CC SR 20230321 01 - Portuguese Bend DEIR
PUBLIC HEARING
Date: March 21, 2023
Subject:
Consideration and possible action to receive public comments on the Draft Environmental Impact
Report for the Portuguese Bend Landslide Remediation Project.
Recommendation:
(1) Conduct a public hearing to receive public comments on the Portuguese Bend Landslide
Remediation Project Draft Environmental Impact Report.
1. Report of Notice Given: City Clerk
2. Declare Public Hearing Open: Mayor Ferraro
3. Request for Staff Report: Mayor Ferraro
4. Staff Report & Recommendation: Ramzi Awwad, Public Works Director
5. Council Questions of Staff (factual and without bias):
6. Testimony from members of the public:
The normal time limit for each speaker is three (3) minutes. The Presiding Officer may grant additional time to a representative speaking
for an entire group. The Mayor also may adjust the time limit for individual speakers depending upon the number of speakers who
intend to speak.
7. Declare Hearing Closed/or Continue the Public Hearing to a later date: Mayor Ferraro
8. Council Deliberation:
The Council may ask staff to address questions raised by the testimony, or to clarify matters. Staff and/or Council may also answer
questions posed by speakers during their testimony. The Council will then debate and/or make motions on the matter.
9. Council Action:
The Council may: vote on the item; offer amendments or substitute motions to decide the matter; reopen the hearing for additi onal
testimony; continue the matter to a later date for a decision.
CITY COUNCIL MEETING DATE: 03/21/2023
AGENDA REPORT AGENDA HEADING: Public Hearing
AGENDA TITLE:
Consideration and possible action to receive public comments on the Draft Environmental
Impact Report for the Portuguese Bend Landslide Remediation Project
RECOMMENDED COUNCIL ACTION:
(1) Conduct a public hearing to receive public comments on the Portuguese Bend
Landslide Remediation Project Draft Environmental Impact Report.
FISCAL IMPACT: There is no fiscal impact associated with conducting the Public
Hearing.
Amount Budgeted: N/A
Additional Appropriation: N/A
Account Number(s): N/A
ORIGINATED BY: Ramzi Awwad, Public Works Director
REVIEWED BY: Same as above
APPROVED BY: Ara Mihranian, AICP, City Manager
ATTACHED SUPPORTING DOCUMENTS:
A. Portuguese Bend Landslide Remediation Project Draft EIR (document and
appendices at this link).
B. Mitigation and Monitoring Report Program (MMRP)
C. December 19, 2020 Staff Report- Portuguese Bend Landslide Remediation Project
Environmental Impact Report Scoping (at this link).
D. December 17, 2019 Staff Report- Portuguese Bend Landslide Remediation Project
Preliminary Design (at this link).
E. August 7, 2018 Staff Report- Portuguese Bend Landslide Remediation Updated
Feasibility Study (at this link).
F. Natural Communities Conservation Plan/Habitat Conservation Plan (NCCP/HCP)
(at this link)
BACKGROUND:
Feasibility Study
In the spring of 2017, the City Council appointed then-Mayor Pro Tem Jerry Duhovic and
then-Council Member Ken Dyda to a subcommittee to identify possible solutions or
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strategies to remediate the Portuguese Bend Landslide (PBL). This subcommittee was
formed to begin a collaborative process with community stakeholders and professional
experts from D.B. Stephens & Associates on identifying possible engineering solutions to
remediate the PBL. Additionally, to provide a forum for stakeholder involvement, the City
Council convened a committee of concerned residents to chart a path toward significantly
reducing movement of the PBL.
A series of four public workshops were held to elicit the best ideas from the community,
and to seek input on goals and possible solutions to remediate the PB L. Approximately
20-30 residents attended each of these workshops and participated in the process.
Considering input at these workshops, the City commissioned the Portuguese Bend
Landslide Remediation Feasibility Study (Feasibility Study) to identify and select a
conceptual solution to significantly reduce landslide movement.
On January 16, 2018, Staff presented the City Council with a draft Feasibility Study, and
on June 18, 2018, a public workshop was conducted to provide residents with a summary
of the Feasibility Study and answer their questions. On August 7, 2018, Staff presented
the City Council with the Updated Feasibility Study (Attachment D). The City Council then
authorized Staff to move forward with design of the PBL Remediation Project (Project).
On December 17, 2019, following meetings with the Palos Verdes Peninsula Land
Conservancy (PVPLC) and other community stakeholders, Staff presented to the City
Council the proposed preliminary design for the PBL Remediation Project (Attachment
C). After considering public testimony, the City Council accepted the proposed plan and
directed Staff to proceed with preparing the environmental documents required by the
California Environmental Quality Act (CEQA).
On May 19, 2020, the City entered into a professional services agreement (PSA) with
Chambers Group Inc. (Chambers) for preparation of environmental documen ts.
Chambers first prepared an Initial Study (IS), which concluded that an Environmental
Impact Report (EIR) was necessary to meet CEQA requirements.
