HomeMy WebLinkAbout15. ScreencheckFEIR36Hazardous 3.6 HAZARDS AND HAZARDOUS MATERIALS
Avila Ranch Development Project 3.6-1
Final EIR
3.6 HAZARDS AND HAZARDOUS MATERIALS
This section of the Environmental Impact Report (EIR) describes the existing conditions
related to hazards and hazardous materials in the vicinity of the Project site and analyzes
the potential for hazards and hazardous materials impacts to occur as a result of
implementation of the Avila Ranch Development Project (Project), as well as airport-
related hazards. Any land use conflicts with Airport Land Use Plan (ALUP) Safety Areas
or the Airport Overlay Zones (AOZs) of the City of San Luis Obispo’s (City) are further
discussed in Section 3.8, Land Use and Planning.
Hazards may include exposure to both natural and man-made hazards. These could include
hazards associated with aircraft operations at the nearby San Luis Obispo County Regional
Airport (Airport) or natural hazards such as wildfires. Hazardous materials are defined as
substances with physical and chemical properties of ignitability, corrosivity, reactivity, or
toxicity, which may pose a threat to human health or the environment. To clarify, the term
“hazardous materials” is used in this section to generally describe chemical materials, such
as petroleum products, solvents, pesticides, herbicides, paints, metals, asbestos, and other
regulated chemical materials. Additionally, the term “release” as used in this section
includes known historical spills, leaks, illegal dumping, or other methods of release of
hazardous materials to soil, sediment, groundwater, or surface water. If a historical release
exists, then there is a risk associated with disturbing the historical release area. Potential
future releases of hazardous materials that could occur during construction or operation of
the Project facilities also are included in the analysis.
Information for this section was gathered from Environmental Site Assessments (ESAs)
and EIRs prepared for adjacent properties such as the Chevron Tank Farm property,
information provided by the City’s General Plan Safety Element, Airport Specific Plan
(AASP), ALUP, and Project site information on file with the City. Additionally, site-
specific hazardous materials information was provided in a Preliminary Site Assessment
(PSA) and Phase II Addendum for the Avila Ranch Property, and soil engineering studies
prepared for the Project site (Grisanti & Associates 2011; GeoSolutions, Inc. 2015a; see
Appendix L).
3.6.1 LUCE Update EIR
The 2014 Land Use and Circulation Elements (LUCE) Update EIR previously analyzed
hazards and hazardous materials impacts related to adoption and implementation of the
2014 LUCE. The LUCE Update EIR identified potentially significant impacts to hazards
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associated with potential future development of the Project site due to the potential for
airport land use incompatibility and introduction of residential uses to high wildland fire
hazards; however, the EIR concluded that implementation of the existing General Plan
policies, would reduce impacts to a less than significant level. In particular, LUCE
Chapter 7, Airport Areas policies were found to mitigate potential impacts (City of San
Luis Obispo 2014).
3.6.2 Environmental Setting
The Project site is located in the southern area of the City within a region that transitions
from urban industrial to agriculture and rural development. Industrial uses lie to the north
and northwest of the Project site, while agricultural uses are adjacent to the south and
southeast within unincorporated County areas. The nearest schools to the Project site are
located over 2 miles away. The Airport is approximately 0.6 mile east of the Project site.
The Chevron Tank Farm property lies to the northeast of the Project site and is a location
of previous releases of hazardous materials, most notably the release of petroleum that
resulted from the Unocal Tank Farm fire of 1926. This is discussed in detail below.
The Project site has been in long-term agricultural use and is largely undeveloped. The
onsite agricultural operations involve the routine use and handling of hazardous materials
such as fertilizers, pesticides, and herbicides. Historical aerials indicate that the site was
developed with a ranch-style farm house and agricultural accessory structures near the
center of the Project site. These structures have since been demolished.
3.6.2.1 Wildfire Risk
In central California, the fire season
usually extends for approximately five to
six months, from late spring to fall, or
roughly May through October. The
duration of the fire season is influenced by
a combination of climatic, vegetative, and
physiographic conditions; rainfall totals,
distribution and/or drought conditions
may affect the duration of this period.
Structural losses or damage from
wildfires can be caused directly due to
wildland fires, but also often result from
The Project site is within a Moderate Wildland Fire
Hazard Zone and contains open grasslands and
riparian vegetation that present moderate wildfire
hazards.
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inappropriate siting of structures, use of inappropriate construction materials, flammable
ornamental landscaping, and accessory structures.
Wildfire hazard zones are assessed by the California Department of Forestry and Fire
Protection (CALFIRE) based on the presence of fire-prone vegetation, climate, topography,
assets at risk (e.g., high population centers), and a fire protection agency’s ability to provide
service to the area. The Project site is designated as a Moderate Wildland Fire Hazard Zone
(CALFIRE 2007). As the Project is located at the edge of a rural area, it has potential to be
exposed to wildfire hazards. Within the Project vicinity, vegetation such as open grasslands
on and adjacent to the site and riparian vegetation such as that along Tank Farm Creek, can
quickly burn during the dry fire season, particularly under strong wind conditions.
3.6.2.2 Hazardous Materials
Potential for Hazardous Materials on the Project Site
The Project site supports existing agricultural operations and is adjacent to active
agricultural operations to the south and east. Typical hazardous materials in use on
agricultural lands include lubricants, fuels, fertilizers, and pesticides. Production and
storage of these chemicals can pose potential hazards where leaks can contaminate air,
water, and soil, or generate fire. Areas on agricultural lands that are of particular concern
for these hazardous materials are farming headquarters or staging areas in which operations
are conducted and where hazardous materials or equipment might have been stored. At the
Project site, the PSA inspection of the location of the previous farm headquarters area
showed no evidence of storage or use of hazardous materials. Further, inspection of the
other possible staging areas showed no visual evidence of pesticides, fuels or other
hazardous substance releases or spills (Grisanti & Associates 2011).
However, as a result of historical agricultural operations within the Project site, there is
potential for pesticides and herbicides to be present in low concentrations near the soil
surface. These chemicals are not usually regulated by government agencies and the PSA
indicates there is little risk associated with residual presence of pesticides in site soils
(Grisanti & Associates 2011). During the PSA survey, inspection of the Project site
revealed minimal presence of some non-hazardous solid waste from residual homeless
campsites adjacent to Tank Farm Creek, in addition to a small pile of refuse near where a
former windmill once stood (Grisanti & Associates 2011).
Additionally, a reuse dump associated with an old farm house from the early 1900s was
located onsite during inspections in 2011. The PSA notes the most significant waste from
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the old farm house includes some plaster and some asphalt shingle roofing. The old farm
house refuse onsite may have contained asbestos containing materials (ACM). Based on
the age of the building, there is a potential for building materials to have contained ACM
or lead-based paint (LBP). When ACM or LBP are disturbed during renovation or
demolition activities, there is a potential to release these hazardous materials, which can be
harmful to human health. Two empty 5-gallon containers were also found during the PSA,
one of which might have contained a lubricant or some other agricultural chemical. Both
containers were deemed free of any previous residual chemicals and could be disposed as
non-hazardous waste (Grisanti & Associates 2011). According to the PSA, what waste was
present does not pose a significant disposal liability. The PSA also notes that Mr. Avila has
already arranged provisions for the cleanup of the farm house waste (Grisanti & Associates
2011). During site inspections conducted by Amec Foster Wheeler in 2016, this refuse had
appeared to be removed.
