developing the Community Wildfire Protection Plan. The buttons in the upper-right corner of the map allow you to control the visibility of layers, as well as change the base layer of the map. Use the controls in the upper-left corner to change the extent of the map, as well as search for addresses or communities with the Plan Area.

Different buttons are shown with arrow labels of text defining what each button does for interacting in the interactive web app. The plus (+) and minus (-) buttons change the zoom level of the map. The home button resets the map extent to the default, which overlooks all of the Plan Area (Monterey, Pacific Grove, and Carmel-by-the-Sea). A search bow allows users to search for an address or place and show its location on the map. A button showing a "list of items" (triangle on top, square in middle, and circle on bottom) allows the user to change legend visibility. A button showing stacked squared allows the user to change the visibility of layers (toggle different layers on and off). A button showing four small squares alongside each other to resemble a square allows the user to change the basemap.

Interactive map instructions

Community Wildfire Protection Plan Interactive Web App


Monterey, Carmel-by-the-Sea, and Pacific Grove CWPP

Click image below for a  downloadable PDF  of the Monterey, Carmel-by-the-Sea and Pacific Grove CWPP.

Logos for Monterey Fire Department, City of Monterey, City of Pacific Grove, and City of Carmel-by-the-Sea.

Monterey Fire Department and Air Operations responding to a fire in Carmel Valley.

Monterey Fire Department responding to a fire in Carmel Valley.

Smoky skies above Monterey City Hall

Fire Behavior Triangle Diagram

Fog over Monterey Pine Forest

Examples of these features near the Plan Area.

Example of grassland fire regime

Wildfire Hazard vs. Risk Areas

Interactive map instructions

Soberanes Fire

Aguajito Fire (source: Monterey Herald)

Stages of Crown Fire

Factors Affecting Spotting