On December 19, 2020, the City Council conducted a public hearing to receive public
comments regarding the issues to be addressed in the EIR (Attachment B). As a result,
the EIR was scoped to study the following based on the project description and objectives:
• Aesthetics
• Air Quality
• Biological Resources
• Cultural Resources
• Energy
• Geology and Soils
• Greenhouse Gas Emissions
• Hazards and Hazardous Materials
• Hydrology and Water Quality
• Land Use and Planning
• Noise
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• Recreation
• Transportation
• Tribal Cultural Resources
• Utilities and Service Systems
• Wildfire
Environmental Impact Report
The purpose of an EIR is to identify the significant effects on the environment of a project,
to identify alternatives to the project, and to indicate the manner in which those significant
effects can be mitigated to a less than significant level or avoided. The City is the lead
agency for the Project and therefore has the authority for preparation of a Draft EIR
(DEIR) and, after the comment/response process, certification of the Final EIR.
The DEIR evaluates and mitigates a reasonable worst-case scenario of potential impacts
associated with the proposed project. It is an informational document for the lead agency
and other public agencies, the general public, and decision makers regarding the potential
environmental impacts from construction and operation of the proposed project. CEQA
requires the lead agency to consider the information contained in the EIR prior to taking
any discretionary action. Certification of an EIR does not render the project approved.
The purpose of the public review of the DEIR is to evaluate the adequacy of the
environmental analysis in terms of compliance with CEQA. The standards from which
adequacy is judged, per CEQA Guidelines, is that the EIR is prepared with a sufficient
degree of analysis to provide decisionmakers with information which enables them to
make a decision which intelligently takes account of environmental consequences. An
evaluation of the environmental effects of a proposed project need not be exhaustive, but
the sufficiency of an EIR is to be reviewed in the light of what is reasonably feasible.
Disagreement among experts does not make an EIR inadequate, but the EIR should
summarize the main points of disagreement among experts. In summary, EIRs are
intended to provide an objective, factually supported, full-disclosure analysis of the
environmental consequences associated with a proposed project that has the potential to
result in significant, adverse environmental impacts.
Chambers concluded its work by delivering the technical studies to be used in developing
the EIR. The technical studies are included in the DEIR as appendices/supporting
documents (Attachment A).
On February 15, 2022, the City retained Hout Engineering (Hout), to provide program
management services for various projects associated with the Portuguese Bend area
landslides, including peer review of the EIR. On October 4, 2022, the City Council retained
LSA Associates, Inc. (LSA) to prepare the DEIR, and subsequently the Final EIR for
certification by the City Council.
The DEIR was released on February 9, 2023 for public review and comment for a 64-day
period through April 14, 2023. CEQA requires a comment period of no less than 30 days
and not longer than 60 days except under unusual circumstances. The City elected to
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give 60 days to allow maximum public participation. However, because the 60th day would
be the day following Easter and might exclude some persons from commenting, the City
extended the comment period a few days beyond the 60 days.
This evening, as part of the public comment process, the City Council is holding a public
hearing to receive comments from interested parties, and to provide their own comments
if desired. After the public review period ends, LSA will review the comments, respond to
them and make final revisions to the report. A Final EIR will go before the City Council for
certification at a future meeting, likely in summer 2023.
DISCUSSION:
Project Objectives
The City established the following project objectives for the PBL Remediation Project that
will aid decisionmakers in their review of the project and its associated environmental
impacts:
• Identify geotechnical engineering solutions that are environmentally sensitive; will
substantially reduce the risk of damage to public and private property (including
residences); and would allow for the significant improvements of roadway and
infrastructure, safety, and stability projects.
• Reduce substantial human health risk and improve public safety.
• Reduce the likelihood of major landslide movement that would drastically impact and
could sever sewer trunk lines along Palos Verdes Drive South and cause effluent
discharge into the ocean, resulting in regional impacts to the marine and terrestrial
ecosystem.
• Reduce the likelihood of major landslide movement that would damage and render a
major arterial street, Palos Verdes Drive South, unusable, potentially leading to major
detours, additional vehicle emissions associated with additional miles traveled, major
disruptions to traveling motorists, and loss of productivity throughout the City of
Rancho Palos Verdes and its surrounding communities.
• Reduce the likelihood of surface fractures that would damage and fragment sensitive
species habitat, thereby enhance native vegetation in the Preserve.
• Alleviate artesian water pressure below the PBL area, which is believed to be a major
contributing factor to landslide movement and control major surface water runoff.
• Reduce discharge of substantial sediments and associated pollutants into the Pacific
Ocean that contribute to negative impacts on the coastal and marine environments.
• Select remedy options that are consistent with the natural visual characteristics of the
surrounding Preserve.
Project Description
The project site is located along the south section of the City and consists of
approximately 206 acres within the overall approximately 750-acre landslide complex
(project site). The project site includes approximately 104 acres of land located within the
City-owned Palos Verdes Nature Preserve (Preserve), specifically within the Portuguese
Bend and Abalone Cove Reserves within the Preserve.