Radon is considered to have a moderate risk in some geologic formations and soils in San
Luis Obispo County. Within the region, only 3 of 173 tests for radon in homes contain over
4pCi/L, ‘the highest’ rating. The PSA indicates there is little risks associated with presence
of radon within the Project site (Grisanti & Associates 2011).
The PSA also noted the presence of a transformer on one of the Pacific Gas and Electric
Company (PG&E) power poles that run along the north-central property line that could
possibly contain polychlorinated biphenyls (PCBs). As indicated by the PSA, the PG&E
transformer is not expected to contain PCBs as PG&E discontinued use of PCBs in
transformers in the 1980s (Grisanti & Associates 2011).
Hazardous Materials Site Listings
No evidence of aboveground storage tanks (ASTs) or underground storage tanks (USTs)
is known to occur within the Project site. In addition to the lack of ASTs and USTs, the
Project site is not currently or has not historically been associated with any bulk fuel storage
or fixed dispensing equipment (Grisanti & Associates 2011; Department of Toxic
Substances Control [DTSC] 2016).
However, records indicate that several permitted USTs, inactive Leaking Underground
Storage Tanks (LUSTs) and Cleanup Program sites are located within 0.5 mile of the
Project site (see Table 3.6-1; DTSC 2016). There are five active cleanup sites that were
identified within 0.5 mile of the site; three within the Chevron Tank Farm property to the
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Table 3.6-1. USTs and Cleanup Sites within a 0.5 mile-Radius of the Project Site
Hazardous Site Record Location Potential for Migration to the
Project site
PG&E Permitted UST Vachell Lane, 1,100 feet
east of Project site
Very Low – Listed site does not
indicate release of hazardous
materials.
Pacific Bell Permitted UST Tank Farm Road, 0.5 mile
north of the Project site
Very Low – Listed site does not
indicate release of hazardous
materials.
Pacific Bell Inactive LUST
Inactive Cleanup site
Suburban Road, 0.3 mile
north of the Project site
Very Low – Two inactive cleanup
sites included a release of diesel and
gasoline in 1995 and 2003 that
potentially affected groundwater
supplies. Cleanup was completed in
2004. Given its inactive status,
potential contamination of the Project
site is very low.
Chevron Tank Farm Cleanup
Program Site
Tank Farm Road, 100 feet
north of the Project site
Low – Active cleanup site since 1998
for crude oil, petroleum, arsenic, lead,
and asphalt that contaminated
groundwater, soils, and surface water.
Groundwater monitoring conducted
since 1998 indicates that
contamination is limited to a plume
contained within the site. The site is
part of Chevron Tank Farm property
remediation activities.
Unocal Pipeline Cleanup
Program Site
Tank Farm Road, 0.5 mile
north of the Project site
Low – Active cleanup site since 1991.
Crude oil from the pipeline
potentially contaminated groundwater
supply. The site is part of a
groundwater monitoring program.
San Luis Truck Service Garage
LUST
Tank Farm Road, 0.5 mile
north of the Project site
Low – Groundwater and soil
contamination from release of
solvents and gasoline. The site is part
of a groundwater monitoring
program.
Unocal Pipeline Inactive
Cleanup Program Site
South Higuera Street, 883
feet west of the Project site
Very Low – Soil and groundwater
was contaminated with non-petroleum
hydrocarbons in 1998. Groundwater
monitoring was performed between
2004 and 2015 and indicates that
contamination is confined within an
area along South Higuera Street.
Chevron developed a soil and
groundwater management plan.
San Luis Obispo
Perchloroethylene (PCE) Plume
DTSC Cleanup Site
Los Osos Valley Road, 0.5
mile northwest of the
Project site
Low – Active cleanup site since 2010.
Groundwater was potentially
impacted by tetrachloroethylene from
the site’s previous dry-cleaning use.
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Table 3.6-1. USTs and Cleanup Sites within a 0.5 mile-Radius of the Project Site
(Continued)
Hazardous Site Record Location Potential for Migration to the
Project site
Los Osos Valley Road Cleanup
Site
Los Osos Valley Road, 0.5
mile northwest of the
Project site
Low – Active cleanup site since 2010.
Soils were contaminated with crude
oil, diesel and gasoline. Due to the
distance and potential for soil to
migrate, potential for migration to the
Project site is low.
Source: DTSC 2016; Grisanti & & Associates 2011.
north, and two along Los Osos Valley Road to the northwest. These sites are undergoing
remediation for contaminants that affected soils, groundwater, and surface water. Records
indicate these sites are undergoing groundwater monitoring and soil sampling programs
and contamination has been isolated to the sites.
These offsite cleanup sites located near the Project site or hydraulically up-gradient could
be a concern if contaminants migrate to the Project site. Given the location of the sites and
soil and groundwater affected, there is a low potential for migration of contaminates to the
Project site, in particular, to groundwater resources (Grisanti & Associates 2011). This is
further described below.
The 1926 Unocal Fire and Potential for Total Petroleum Hydrocarbons
The largest historical hazardous materials release in the Project vicinity occurred during
the 1926 Unocal Tank Farm fire. After a lightning strike hit the facility, it caused a massive
fire resulting in the burning and release of an estimated 6 million barrels of oil (Applied
EarthWorks, Inc. 2015). Hot crude oil was estimated to have flowed over the northern part
of the Project site. According to the PSA, the majority of residue from the spill was
removed by the family owner/operators and disposed offsite soon after the spill; however,
during PSA sampling, total petroleum hydrocarbons (TPH) remnant from the 1926 fire was
recovered in soils in the northeastern portion of the Project site near its boundary with the
Chevron Tank Farm property. Relatively shortly after the release, historical aerials indicate
the Project site remained in active agricultural use by the Avila family from 1939 to 2006.
Since the spill, numerous studies have been conducted on the Chevron Tank Farm property
and results conclude that contamination appears to remain contained on the Chevron Tank
Farm property (Grisanti & Associates 2011).
Testing for the PSA indicated that groundwater and soil samples showed relatively minor
amounts of heavy petroleum hydrocarbons still exist in the northeast corner of the Project
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site, directly south of the common border of the Chevron Tank Farm property. The levels
of which TPH are detected are in smaller concentrations the farther the distance to the
Chevron Tank Farm property. Collected samples registered TPH as high as 220 parts per
million (ppm) and low as 41 ppm. The PSA indicated the hydrocarbon presence does not
pose any significant health or environmental concerns (Grisanti & Associates 2011).
Naturally Occurring Asbestos
The Buckley Road Extension Soils Engineering Report suggests that naturally occurring
asbestos (NOA) could occur within the serpentine rock found during field exploration of
the Buckley Road Extension site, but the quantity is less than one acre (GeoSolutions, Inc.
2015). The existing structures within the Buckley Road Extension site may also contain
ACMs.
3.6.2.3 Airport Safety Hazards
The Project site is approximately 0.6 mile west of the Airport and falls within the
jurisdiction of both the ALUP adopted by the Airport Land Use Commission’s (ALUC) in
1973 and updated in 2005, as well as the City’s AOZs addressed in Chapter 7 of the City’s
2014 LUCE Update, regarding airport safety issues.1 Both documents put forth standards
for development intensity within airport safety zones, and identify potential airport safety
hazards using similar, but different criteria governing allowable types and intensity of
future development and the location of safety zones based on differences in mapping. The
County ALUC oversees development subject to the ALUP to ensure safety, while the City
has ultimate jurisdiction over potential land use decisions and future development. This
section briefly describes the operations at the Airport and associated physical safety
hazards associated with the Project site in terms of both the ALUP and LUCE safety
standards. A more detailed description of the standards for allowable development intensity
within the ALUP Safety Areas and LUCE AOZs, along with associated land use impacts
are described in Section 3.8, Land Use and Planning.
