
Community Wildfire Protection Plan
For the cities of Monterey, Carmel-by-the-Sea, and Pacific Grove
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
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.
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.
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.
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
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.
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.
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.
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.
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
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
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
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
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
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
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.
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.
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.
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).
Stages of Crown Fire
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
- Home Hardening | CAL FIRE
- Wildfire Home Retrofit Guide (readyforwildfire.org)
- Low-Cost Retrofit List ( low-cost-retrofit-list-update-2_17_22.pdf (ca.gov) )
- Home Hardening | National Fire Protection Association ( FirewiseHowToPrepareYourHomeForWildfires.ashx (nfpa.org)
Built Environment
Evacuation and Emergency Preparedness
- Go! Evacuation Guide - Ready for Wildfire
- Create Your Go Bag - Ready for Wildfire
- Evacuation Steps - Ready for Wildfire
- Evacuation Guide | Monterey County, CA
- Sign up for Alerts | Monterey County, CA
- Family Communication Plan (firesafemonterey.org)
- GO! Evacuation (firesafemonterey.org)
- Peninsula Region Evacuation Guide, 637680098811670000 (monterey.ca.us)
- City of Monterey, CA (Community Emergency Response Team (CERT)
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.
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.