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Surrounding the project site are residential uses that include the Portuguese Bend Beach
Club to the south, the Portuguese Bend Community Association to the west, and the
Seaview neighborhood to the east. East of the project site is Klondike Canyon and directly
north is the Portuguese Bend Reserve, followed by additional residential uses. The
southern portion of the project site can be accessed via Yacht Harbor Drive/Seawall
Road, a private road within the Portuguese Bend Beach Club community. The Pacific
Ocean is located to the south of the project site. Several residences exist adjacent to the
northwestern boundary of the project site. Many neighborhoods are affected by this
landslide, such as the Portuguese Bend Community Association and the Portuguese
Bend Beach Club. The exhibit below is Figure 3-2 from the DEIR. The yellow outline is
the project area and the green shaded area is the Portuguese Bend Reserve.
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The proposed preliminary design consists of three remediation measures that can be
constructed all at once or be phased depending on factors, such as funding availability.
The Project components — preventing groundwater infiltration, diverting stormwater, and
extracting groundwater — will greatly reduce ground movement and the risk of a sudden
event.
The DEIR identifies three construction components that should be implemented to
achieve the maximum reduction in ground movement:
1. Surface Fracture Infilling: PBL movement is manifested, in addition to lateral
displacement, by surface settlement and cracking. Multiple fractures are present,
and most are observable throughout the project site. A surface fracture can be
defined as a long, narrow crack opening observable at the ground surface. Surface
fractures are induced by landslide movement and once formed, can be extended
and eroded by stormwater runoff. They can be hazardous to people living on or
near the affected surfaces and damaging to property and infrastructure, as well as
to the general public visiting the area and utilizing the trails in the Preserve. The
fractures increase erosion and disrupt native habitat. The existing surface fractures
within the project site are a few feet wide, and some are as deep a s 15 or more
feet. These fractures collect stormwater runoff that discharges into the ground. The
stormwater runoff enters the fractures, where it percolates into the ground and
becomes part of the groundwater, which exacerbates landslide movement. The
surface fracture infilling will control stormwater runoff infiltrating the ground and will
help in solving one aspect of the landslide movement. The infilling of the surface
fractures (shown on Figure 3-6, Surface Fracture Infilling Locations) with
appropriate materials (such as bentonite chips and/or soil) will minimize direct
uncontrolled stormwater infiltration, which currently percolates into the
groundwater. The exhibit on the next page is Figure 3-6 from the DEIR. The area
outlined in yellow is the project area, and the red lines generally show the surface
fracture infilling locations.
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2. Surface Water Improvements and Drainage System : The proposed project
considers installing new surface water drainage improvements and refurbishing
existing pipes to minimize the soil erosion loss and stormwater ponding and
infiltration that contributes to landslide movement. These surface water
improvements are described and shown in the exhibit below which is Figure 3-7
from the DEIR. The project area is outlined in yellow; the flow reduction (detention
basin) area is shown in light blue; the engineered vegetated natural swales are
shown in dark blue; and the underground pipes are shown in black.
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Natural vegetated swales will be installed to collect surface water runoff, convey it
to a new flow reduction (detention basin) area, and then through a pipe to be
rehabilitated underneath Palos Verdes Drive South conveyed to the Pacific Ocean.
The vegetated swales are a nature-based approach consistent with the sensitive
natural habitat and vegetation in the Preserve. These improvements will manage
runoff and not allow it to pond or infiltrate into the ground, therefore minimizing the
consequences of rainwater aggravating or accelerating landslide movement.
Swales are designed to manage surface stormwater runoff and can be described
as shallow channels with gently sloping sides. The proposed project would install
a network of surface drainage swales that extend south from Burma Road and
traverse through the project site. The drainage swales have been designed to be
vegetated ranging from a width of 2 to 10 feet at the bottom and a width of 14 to
26 feet at the top. The surface drainage swales would convey surface runoff from
the northern limits of the project site, connect to a new flow reduction area, and
travel south underneath Palos Verdes Drive South to the Pacific Ocean. The
surface drainage swales would be designed to be visually complementary to the
surrounding setting of the Preserve and lined with context-sensitive vegetation
instead of concrete. Erosion control measures, such as geocells and/or riprap will
be implemented within swales. The designs will be consistent with restoration
requirements outlined in the City’s Natural Communities Conservation
Plan/Habitat Conservation Plan (NCCP/HCP) and other resource/regulatory
review requirements. The swales will be planted with native vegetation and the
Palos Verdes Land Conservancy will be consulted regarding the plant pale tte
along with the source of plants/seeds.
Surface Drainage Swale Concept
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3. Hydrauger Systems: Hydraugers will be installed to extract groundwater, relieving
artesian water pressure on the landslide and reducing lubrication of the landslide
soils. These drains will be advanced by directional drilling rather than vertical
drilling, which is susceptible to shearing from landslide movement. The collected
water will be tested for quality prior to discharging it to the ocean.