San Luis Obispo County Regional Airport
The Airport provides commuter, charter, and private aviation service to the area. The
primary hazard associated with land uses near the Airport is the risk of aircraft incidents
on approach and takeoff. Aircraft flight operations are determined largely by the physical
1 As noted in Section 3.8, Land Use and Planning, the ALUP is currently undergoing an update which is
expected to be completed in 2017.
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layout of the Airport and rules of the Federal Aviation Administration (FAA) (City of San
Luis Obispo 2014). The Airport has had a mix of commercial airline service and general
aviation operations for most of its history. At the time of the SBP Master Plan Update
(adopted in 2005), business aviation accounted for approximately 5 percent of general
aviation operations, with the majority of general aviation operations being flight training
and leisure flying. The split of general aviation operations at the Airport averaged 60
percent itinerant and 40 percent local, and military operations accounted for less than 1
percent of total operations. Enplaned air cargo at the Airport was growing at an average
annual rate of 2.4 percent (Johnson Aviation 2014). In 2015, the split of general aviation
operations averaged 66 percent itinerant and 34 percent local, with military operations
accounting for less than 1 percent of total operations (San Luis Obispo County Regional
Airport 2015).
Figure 3.6-1 San Luis Obispo County Regional Airport
There are two runways at the Airport (see Figure 3.6-1). Runway 11-29 is utilized for the
majority of aircraft operations, with 97 percent of all aircraft operating at the Airport using
this runway for departures and arrivals, as well as touch-and-go flights. Runway 7-25 is
mostly used by small, light, general aviation aircrafts during crosswind conditions and is
utilized for the remaining 3 percent of aircraft flights, only for General Aviation propeller
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aircraft.2 Both runways have parallel taxiways (Johnson Aviation 2014). The Project site
is located in the path of the arrival/departure pattern for Runway 7-25, the runway with the
lowest level of use.
Aviation Accidents at San Luis Obispo County Regional Airport
According to the California Airport Land Use Planning Handbook Accident Study, 68
percent of aviation accidents occur over or within an airport, and accident sites tend to
occur fairly close to the extended runway centerline (Johnson Aviation 2014). There had
been a total of 33 aviation accidents or incidents associated with the Airport, six of which
resulted in fatalities, between 1984 and 2014. Of these, five incidents resulting in
emergency landings within LUCE-defined AOZs between 1984 and 2014, none of which
resulted in an on-ground fatality or occurred within or adjacent to the Project site (see Table
3.6-2).
Table 3.6-2. Fatal Aircraft Accidents within the Vicinity of San Luis Obispo
County Regional Airport
Approximate Location of Crash Site within AOZ and/or ALUP Safety Areas
Flight Date AOZ area ALUP Safety Area
9/24/1990 n/a S-2
8/7/1994 AOZ-4 S-1B
1/16/2001 AOZ-6 S-1C
8/1/2005 AOZ-6 S-2
6/24/2013 AOZ-2 S-1B
Source: Johnson Aviation 2014.
Note: Accident site placement for repsective AOZ and ALUP Safety Areas were based on visual determination of
Figure 4-3 from the Johnson Aviation Land Use Compatibility Report.
3.6.3 Regulatory Setting
3.6.3.1 Federal
Comprehensive Environmental Response, Compensation, and Liability Act (1980)
The Comprehensive Environmental Response, Compensation, and Liability Act
(CERCLA) addresses procedures to identify and cleanup sites contaminated by
unauthorized releases of hazardous materials. Commonly known as Superfund, CERCLA
was enacted by Congress on December 11, 1980. This law created a tax on the chemical
and petroleum industries and provided broad federal authority to respond directly to
2 General aviation is all civil aviation operations other than scheduled air services and non-scheduled air
transport operations for remuneration or hire.
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releases or threatened releases of hazardous substances that may endanger public health or
the environment. Superfund sets priorities for cleanup in the National Oil and Hazardous
Substances Pollution Contingency Plan (National Contingency Plan). The National
Contingency Plan includes lists of abandoned and uncontrolled hazardous waste sites,
which the Environmental Protection Agency (EPA) updates annually.
Under CERCLA, owners and operators of real estate where there is hazardous substance
contamination may be held strictly liable for the costs of cleaning up contamination found
on their property. No evidence linking the owner/operator with the placement of the
hazardous substances on the property is required.
Clean Water Act (1977)
The Clean Water Act governs the control of water pollution in the U.S. This Act
implements the National Pollutant Discharge Elimination System (NPDES) program,
which requires that permits be obtained for point discharges of wastewater. This Act also
requires that storm water discharges be permitted, monitored, and controlled for various
entities.
The Central Coast Regional Water Quality Control Board (RWQCB) oversees onsite
treatment of “California Designated, Non-Hazardous Waste.” The Central Coast RWQCB
enforces water quality thresholds and standards set forth in the Basin Plan through the
project permitting process. The RWQCB requires project applicants to obtain a General
Construction Activities Stormwater Permit under the NPDES program. This program is
enforced in California by the RWQCBs. The permit requires that the applicant develop and
adhere to a Stormwater Pollution Prevention Plan (SWPPP) including implementation of
Best Management Practices (BMPs) to control erosion, siltation, turbidity, and pollution of
study area media by other potential contaminants typically associated with construction
activities. The SWPPP also includes BMPs necessary to control or prevent the release of
non-storm water discharges in storm water runoff. Additional information on storm water
management is described in Section 3.6, Hydrology and Water Quality.
Asbestos Hazard Emergency Response Act (AHERA) (1986)
This Act is the federal legislation that governs the control and abatement of asbestos
hazards present in school buildings. The purpose of this Act is to also require EPA to
conduct a study to determine the extent of danger to human health posed by asbestos in
public and commercial buildings and the means to respond to any such danger.
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National Emission Standards for Hazardous Air Pollutants 40 CFR 61 Subpart M –
(NESHAP)
If utility pipelines would be removed or relocated, or buildings would be removed or
renovated, the Project may be subject to the requirements stipulated in NESHAP. These
requirements include but are not limited to: 1) Notification requirements to the San Luis
Obispo County Air Pollution Control District (APCD); 2) asbestos survey conducted by a
Certified Asbestos Inspector; and 3) applicable removal and disposal requirements of
ACMs.
Federal Occupational Safety and Health Administration (OSHA) - Process Safety
Management Standard (29 CFR 1910.119)
This standard includes requirements for preventing or minimizing the consequences of
catastrophic releases of toxic, reactive, flammable, or explosive chemicals. Some of the
requirements of this standard include: all information pertaining to the hazardous chemicals
shall be available to the employees; employees shall be given training on the operation of
equipment with hazardous materials; and, the employer is required to perform a process
hazard analysis.
U.S. Department of Transportation
The U.S. Department of Transportation regulates hazardous materials transportation
between states. Within California, the California Department of Transportation (Caltrans)
and California Highway Patrol enforce federal law. Together, these agencies determine
driver training requirements, load labeling procedures, and specifications for container
types to be used.
3.6.3.2 State
Site-Specific Health and Safety (California Division of Occupational Safety and Health
Administration [Cal/OSHA] Title 8 and OSHA 29 Code of Federal Regulations [CFR]
1910).
The Project is subject to the requirements of state and federal occupational safety and health
requirements during Project operations. Under these requirements, a Site-specific Health
and Safety Plan must be developed prior to initiation of a proposed project. Workers
potentially exposed to hazardous materials in their workplace must be trained so that they
are aware of the hazards and provided necessary protection from the hazardous materials.
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California Air Resources Board (ARB) Airborne Toxics Control Measure (ATCM) for
Construction, Grading, Quarrying, and Surface Mining Operations (Section 93105)
This regulation applies to any area to be disturbed that is located in a geographic ultramafic
rock unit, or to any area where Naturally Occurring Asbestos (NOA) or serpentine would
be disturbed. Specific requirements may include conducting a geologic evaluation,
development of an Asbestos Dust Mitigation Plan and an Asbestos Health and Safety
Program for approval by the APCD.
Hazardous Material Release Response Plans and Inventory Law (California Health and
Safety Code [HSC], Chapter 6.95)
This law is designed to reduce the occurrence and severity of hazardous materials releases.
This state law requires businesses to develop a Release Response Plan for hazardous
materials emergencies if they handle more than 500 pounds, 55 gallons, or 200 cubic feet
of hazardous materials. In addition, the business must prepare a Hazardous Materials
Inventory of all hazardous materials stored or handled at the facility over the above
thresholds. Also, all hazardous materials must be stored in a safe manner. Both the Release
Response Plan and the Hazardous Materials Inventory must be supplied to the Certified
Unified Program Agency (CUPA) for the program. For the Project site, the CUPA is the
San Luis Obispo County Health Agency.
California HSC, Division 20, Chapter 6.8, Section 25319.5 - Preliminary Endangerment
Assessment (PEA)
The California HSC requires that a PEA provide sufficient information to determine
whether or not current or past waste management practices have resulted in the release or
a threatened release of hazardous substances that pose a threat to public health or the
environment. The PEA should also provide sufficient information to conclude whether or
not significant response actions are necessary at the site as well as include an analysis of
the scope and identity of the affected community.
Safe Drinking Water and Toxic Enforcement Act (Proposition 65) (1986)
In California, pursuant to the Safe Drinking Water and Toxic Enforcement Act of 1986:
(1) no person in the course of doing business shall knowingly discharge or release a
chemical known to the state to cause cancer or reproductive toxicity into water or onto land
where such chemical passes or probably will pass into any source of drinking water, and
(2) no person in the course of doing business shall knowingly and intentionally expose any
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individual to a chemical known to the state to cause cancer or reproductive toxicity without
first giving clear and reasonable warning to such individual. The "no significant risk" level
for carcinogens that is enforced by this Act is one in one hundred thousand (1 x 10-5).
Porter-Cologne Water Quality Control Act (Division 7 of the California Water Code)
The Porter-Cologne Act establishes a regulatory program to protect water quality and to
protect beneficial uses of state waters. The Porter-Cologne Act also establishes the state
board and regional boards as the principal state agencies responsible for control of water
quality. Each of the nine RWQCBs in California is required to develop guidance to assist
in ensuring that the intent of the Porter-Cologne Act is met. Cleanup criteria are based on
the type of contaminant (e.g., gasoline, diesel, or oil) released and the depth to
groundwater.
HSC, Division 20, Chapter 6.5, and California Code of Regulations (CCR) Title 22 –
Hazardous Waste Management
Waste that is toxic, corrosive, flammable, or reactive when tested in accordance with the
CCR, Title 22, Article 11, Section 66693, must be handled, stored, transported, and
disposed of in accordance with these regulations, which are more stringent than federal
regulations.
HSC, Division 20, Chapter 6.7, and CCR, Title 23 – UST Management
USTs used for storing petroleum products must be managed in accordance with California
law, which provides requirements for installation, materials used, secondary containment,
overspill protection, and monitoring.
California Fire Code
To minimize risks to public health and the environment, a Fire Prevention Inspector shall
review a list of hazardous materials stored aboveground on a property to assess potential
individual and/or cumulative impacts to the property and surrounding areas. The inspector
would ensure that hazardous materials stored onsite are in compliance with Chapter 6.95
of the California HSC. The fire code provides uniform fire prevention, hazardous material,
and building construction regulations.
FAA, Federal Aviation Regulation, Part 77 Objects Affecting Navigable Airspace - A
Notice of Proposed Construction or Alteration (Form 7460-1) maybe required by the FAA.
The FAA Airport Design Guide, Advisory Circular (AC) 150/5300-13, contains guidance
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pertaining to land uses within the Runway Protection Zone (RPZ). As part of FAA grant
assurances, if an airport sponsor receives federal funds for an airport, it is required that use
of land adjacent to or in the immediate vicinity of the airport be restricted to activities and
purposes compatible with normal airport operations.
3.6.3.3 Local
San Luis Obispo Municipal Code – Demolition and Moving of Buildings Section 115
Public Safety Requirements
These requirements include general requirements for building demolition activities,
permitting for such activities, hauling operations, and routes of moving materials. In
addition, there are subsections included for dust and debris, fire safety, and removal and
disposal of demolition materials.
City of San Luis Obispo General Plan
Safety Element
The City’s General Plan guides the use and protection of various resources to meet
community purposes. The Safety Element focuses on achieving acceptable levels of risk
through decisions on land use and the form of development, with consideration for the
closely related factor of transportation. The Safety Element includes policies that describe
an approach to achieving the goals of the General Plan. In terms of hazardous materials,
there are three policies included in the Safety Element:
Policy 3.0 Adequate Fire Services. Development should be approved only when adequate
fire suppression services and facilities are available or will be made available concurrent
with development, considering the setting, type, intensity, and form of the proposed
development.
Policy 3.1 Wildland Fire Safety.
F. Wildland fire hazard severity zones shall be classified as prescribed by CAL
FIRE. Areas within the City, including “Very High” Fire Hazard Severity Zones, if
any, shall be classified by the City’s Fire Code Official based on findings supported
by substantial evidence in the record as required by Government Code Section
51179 and considered by City Council at a public hearing. Meaningful, early
notification and input shall be obtained from nearby neighborhoods which may be
affected.
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G. New subdivisions shall be prohibited in areas of “Very High” wildland fire
hazard unless part of conservation or open space acquisition program. Development
of existing parcels shall require a development plan to manage fuels, maintain a
buffer zone, and provide adequate fire protection to the approval of the Chief
Building Official. The development plan must be consistent with Policies required
by the City’s Conservation and Open Space Element.
H. The City of San Luis Obispo is considered a “Community at Risk” due to the
threat of wildfire impacting the urban community. The City shall continue to
enhance the fire safety and construction codes for new buildings in order to reduce
the risk of urban fires that may result from wildfires. Citywide building code
enhancements should include: Fire resistant exterior wall coverings; Sprinkler
protection in attic areas; and Ember resistant vent systems for attics and under floor
areas and other provisions identified in CBC Chapter 7A.
Policy S 5.2 Minimizing Hazardous Materials Exposure – People’s exposure to hazardous
substances should be minimized.