A groundwater extraction system of horizontal pipes, or hydraugers, would be
installed to alleviate artesian water pressure below the PBL, which is believed to
be the main contributor to landslide movement. The approximate locations of the
hydraugers are shown on Figure 3-9, Hydrauger Locations. Where possible,
hydraugers would be installed below the side plane to avoid shearing off by
landslide movement. Water will exit by controlled pressure flow and/or gravity flow
and will be routed through a storm drain system into the Pacific Ocean. The two
hydraugers located within the northern portion of the project site (A2 and A3) will
be installed horizontally, beneath the active movement zone of the landslide. The
horizontal hydraugers are advanced on a slightly upward slope to promote gravity
flow to alleviate artesian water pressure underground. The other three hydraugers
in the southern portion of the project site (A1, A5, and A6) will be installed
directionally (following the contour of the basal sliding plane). Within the PBL, the
hydraugers will be installed sequentially, in fan-shaped patterns. They will extend
within City-owned right-of-way or property. The ultimate size of the hydraugers
would depend on field conditions (groundwater yield). Depending on site
conditions, hydrauger length might reach up to 1,200 feet with a diameter of up to
6 inches. The hydrauger depth will vary, with the deepest points reaching up to
400 feet below ground surface. The exhibit on the next page is Figure 3-9 from the
DEIR. The project area is shown in a yellow outline; the hydraugers are show with
red lines in a fan pattern; the orange squares indicate the hydraugers are
horizontally drilled; and the green square indicate the hydraugers are directionally
drilled.
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The ground water extraction system will utilize pumps (either electric or gasoline
powered) to pump the artesian water from beneath the surface to ground level. The
pumped water will be stored, tested, and discharged appropriately for the best use of the
underground water. During final engineering, the pumps will be designed and specified in
the project construction documents.
The hydrauger system of extracting underground water in active landslide areas has been
successfully implemented for several years in the United States and abroad, including as
close as White Point in San Pedro and Malibu near the Big Rock area. The City will ensure
that the project will receive a tailored design specific to the site conditions. The exhibits
below (courtesy of others) are examples of the hydrauger system illustrating its
installation and operation in a landslide area.
The three project components will be constructed on City/public property . Therefore,
permanent easements will not need to be acquired. Construction will take place outside
of the mean tide line that will streamline the California Coastal Commission (CCC)
permit/approval if needed.
The Ransome Construction Co. began installing horizontal drains in the Oakland Hills in 1940, and others
began using them along the Pacific Coast Highway in Santa Monica (shown here) a few years later.
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Project Impacts
During the Project’s scoping process and earlier public comments, areas of concern
included impacts the project might have on the aesthetic value in the Preserve, minimizing
biological impacts, erosion of topsoil, and recreational accessibility. The DEIR address es
each of these areas as well as additional topics.
The DEIR identified no significant effects on agriculture and forestry resources, mineral
resources, population and housing, and public services.
All remaining environmental issues analyzed in this DEIR were determined to result in
less than significant impacts or can be reduced to less than significant levels with the
incorporation of mitigation measures (Attachment B).
Environmental topics analyzed in the DEIR include:
1. Aesthetics
2. Air Quality
3. Biological Resources
4. Cultural Resources
5. Energy
6. Geology and Soils
7. Greenhouse Gas Emissions
8. Hazards and Hazardous Materials
9. Hydrology and Water Quality
10. Land Use and Planning
11. Noise
12. Recreation
13. Transportation
14. Tribal Cultural Resources
15. Utilities and Service Systems
16. Wildfire
Following is a summary of each of the topics addresse d in the DEIR:
1. Aesthetics: This DEIR section provides a discussion of the existing visual and
aesthetic resources in the project site and in the surrounding area and evaluates
the potential for changes in visual character that could result from implementation
of the Project. This section also evaluates the potential loss of existing visual
resources, effects on public views and compatibility with existing uses.
The proposed project would not degrade the character or quality of the project site,
nor would it contribute to an overall degradation of the visual character or quality
of the surrounding area. Construction of the project would prevent the hillside from
eroding into the ocean, which would provide long-term improvements for the visual
character of the area. Further, the proposed landslide remediation is consistent
with all applicable General Plan goals and policies governing aesthetics and scenic
quality. The proposed project would also be consistent with all applicable zoning
regulations governing aesthetics and scenic quality on the property.
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Therefore, the proposed project would not substantially degrade the visual
character of the project site or conflict with applicable zoning and other regulations
governing scenic quality, and no mitigation would be required.
2. Air Quality: This DEIR section discusses existing air quality, summarizes existing
air quality regulations, and evaluates potential air quality impacts associated with
the proposed project. This section also summarizes the pertinent information and
findings provided in the Air Quality, Energy, and Greenhouse Gas Emissions
Analysis.
Air pollution is inherently a cumulative impact measured across an air basin. The
DEIR includes an analysis of the proposed project’s contribution to cumulative air
impacts. The incremental effects of projects that do not exceed the project-specific
thresholds are generally not considered to be cumulatively considerable per the
South Coast Air Quality Management District (SCAQMD) guidelines. The
proposed project’s construction-related regional daily emissions are less than the
SCAQMD significance thresholds for all criteria pollutants. In addition, adherence
to SCAQMD rules and regulations would substantially reduce potential impa cts
associated with the related cumulative projects and Basin-wide air pollutant
emissions.