Policy S 9.18 Safety of Structures and Facilities – Existing and new structures and facilities
should reflect adopted safety standards. Within this policy, the City has developed a
program, Program S 8.6.5 Required Inspections, whereby the City will conduct safety
inspections for hazardous materials in commercial, industrial, and multifamily residential
buildings.
Land Use Element
The City’s 2014 LUCE, the associated LUCE Update EIR, and technical studies such as
the 2014 Johnson Aviation Report address the issues of airport hazards in great detail.
Based on this analysis, the LUCE set forth both policies and programs to address airport
safety which are summarized below and discussed in more detail in Section 3.8, Land Use
and Planning. It should be noted that Program 7.16 and 7.17 have been completed and
adopted and are presented here for informational purposes only.
Policy 7.4 Airport Safety Zones. Density and allowed uses within the Airport Safety Zones
shall be consistent with the San Luis Obispo County Regional Airport ALUP unless the
City overrides a determination of inconsistency in accordance with Section 21676 and
21676.5 et seq. of the Public Utilities Code. If the City overrides a determination, all land
uses shall be consistent with the State Aeronautics Act and guidance provided in the
California Airport Land Use Planning Handbook guidelines, City policies, and noise
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3.6-16 Avila Ranch Development Project
Final EIR
standards as substantiated by the San Luis Obispo County Regional Airport Master Plan
activity forecasts as used for noise planning purposes.
Policy 7.6 Airspace Protection. The City shall use the Airport Master Plan Update and
FAA airport design standards and Part 77 surfaces to keep the airspace surrounding the
airport free of objects where required by the FAA or shall limit the height of objects as
required by the FAA. The City shall also ensure obstruction clearance is provided for all
en route and terminal (airport) instrument procedures as per the United States Standard for
Terminal Instrument Procedures (TERPS) to avert modifications to any planned or
published instrument approach or instrument departure procedures at SBP.
Program 7.16 Airport Overlay Zone. The City shall create an AOZ to reflect the
boundaries of the ALUP within the City limits. The purpose of the AOZ is to codify airport
compatibility criteria in areas for which the City may override the ALUC determination to
ensure compliance with the requirements of the California State Aeronautics Act (Cal. Pub.
Utilities Code, Section 21670, et seq.), which establishes statewide requirements for airport
land use compatibility planning, guidance from the California Airport Land Use Planning
Handbook, which is published by the Caltrans Division of Aeronautics to support and
amplify the State Aeronautics Act requirements, and other related federal and state
requirements relating to airport land use compatibility planning. Implementation of the
compatibility policies will be accomplished through the Zoning Code.
Program 7.17 Airport Land Use and Zoning Code. The City shall update its Zoning
Regulations to address allowable uses and development standards for areas in which the
City may override a determination of inconsistency. Zoning regulations shall be consistent
with the requirements of the State Aeronautics Act, use guidance from the Caltrans Airport
Land Use Planning Handbook, and comply with related state and federal requirements
relating to airport land use compatibility. These development standards will include, but
not be limited to, intensity and density limitations, identification of prohibited uses, infill
development, height limitations, obstructions, and other hazards to flight, noise insulation
requirements, buyer awareness measures, nonconforming uses and reconstruction and the
process for airport compatibility criteria reviews by the City consistent with these
development standards.
Airport Compatible Open Space Plan
The Airport Compatible Open Space Plan (ACOS) establishes open spaces in the areas
around the Airport that can serve as reserve spaces (for aircraft emergency situations; see
3.6 HAZARDS AND HAZARDOUS MATERIALS
Avila Ranch Development Project 3.6-17
Final EIR
Figure 6 of the ALUP Compatibility Analysis Pre-Application in Appendix N). By
maintaining reserve spaces that keep certain land adjacent to the Airport free and clear from
obstruction or from buildings and uses where people congregate, the ACOS improves
airport safety while allowing for more intense development of urban areas. The areas
identified as reserve space in the ACOS include land that is close to the Airport, in line
with the main airport runway, or along an over-flight area where aircraft typically operate
at lower altitudes. Identification of these areas in the ACOS adds airport safety to the list
of reasons why these lands should not be developed (City of San Luis Obispo and County
of San Luis Obispo 2013). On July 21, 2004, the ALUC voted to amend the ALUP with
inclusion of the City’s ACOS.
Airport Area Specific Plan
Policy 4.3.8 Approach and Climb-Out Paths. Retain extensive undeveloped land under
the approach and climb-out paths for all active runways.
Policy 4.3.9 East Airport Area Clear Zones. The City and the County will work to obtain
land or development rights in the East Airport Area to maintain clear zones for the east-
west runway.
Policy 4.3.10 Runway Protection Zones. No new development, roads or land uses shall be
allowed within the Runway Protection Zone in accordance with the Federal Aviation
Administration policies (including the Interim Guidance published on September 27, 2012,
and the Advisory Circular 150/5300-Change 17, unless the interim guidance is replaced
with future FAA policies), unless the development or land use is specifically approved in
coordination with the FAA.
Airport Land Use Plan for the San Luis Obispo County Regional Airport
State law requires an independent, countywide ALUC to adopt an ALUP for each airport.
This plan establishes zones based on flight patterns, with the aim of having future
development be compatible with airport operations, considering safety and noise exposure.
The ALUP was last amended in 2005 and is in process of being updated reflect the adopted
Airport Master Plan. A draft plan has not yet been released for public review and is
anticipated to be available in 2017. The ALUP contains several safety-related policies to
address future development:
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Final EIR
• Policy S-1. Would permit or lack sufficient provisions to prohibit structures and
other obstacles within the Runway Protection Zones for any runway at the Airport,
as depicted in ALUP Figure 4.
• Policy S-2. Would permit or fail to adequately prohibit any future residential or
nonresidential development or redevelopment which would create, within the site
to be developed or redeveloped, a density greater than specified in ALUP Table 7
or any mixed-use development or redevelopment which would create, within the
site to be developed or redeveloped, densities greater than illustrated in ALUP
Figures 5 through 8.
• Policy S-3. Would permit or fail to adequately prohibit any future development
project which specifies, entails, or would result in a greater building coverage than
permitted by ALUP Table 7 (see Table 3.8-3 in Section 3.8, Land Use and
Planning).
• Policy S-4. Would permit or fail to adequately prohibit high intensity land uses or
special land use functions (impaired egress uses or unusually hazardous uses),
except that, when conditions specified by ALUP Table 7 for density adjustments
have been determined to be met by the ALUC, high intensity land and/or special
function uses may be allowed in Aviation Safety Area S-2.
• Policy 4.4.4.2 Aviation Safety Sub-Areas. In consideration of the above, the ALUC
has established and adopted, within Aviation Safety Area S-1, the Aviation Safety
Sub-Areas shown in Figure 3. The Aviation Safety Sub-Areas are:
a. Safety Area S-1A – Those portions of Safety Area S-1 which are located
within 500 feet of the extended runway centerline of Runway 11-29 and
within 5000 feet of an existing or planned runway end or which are within
250 feet of the extended runway centerline of Runway 7-25 and within 3000
feet of the runway end.
b. Safety Area S-1B – Those portions of Safety Area S-1 which are not
included in Safety Area S1a, but are within probable gliding distance for
aircraft on expected approach or departure courses; also includes State-
defined sideline safety areas, inner turning zones and outer safety zones for
both Runway 11-29 and Runway 7-25 and portions of existing Airport Land
Use Zone 3. Aviation safety hazards to be particularly considered in this
area include mechanical failures, fuel exhaustion, deviation from glideslope
3.6 HAZARDS AND HAZARDOUS MATERIALS
Avila Ranch Development Project 3.6-19
Final EIR
or MDA during IFR operations (due to pilot error or equipment
malfunction), loss of control during short approach procedures, stall/spin
incidents during engine-out maneuvers in multi-engine aircraft, loss of
control during “go around” or missed approach procedures, and midair
collisions.
c. Safety Area S-1C – Those portions of Safety Area S-1 which are not
included in Safety Areas S-1a or S-1b, but are adjacent to (within 0.5 nm)
frequent or low-visibility aircraft operations at less than 500 feet above
ground level. Aviation safety hazards to be considered in this area include
mechanical failures, deviation from localizer or VOR during IFR operations
(due to pilot error or equipment malfunction), stall/spin incidents during
engine-out maneuvers in multi-engine aircraft, loss of control during “go
around” or missed approach procedures, and loss of visual references by
aircraft performing circle-to-land procedures.
In the event of any conflict between these verbal descriptions and the depiction of
Aviation Safety Areas in Figure 3, the depictions shown in Figure 3 shall take
precedence.
• 4.5.3 Airspace Protection Policies. Notwithstanding any other provision of this
ALUP, any proposed general plan, general plan amendment, specific plan, specific
plan amendment, zoning ordinance, zoning ordinance amendment, building
regulation modification, or individual development proposal will be determined to
be inconsistent with the ALUP if the proposed local action:
a. Policy A-1 – Lacks sufficient provisions to ensure that no structure,
landscaping, apparatus, or other feature, whether temporary or
permanent in nature shall constitute an obstruction to air navigation or
a hazard to air navigation, as defined above.
b. Policy A-2 – Would permit or lacks sufficient provisions to prohibit any
new landfill or other disposal site at a site or of a configuration which is
not consistent with all current state and federal statutes, FAA
regulations, and FAA Advisory Circulars concerning the relationship of
landfills and waste disposal sites to aeronautical operations and
facilities.
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3.6-20 Avila Ranch Development Project
Final EIR
These policies are linked to designated Airport runway safety zones which encompass the
Project site and are discussed more fully in Section 3.8, Land Use and Planning.
3.6.4 Environmental Impact Analysis
3.6.4.1 Thresholds of Significance
The Project would have a significant impact if it would create a public health hazard or
cause harm to the environment. The significance criteria for this hazardous materials
analysis are based on Appendix G of the 2016 CEQA Guidelines. A hazards and hazardous
materials impact is considered significant if the Project would:
a) Create a significant hazard to the public or the environment through the routine
transport, use, or disposal of hazardous materials;
b) Create a significant hazard to the public or the environment through reasonably
foreseeable upset and accident conditions involving the release of hazardous
materials into the environment;
c) Emit hazardous emissions or handle hazardous or acutely hazardous materials,
substances, or waste within 0.25 mile of an existing or proposed school;
d) Be located on a site which is included on a list of hazardous materials sites
compiled pursuant to Government Code Section 65962.5 and, as a result, would
create a significant hazard to the public or the environment;
e) Locate a project within an airport land use plan or, where such a plan has not been
adopted, within 2 miles of a public airport or public use airport, would the project
result in a safety hazard for people residing or working in the project area;
f) For a project within the vicinity of a private airstrip, would the project result in a
safety hazard for people residing or working in the project area;
g) Impair implementation of or physically interfere with an adopted emergency
response plan or emergency evacuation plan; or
h) Expose people or structures to a significant risk of loss, injury, or death involving
wildland fires, including where wildlands are adjacent to urbanized areas or where
residences are intermixed with wildlands.
3.6.4.2 Impact Assessment Methodology
The methodology used in this assessment includes review of existing adopted plans, public
databases, recent studies and EIRs, and site specific studies such as the PSA to assess the
potential presence of hazards and hazardous materials sites within the Project site and
vicinity. The PSA evaluated the site for conditions indicative of hazardous materials
resulting from previous releases, or potential release of hazardous materials. As part of the
PSA, soil sampling was conducted and tested for hydrocarbons. The Project site was also
3.6 HAZARDS AND HAZARDOUS MATERIALS
Avila Ranch Development Project 3.6-21
Final EIR
evaluated for the presence of hazardous materials based on a review the LUCE Update
EIR. In addition, this analysis integrated current information for contaminated sites from
EPA’s EnviroFacts, and DTSC’s EnviroStor and GeoTracker databases.
Risk associated with wildfire is assessed based on the existing Fire Hazard Severity Zone
as determined by CALFIRE and changes that may result after implementation of the
Project.
The analysis also describes how the policies, regulations, and standards provided in the
LUCE, as well as Project design measures would minimize airport-related hazards. Key
LUCE related restrictions include limitations on development within designated Airport
AOZs which limit allowable development types and intensity based upon updated mapping
of runway approach areas (refer to Section 3.8, Land Use and Planning for a complete
description). Project-related design features would include:
• A 300-foot-wide open space buffer north of Buckley Road aligned with the
approximate extended centerline of Runway 7-25, and a 100- by 1,200-foot-wide
ACOS between the Jespersen Road Extension and the eastern Project boundary.
• A 150-foot-wide open space buffer on the eastern Project boundary.
• Approximately 34.5 acres of open space and parks in southeastern area of Project
site nearest the Airport and ALUP Safety Area S-2.
• Limiting development in ALUP Safety Area S-1B to seven dwelling units, to be
located in the northeastern corner of the safety zone.
• No development within the S-1C Safety Zone.
Further, analysis included review of the State Aeronautics Act, the FAA regulations, and
guidance provided in the Caltrans Airport Land Use Planning Handbook. In addition,
policy consistency with the ALUP Safety Areas and City LUCE AOZs is provided in
Section 3.8, Land Use and Planning. According to CEQA Section 21096 and CEQA
Guidelines Section 15154, for the purposes of determining excessive safety and noise
impacts “…the agency shall utilize the Airport Land Use Planning Handbook published by
Caltrans’ Division of Aeronautics to assist in the preparation of the EIR relative to potential
airport-related safety hazards and noise problems.” ALUP consistency or inconsistency is
addressed in Section 3.8, Land Use and Planning; however, for the purposes of this section,
the Handbook and the ALUP are used for hazards impacts.
There are no public schools within 0.25 mile of the Project site and therefore threshold ‘c’
would not apply. Typical materials (e.g., cleaning soaps, solvents and pesticides) used in a
residential and commercial development such as the Project would be similar in nature to
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3.6-22 Avila Ranch Development Project
Final EIR
those used at the school due to the continual presence of residents and retail patrons.
Accordingly, there would be no potentially significant adverse impact to schools.
3.6.4.3 Project Impacts and Mitigation Measures
Potentially sensitive receptors that could be affected by hazards and hazardous materials
impacts include future Project site occupants, Project construction workers, and nearby
ecological receptors. Potential impacts related to hazardous materials, airport operations
and wildfire are discussed further below and summarized in Table 3.6-3.
Table 3.6-3. Summary of Project Impacts
Hazards and Hazardous Materials Impacts Mitigation Measures Residual Significance
HAZ-1. During grading/construction activities and
Project operations, the Project would potentially
expose persons to potentially toxic, hazardous, or
otherwise harmful chemicals through reasonably
foreseeable upset and accidental conditions
involving the release of hazardous materials into the
environment.