Therefore, the proposed project would not have a cumulatively considerable
increase in emissions, the proposed project’s cumulative air quality impacts would
be less than significant, and no mitigation is required.
3. Biological Resources: This DEIR section provides a discussion of the existing
biological resources within the boundaries of the proposed project site and
provides an analysis of potential impacts to biological resources from
implementation of the project. Where impacts are identified, mitigation measures
pursuant to CEQA, the state and federal Endangered Species Acts (CESA and
FESA, respectively), the City’s Natural Communities and Conservation
Plan/Habitat Conservation Plan (NCCCP/HCP) and other pertinent regulations are
recommended.
The Biological Survey Area footprint is approximately 206.5 acres, of which 104
acres are in the Portuguese Bend Reserve and Abalone Cove Reserve; all
biological resources were noted and mapped.
Noted vegetation within the Biological Survey Area includes the following:
• Coastal Sage Scrub – Undifferentiated
• Coastal Sage Scrub – Rhus-Dominated
• Saltbrush Scrub
• Disturbed Vegetation
• Exotic Woodland
• Developed
• Rocky Shore
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Six soil types are known to occur withing and/or adjacent to the site:
• Haploxerepts Soil (10-35% slopes)
• Zaca-Ballast Complex (10-50% slopes)
• Urban Land-Filiorum Complex (2-9% slopes)
• Urban Land-Dapplegray Complex (5-20% slopes, terraced)
• Urban Land-Dapplegray Complex (20-55% slopes)
• Beaches and Rocky Soils
Special-status plants that have a moderate potential to occur within the Biological
Survey Area:
• Coulter’s Saltbush (Atriplex coulteri)
• Island Green Dudleya (Dudleya virens subsp. insularis)
• Parish’s Brittlescale (Atriplex parishii)
• Mesa Horkelia (Horkelia cuneata var. puberula)
• Brand’s Star Phacelia (Phacelia stellaris)
Special-status plants that have a high potential to occur within the Biological
Survey Area:
• Aphanisma (Aphanisma blitoides)
• South Coast Saltscale (Atriplex pacifica)
• Santa Catalina Island Desert-thorn (Lycium brevipes var. hassei)
Special-status animals that have a moderate potential to occur within the Biological
Survey Area:
• Coast Horned Lizard (Phrynosoma blainvillii)
Animal species that have a high potential to occur within the Biological Survey
Area:
• San Diego Desert Woodrat (Neotoma lepida intermedia)
• Palos Verdes Blue Butterfly (Glaucopsyche lygdamus palosverdesensis)
• Coastal California Gnatcatcher (Polioptila californica californica)
Three National Wetlands Inventory mapped bluelines and National Hydrography
Dataset streams occur within the Biological Survey Area. All three drainages are
ephemeral; they only support surface flows during and immediately after rain
events. No potential wetlands or riparian habitat areas were observed within the
Biological Survey Area.
The methodology included a literature review and records search to identify the
existence and potential for occurrence of sensitive or special-status plant and
animal species in the project vicinity. Federal and state lists of sensitive species
were also examined. In addition to the database searches, historic and current
aerial imagery, soil maps for Los Angeles County, the U.S. Department of
Agriculture (USDA) Natural Resources Conservation Service (NRCS) Web Soil
Survey, and regional HCPs and local land use policies related to biological
resources were reviewed.
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After the literature review and records search, a general project site biological
reconnaissance survey (field investigation) was conducted. The entire project site
was surveyed on foot, and all biological resources were noted and mapped.
Suitable habitat for any species of interest or concern was duly noted, and general
site conditions were photographed. A delineation of potential jurisdictional aquatic
resource areas within the project site was conducted by qualified biologists.
Plants: No special-status plants have been determined to be present on the project
site. While special-status plant species are not expected within the project impact
areas, a mitigation measure requires an appropriately timed, focused plant survey,
which should be conducted within the final project work areas in May/June to
capture the appropriate blooming periods for these species. Pursuant to the City’s
NCCP/HCP, if an existing population will be impacted by projects or activities that
are covered by the NCCP/HCP, a habitat restoration plan will be prepared and
implemented in accordance with the appropriate regulations. There is a potential
for temporary indirect effects to water quality during construction, which could lead
to habitat degradation. However, implementation of regulatory compliance
measures and mitigation measures would effectively mitigate potential impacts on
special-status wildlife plant and animal species to less than significant levels.
A total of three ephemeral drainages vegetated with upland plant species (e.g.,
nonwetland, nonriparian) were delineated within the Biological Survey Area. In
addition, upland-vegetated swales, existing corrugated metal pipes, and culverts
were also delineated. No vernal pools, wetlands, or riparian habitats were identified
within the Biological Survey Area, and the project would not impact any of these
resources.