MM HAZ-1 Significant but
Mitigable
HAZ-2. The Project would not create a hazard to
the public or the environment through the routine
transport, use, or disposal of hazardous materials.
None required Less than Significant
HAZ-3. The Project site is located within the
LUCE defined AOZs and ALUP Safety Areas and
would potentially result in an airport-related safety
hazard for people residing or working in the Project
site.
None required Less than Significant
HAZ-4. Implementation of the Project could
expose people or structures to a significant risk of
loss, injury, or death involving wildfire.
None required Less than Significant
Impact HAZ-1 During grading/construction activities and Project operations, the
Project would potentially expose persons to potentially toxic,
hazardous, or otherwise harmful chemicals through reasonably
foreseeable upset and accidental conditions involving the release of
hazardous materials into the environment (Significant but
Mitigable).
Based on the Project’s proximity to the Chevron Tank Farm property and contaminants
contained within associated cleanup sites, other identified cleanup sites, the potential
presence of ACM within the onsite farm house, and the use of pesticides and herbicides
within the site, there is a potential for construction workers and the nearby general public
3.6 HAZARDS AND HAZARDOUS MATERIALS
Avila Ranch Development Project 3.6-23
Final EIR
to be exposed to hazardous materials during grading and construction of site buildings and
structures.
Contamination from the 1926 Unocal Tank Farm Fire
The 1926 Unocal Tank Farm fire and associated release of hazardous materials onto the
Project site resulted in the contamination of soils and groundwater onsite. As described
above, several investigations performed on the Chevron Tank Farm property concluded
that residual contaminants from this incident are currently contained within the Chevron
Tank Farm property. The PSA concludes that the relatively minor amounts of heavy
hydrocarbon presence does not pose any significant health or environmental concerns (see
Appendix L). However, although extensive testing and groundwater monitoring at this site
has shown that the contamination has not migrated from the Chevron Tank Farm facility,
future construction associated with development of the Project has the potential to expose
construction workers to hydrocarbons within soils and groundwater (City of San Luis
Obispo 2014).
Offsite Contamination
In addition to the two active cleanup sites associated with the Chevron Tank Farm property,
there are three additional active cleanup sites and three inactive within 0.5 mile of the
Project (refer to Table 3.6-1). The potential of these sites to result in migration of
contaminated materials to the Project site is assessed in the PSA. The inactive cleanup sites
have been remediated of contamination and require no further action from the DTSC; thus,
these inactive sites have a very low potential for migration of contaminants into the site.
Two active cleanup sites are along Los Osos Valley Road 0.5 mile away from the Project
site and contain of soil and groundwater contamination; and two cleanup sites are located
on Tank Farm Road 0.5 mile from the Project site, and contain groundwater contamination.
Given the distance between the Project site and the active cleanup sites, the PSA concludes
that potential for Project site contamination from these sites due to migration is low.
Hazardous Materials Associated with Agricultural Operations
Based on historical agricultural use on the Project site, there is potential for low
concentrations of pesticides, herbicides and fertilizers to be to be exposed to construction
workers and the nearby general public during grading and construction activities. Soil
samples analyzed as part of the PSA were tested for 64 types of pesticides and herbicides
of toxic concern, and samples showed no detectable concentrations. In addition, users of
such materials are required to follow manufacturer instructions and dispose of excess
3.6 HAZARDS AND HAZARDOUS MATERIALS
3.6-24 Avila Ranch Development Project
Final EIR
solutions and empty containers properly. Under normal use, pesticides and herbicides
would be in low concentrations within soils that are generally not considered a hazard to
human health (Grisanti & Associates 2011).
ACM and Lead
Due to the age of the existing farmhouse onsite, hazardous materials such as LBP and
ACMs may be present onsite. As such, the potential exists for workers or the public to be
exposed to these materials during demolition of the onsite building and hauling of debris
materials. Existing state regulations require the abatement and control of asbestos and lead
in advance of demolishment or renovation activities, as regulated in Title 8, Industrial
Relations, of the CCR. The demolition waste may contain ACMs due to the age of the old
farmhouse. However, based on recent field work at the Project site, this farmhouse appears
to have been demolished. Accordingly, no demolition would be carried out as part of the
Project. There may also be ACMs within the existing buildings on the Buckley Road
Extension site. These structures would be demolished as part of the Project and may result
in exposure of asbestos.
Naturally Occurring Asbestos
NOA could be uncovered as a result of the grading of less than 1 acre within serpentine
rock on the Buckley Road Extension site (GeoSolutions, Inc. 2015). Where it is
encountered, the mitigation below would apply.
Overall, due to the proximity of the adjacent Chevron Tank Farm property and associated
historic releases, low concentrations of hazardous materials exist within soils and
groundwater. Based on these conditions, there is potential for construction workers and/or
nearby occupants to be exposed to potentially toxic, hazardous, or otherwise harmful
chemicals during excavation, grading, and site preparation activities. However, with
inclusion of mitigation measures, potential impacts to the construction workers and nearby
general public associated with hazardous materials would be significant but mitigable.
Mitigation Measures
MM HAZ-1 Prior to earthwork and demolition activities, a site-specific Health and
Safety Plan shall be developed per California Occupational Safety and
Health Administration (Cal/OSHA) requirements. The Health and Safety
Plan shall include appropriate best management practices (BMPs) related
to the treatment, handling, and disposal of NOA and ACMs. A NOA
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Avila Ranch Development Project 3.6-25
Final EIR
Construction and Grading Project Form shall be submitted to the APCD
prior to grading activities. All construction employees that have the
potential to come into contact with contaminated building materials and
soil/bedrock shall be briefed on the safety plan, including required proper
training and use of personal protective equipment. During earthwork and
demolition activities, procedures shall be followed to eliminate or minimize
construction worker or general public exposure to heavy hydrocarbons and
other potential contaminants in soil and groundwater, and potential ACMs
within potential demolished materials. Procedures shall include efforts to
control fugitive dust, contain and cover excavation debris piles, appropriate
laboratory analysis of soil for waste characterization, segregation of
contaminated soil from uncontaminated soil, and demolished materials. The
applicable regulations associated with excavation, removal, transportation,
and disposal of contaminated soil shall be followed (e.g., tarping of trucks
and waste manifesting).
Plan Requirements and Timing. The Applicant shall submit the Site-
specific Health and Safety Plan to the City for review and approval prior to
issuance of grading and building permits from the City, and/or demolition
permits from the County. The Applicant shall conduct necessary
construction employee training prior to the initiation of construction.
Monitoring. The City and County shall ensure compliance. An
Environmental Monitor shall be made available to monitor environmental
compliance of the construction activities. The City and County shall also
inspect the Project site during construction to ensure compliance with
required plans.
Residual Impacts
Implementation of the above mitigation measures and compliance with federal, state, and
local regulations would reduce the risk of hazardous impact to less than significant.
Additionally, mitigation measures would facilitate the safe removal of potentially
hazardous building materials and the cleanup of contaminated soils, thus reducing the level
of risk within the Project site.
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3.6-26 Avila Ranch Development Project
Final EIR
Impact HAZ-2 The Project would not create a hazard to the public or the
environment through the routine transport, use, or disposal of
hazardous materials (Less than Significant).