Wetlands: There are no state or federal wetlands within the Biological Survey Area.
Additionally, based on the current design, the proposed swale feature is
approximately 20 feet wide, with 10 feet of temporary impacts on either side of the
feature, for a total of 40 feet. Temporary work areas outside of the geocell limits of
the proposed swale feature (but within the construction disturbance limits) will be
covered with biodegradable erosion control matting and hydroseeded with native
vegetation after grading activities. Overall, the proposed project features that will
be implemented at the project site will assist with stabilization of slopes and
drainages, along with conversion of pipe culverts to open swales. This will
ultimately benefit the native habitats in the area, which are being disturbed by the
landslide and associated alteration of drainages, erosion, and more.
Wildlife: There are no designated wildlife corridors or wildlife nurseries on the
project site where landslide remediation and associated drainage improvements
are proposed. Given the project site’s isolated and disturbed nature, the site most
likely minimally serves as an important corridor for animals moving locally,
regionally, or in broader migrations. Migratory bird species may utilize the project
site for foraging. However, the usage is likely transient and limited to species that
forage over open grassland areas. Additionally, the project site does not possess
any characteristics that would indicate a locally significant stopover point for
migratory species, including raptors or waterfowl. No known wildlife movement
corridors occur within the project site. Further, the project would not place any
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permanent barriers to wildlife movement within any corridors, nor would it
permanently disrupt or impede the movement of any wildlife species within the
project area.
The wildlife species that occur in the project vicinity and utilize the project area as
a movement corridor are adapted to the urban-wildland interface, and the project
would not introduce new effects to the area. The noise, vibration, light, dust, or
human disturbance within the construction areas would only temporarily deter
wildlife from using areas in the immediate vicinity of construction activities. These
indirect effects could temporarily alter migration behavio rs, territories, or foraging
habitats in select areas. However, because these are temporary effects, it is likely
that wildlife already living and moving in close proximity to urban development
would alter their normal functions for the duration of the project construction and
then reestablish these functions once all temporary construction effects have been
removed.
Nevertheless, the project site contains suitable nesting habitat for ground-nesting
birds and for other birds that are protected under the Cal ifornia Fish and Game
Code. The proposed project has the potential to impact active native bird nests if
construction or demolition activities occur during the nesting and flight season.
Therefore, vegetation clearing activities should be conducted outside the bird
breeding seasons (February 15- August 31) to minimize the overall impact to listed
species, nesting habitat, host plants, and/or nectar sources. Mitigation measures
require a qualified biologist to conduct preconstruction surveys for the Californ ia
gnatcatcher if construction occurs within its breeding season. Mitigation measures
require pre-construction surveys for the host plant in all suitable habitat within the
proposed project impact areas. With implementation of these mitigation measures,
potential impacts to nesting birds would be less than significant.
The PBL Remediation project is a covered project under the City’s NCCP/HCP;
which is a regional planning document, the goal of which is to allow appropriate
development/projects to take place while providing regional protection of sensitive
species and their habitats. The Project is located within the designated boundaries
of the NCCP/HCP, and each proposed Project component falls within a covered
activity under the NCCP/HCP. Specifically, the Project components fall under the
following covered activities:
• Landslide Abatement Measures (Section 5.2.3 of the NCCP/HCP),
• Dewatering Wells (Section 5.2.2 of the NCCP/HCP), and;
• Miscellaneous Drainage Repair in Landslide Areas (Section 5.2.4 of the
NCCP/HCP).
Collectively, these covered activities authorize up to 12.5 acres of permanent
impacts to coastal sage scrub (CSS) habitat within the Preserve. The maximum
CSS acreage that will be permanently impacted by the Project is 6.34 acres, which
is within the City’s remaining take allowances for each NCCP/HCP covered
activity. Permanent impacts to CSS associated with the project have therefore
been pre-mitigated by the establishment and management of over 1,500 acres of
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NCCP/HCP Preserve lands. Table 5-1 of the NCCP/HCP shows the total habitat
loss allowed for each included City project.
Impacts to habitat within the City-owned Palos Verdes Nature Preserve must be
avoided and minimized consistent with Section 5.5 of the NCCP/HCP. The plan
ensures appropriate definition of temporary and permanent impacts to native
vegetation and provides a clear definition of how project components could hinder
restoration of native habitat. For example, introduction of impervious surfaces into
a natural landscape and the fracture filling may alter surface flow patterns and lead
to localized erosion around the filled fractures, which may damage surrounding
vegetation. Therefore, strict adherence to the NCCP/HCP ensures the best
possible outcome.
The proposed project and all related projects are required to adhere to City
regulations designed to reduce and/or avoid impacts related to biological
resources. Mitigation measures have been added to alleviate any long -term
impacts. With compliance with these mitigation measures and regulations, impacts
related to biological resources would be less than cumulatively significant.
Therefore, implementation of the proposed project would not result in a significant
cumulative impact related to biological resources.
4. Cultural Resources: This DEIR section evaluates the potential for the proposed
project to impact cultural resources. Cultural resources are prehistoric and historic
archaeological artifacts, features, and sites, and historic buildings, structures,
objects, and districts over 50 years old.
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The cumulative impact area for cultural resources for the proposed project is the
City of Rancho Palos Verdes. Potential impacts of the proposed project to
unknown cultural resources, when combined with the impacts of past, present, and
reasonably foreseeable projects in Rancho Palos Verdes, could contribute to a
cumulatively significant impact due to the overall loss of archaeological artifacts
and cultural remains unique to the region. However, if there were any potential for
significant impacts to archaeological resources, an investigation would be required
to determine the nature and extent of the resources and identify appropriate
mitigation measures. When resources are assessed and/or protected as they are
discovered, impacts to these resources are less than significant.
As such, implementation of Regulatory Compliance Measures (RCM) and
Mitigation Measures (MM) would ensure that the proposed project, together with
cumulative projects, would not result in a significant cumulative impact to unique
archaeological resources and previously undiscovered buried human remains.
5. Energy: This DEIR section discusses energy use resulting from implementation of
the proposed project and evaluates whether the proposed project would result in
the wasteful, inefficient, or unnecessary consumption of energy resources or
conflict with any applicable plans for renewable energy and energy efficiency .
Electricity and natural gas in the Project’s geographic area is provided by Southern
California Edison (SCE) and Southern California Gas Company (SoCalGas). The
proposed project would result in increased service demand for electricity and
petroleum during construction. Although the proposed project would result in a net
increase in electricity use, this increase would not require SCE to expand or
construct infrastructure that could cause substantial environmental impacts. The
proposed project’s percentage of the cumulative future potential energy
consumption increase in the service area would be negligible. The proposed
project, in combination with cumulative development, is well within SCE’s
systemwide net annual increase in electricity supplies over the 2020- 2030 period,
and there are sufficient planned electricity supplies in the region for estimated net
increases in energy demands.
Additional natural gas infrastructure is not required because the proposed project
would not utilize natural gas as an energy source.
Transportation energy use would also increase . However, this transportation
energy use would not represent a major amount of energy use when compared to
the amount of existing development and the total number of vehicle trips and
vehicle miles travelled throughout Los Angeles County and the region.
Therefore, the proposed project’s contribution to impacts related to the inefficient,
wasteful, and unnecessary consumption of energy would not be cumulatively
considerable, and no mitigation is required.
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6. Geology And Soils: This DEIR section provides a discussion of the existing
geologic and soils environment and an analysis of potential impacts from
implementation of the proposed project. This section also addresses the potential
for structural damage due to the local geology underlying the project site, as well
as slope stability, ground settlement, soil conditions, grading, and regional seismic
conditions. In addition, this section analyzes the potential for the proposed project
to affect unknown paleontological resources on or within the project vicinity.
The project site was studied from a big-picture view to a small, detailed view. This
included regional (Los Angeles Basin, Southwestern Block); local (Palos Verdes
Hills on the Upper Altamira Shale member of the Monterey Formation); soil
(expansive surface soils containing clay); soil collapse (often found in young
alluvial deposits); groundwater conditions (shallow groundwater zone); seismicity
and faulting (Cabrillo Fault, Palos Verdes Fault, Newport -Inglewood Fault, and a
system of interconnected, closely spaced planar fractures stretching from Santa
Monica Bay to the waters off Dana Point); subsidence (sinking or settling);
liquefaction (sudden loss in strength of a saturated, cohesionless soil caused by
buildup of water pressure); seismic generated tsunami; slope instability and
seismically induced landslide; and flood hazard.
To assess the project impacts with respect to geologic and soil conditions, a
geological, geotechnical, and hydrogeological review was conducted. The scope
of the report included background review and review of readily available, publicly
published references.
Additionally for paleontological resources, a records search was conducted
through the Natural History Museum of Los Angeles County (LACM). Then, a
pedestrian survey was performed by a paleontological surveyor, which consisted
of systematic surface inspection with transects at 10-meter intervals to ensure that
any evidence of paleontological resources could be identified. In addition to the
surface inspection, any safely accessible cliffsides and exposed subsurface
profiles were investigated for any evidence of paleontological resources.
The PBL, a component of the City’s ancient landslide complex, is an ancient
landslide mass that shows possible signs of movement as far back as 120,000 to
800,000 years ago. Specifically, a change in ground water content has had a great
effect on the properties of the Palos Verdes bentonite, and doubling the moisture
content decreases the unconfined shear strength more than tenfold.
The proposed project would minimize PBL movement by implementing a series of
geotechnical engineering solutions to relieve artesian pressure below the landslide
basal surface and minimize stormwater infiltration into the subsurface. The
objective of implementing these solutions would be to reduce substantial human
health risks and improve public safety, reduce the likelihood of major landslide
movement that would potentially damage and render Palos Verdes Drive South
unusable, and alleviate artesian water pressure below the PBL area, a major
contributing factor to landslide movement.