Operation of the Project would involve the use of potentially hazardous materials,
including vehicle fuels, oils, and transmission fluids. In addition, operation of residential
and commercial uses within the Project site would entail routine cleaning and maintenance
activities using common hazardous materials, such as cleaning fluids, detergents, solvents,
adhesives, sealers, paints, fuels/lubricants and pesticides/herbicides, etc. However,
applications of such materials would likely be in limited (i.e., not commercially reportable)
quantities and would be handled in compliance with federal, state, and local regulations
pertaining to their transport, use, or disposal. As further discussed in Section 3.7,
Hydrology and Water Quality, implementation of standard good housekeeping measures,
BMPs, site maintenance and security precautions, as well as compliance with standards
and regulations would reduce potential impacts related to the routine transport, use, or
disposal of hazardous materials to less than significant.
Impact HAZ-3 The Project site is located within the LUCE defined AOZs and ALUP
Safety Areas and would potentially result in an airport-related safety
hazard for people residing or working in the Project site (Less than
Significant).
Airport safety is primarily related to the potential for accidents related to aircraft operations
such as emergency landings or in rare cases crashes, as well as ensuring that land use
development is carried out in manner that minimizes or avoids risks associated with such
aircraft incidents or accidents. Minimizing or avoiding risks to such land uses (e.g.,
residential neighborhoods) involves designating areas around the ends of runways that
must be free of objects or sensitive land uses, limiting the height of new structures in the
surrounding airspace, and understanding historical accident patterns. The Project site’s
proximity to the end of Runway 7-25 would present a potential airport-related safety issue
for future development, if development intensities exceed the standards established in the
ALUP and the Handbook. In the event of an aircraft emergency incident, development of
new structures within or near the approach path for Runway 7-25 has the potential to place
future residents and users of the commercial Town Center, parks and open spaces, as well
as passengers and crew of aircrafts at risk. The risk of an aircraft accident increases with
proximity to the runway and its approach path, and development is generally discouraged
in the zones closest to the ends of runways to prevent placing people at risk of an accident.
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Avila Ranch Development Project 3.6-27
Final EIR
Although Runway 7-25 supports only 3 percent of Airport aircraft operations and is utilized
for general aircraft rather than commercial services, a low potential for accidents remains.
The Project site is located approximately 0.7 mile away from Runway 7-25, and the nearest
proposed developed portion of the Project is 0.8 mile from the end of the runway. The
nearest proposed residential area is in the approximately 1.0 mile from the end of Runway
7-25 along the extended centerline path of Runway 7-25. However, the majority of the
Project site is outside of the general approach areas of Runway 7-25. The site is mostly
overlapped by general circulation areas as indicated by AOZ 6 and S-2 which generally
indicate areas of overhead aircraft turning movements.
Project development would result in construction of 720 new homes and a small
commercial 15,000 sf Town Center with an associated increase of 1,649 new residents
within LUCE AOZs and ALUP Safety Areas.
As confirmed during the pre-application for the Project with the ALUC, approximately
34.9 acres of the Project site fall within ALUP Safety Area S-1B, 7.6 acres would be within
S-1C, and 107.5 acres would be within S-2 (see Appendix N). In comparison, while the
entire Project site is located within City LUCE AOZ 6, the level of proposed development
would be consistent with the restrictions of this AOZ. No Project residential development
would be located within more restrictive City LUCE AOZs, which are located along the
eastern Project boundary or closer to the Airport offsite to the east. These potential
inconsistencies are discussed at length in Section 3.8, Land Use and Planning (see Tables
3.8-3 and 3.8-5).
The proposed development is consistent with the population and density standards
specified in the Handbook, the population and density standards in the ALUP, and the
population and density standards in the City’s AOZs. Therefore, no resultant substantial
physical Airport-related safety hazards would occur as result of Project implementation.
While the Project would still be subject to review by the ALUC for consistency with the
ALUP, such issues are further discussed in Section 3.8, Land Use and Planning., airport
safety impacts to residents and commercial Town Center employees or patrons within the
Project site would be less than significant.
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3.6-28 Avila Ranch Development Project
Final EIR
Impact HAZ-4 Implementation of the Project could expose people or structures to a
significant risk of loss, injury, or death involving wildfire (Less than
Significant).
As described in Section 3.6.2.1, Wildfire Risk, the Project would be located in a part of the
City that includes moderate fire hazard potential. Extensive areas of onsite and adjacent
grasslands and vegetation along Tank Farm Creek could provide natural fuels for wildfires
in the area.
The Project would include the construction of 720 residences and a 15,000 sf Town Center.
Development of the Project would increase the potential to expose both structures and
people to wildfires. Operation of construction equipment such as saws, welders, generators,
and heavy machinery would temporarily introduce new ignition sources into the area.
While the chance of accidental ignition by such heavy equipment may seem improbable,
several wildland fires in Southern California have been ignited by such equipment. Under
Project conditions, wildfires burning into the open space surrounding the Project would
present the potential for serious damage to the Project and would potentially threaten the
health and safety of residents.
Due to the increase in residential population within the site, the potential exists for impacts
related to exposing people or structures to wildfires. However, the northern extent of the
High and Very High Fire Hazard Severity Zones terminate approximately 1 mile north of
the Project site (CAL FIRE 2007). In addition, along the Project site’s southern boundary,
a widened Buckley Road corridor would provide a limited fuel break between higher fire
hazard areas to the south and new development, as well as improved emergency vehicle
access. As such, the Project is at moderate risk for wildfires. Compliance with the CBC
and UBC construction requirements for residences would minimize this risk. Consistent
with the LUCE Update EIR, compliance with policies within the Safety Element would
reduce the risk of damage or injury. Therefore, impacts related to exposing people or
structures to wildland fires are considered less than significant.
3.6.4.4 Cumulative Impacts
Cumulative pending development projects and land use changes within the City and the
Project vicinity would have the potential to expose future area residents, employees, and
visitors to chemical hazards through development of sites and structures that may be
contaminated from either historic or ongoing uses. In addition, the increased development
would also expose residents, employees, and visitors to potential aircraft-related hazards.
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Avila Ranch Development Project 3.6-29
Final EIR
Several cumulative projects listed within Table 3.0-1 are also within AOZs and ALUP
Safety Areas, thereby potentially exposing persons to risk of airport safety hazards. These
include the Chevron Tank Farm Remediation Project, residential units, and commercial
developments near the Airport. Pending projects such as the 500 residential units on the
proposed San Luis Ranch Specific Plan project would also incrementally contribute to
potential cumulative Airport-related hazards. The severity of potential hazards for
individual projects would depend upon the location, type, and size of development and the
specific hazards associated with individual sites. Therefore, specific projects proposed in
the City would be required to undergo individual environmental review, including review
of potential impacts related to hazards and hazardous materials that are applicable to that
particular development site and proposed use. Because restrictions on development or
remediation requirements would be applied in the event that hazardous materials posed a
risk to safety, it is anticipated that cumulative impacts from exposure to hazards or
hazardous materials would not be cumulatively considerable. Additionally, projects
anticipated to occur under the LUCE would facilitate the safe removal of potentially
hazardous building materials and the cleanup of contaminated properties, thus reducing the
level of risk on a particular site. In addition, all future development would be regulated to
reduce the risk of exposure to aircraft-related hazards. Therefore, cumulative impacts are
considered less than significant.
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