The project site is currently vacant with vegetation and exposed soil. During
grading and construction, soil would be exposed and there would be an increased
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potential for soil erosion compared to existing conditions due to soil disturbance
and the exposure of substantial amounts of soil to weather conditions (e.g., wind,
rain). During a storm event, soil erosion could occur at an accelerated rate. The
increased erosion potential would result in short-term water quality impacts.
Because the project would disturb greater than 1 acre of soil, the project is subject
to the requirements of the State Water Resources Control Board’s (SWRCB)
National Pollutant Discharge Elimination System (NPDES) General Permit for
Storm Water Discharges Associated with Construction and Land Disturbance
Activities. The Construction General Permit requires preparation of a Storm Water
Pollution Prevention Plan (SWPPP) and implementation of construction Best
Management Practices (BMP). The construction contractor would be required to
prepare and implement the SWPPP and associated BMPs in compliance with the
Construction General Permit (CGP) during grading and construction. Adherence
to the BMPs in the SWPPP would reduce, prevent, or minimize soil erosion from
future project-related grading and construction activities. Additionally, the
preparation and implementation of an Erosion Control Plan would require the
project proponent to comply with City grading permit regulations and inspections
to reduce sedimentation and erosion.
The majority of the site is within pervious areas where water is anticipated to
percolate into the ground, while excess runoff sheet flow s from northeast to
southwest, discharging to the Pacific Ocean. A Final Hydrology and Hydraulics
Analysis will be prepared and submitted to the City for approval to ensure the peak
flow of stormwater runoff in the proposed condition would not exceed the outfall
capacity. As a result, any increase in peak discharge would be negligible.
Therefore, the proposed project would not result in substa ntial soil erosion or the
loss of topsoil.
For geology and soils, the cumulative study area consists of the area that could be
affected by the proposed project activities and other areas that are affected by the
Portuguese Bend Area Landslides. Specifically, this encompasses the areas under
the Rancho Palos Verdes Landslide Moratorium, where construction of new
structures or buildings is prohibited unless they meet the criteria for an exception.
The analysis indicated no rare or special geological features or soil types on the
project site that would be affected by project activities and no other known activities
or projects with activities that affect the geology and soils of this site. In addition,
the proposed project would be required to comply with the applicable state and
local requirements, including the City of Rancho Palos Verdes Building Code.
Compliance with RCMs for the proposed project would ensure that cumulative
impacts to geology and soils would be less than significant. Therefore, the project’s
contribution to cumulative geotechnical and soil impacts is less than cumulatively
significant.
For paleontological resources, the cumulative study area is the geographical area
of the City, which is the geographical area covered by the City’s General Plan,
including all goals and policies included therein. Future development in the City
could include excavation and grading that could potentially affect paleontological
resources. The cumulative effect of the proposed project is the excavation and
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grading that could potentially affect paleontological resources. With the mitigation
measures, cumulative impacts to paleontological resources would be less than
significant. If subsurface cultural resources are assessed and/or protected as they
are discovered, impacts to these resources would be less than cumulatively
significant. Therefore, the project’s contribution to the destruction of known and
unknown paleontological resources throughout the City would be less than
cumulatively significant.
7. Greenhouse Gas Emissions: This DEIR section provides a discussion of global
climate change (GCC), existing regulations pertaining to GCC, and an analysis of
greenhouse gas (GHG) emissions associated with the proposed project.
GHG emissions are global pollutants, and therefore, result in cumulative impacts
by nature. Consequently, it is speculative to determine how an individual project’s
GHG emissions would impact California. As such, impacts are not project -specific
impacts to GCC, but are the proposed project’s contribution to cumulative GCC
impact.
The impact of project-related GHG emissions would not result in a reasonably
foreseeable cumulatively considerable contribution to GCC. Additionally, the
proposed project, in conjunction with other cumulative projects, would be subject
to all applicable regulatory requirements, which would further reduce GHG
emissions.
Therefore, the project’s cumulative contribution of GHG emissions would be less
than significant and the project’s cumulative GHG impacts would also be less than
cumulatively considerable.
8. Hazards And Hazardous Materials: This section addresses potential hazards and
hazardous material impacts at the project site and in the surrounding area that may
result from implementation of the proposed project.
The cumulative impact area for hazards and hazardous materials related to the
proposed project is the City of Rancho Palos Verdes.
The proposed project’s construction activities would temporarily use hazardous
materials typical of construction such as equipment fuel, but not materials
classified as acutely hazardous. Storage, handling, use, and disposal of these
materials would require compliance with laws and regulations.
Operation and maintenance of the project would require use of hazardous
materials typical of construction, but only in small quantities, and in compliance
with laws and regulations.
The proposed project is not expected to substantially impair an adopted
emergency response or evacuation plan because the designated disaster route,
Palos Verdes Drive South, would only be affected temporarily during limited hours
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and with implementation of a traffic control plan that ensures adequate emergency
access is maintained. Moreover, project implementation improves emergency
access because controlling landslide movement reduces impacts to and the
potential closure of Palos Verdes Drive South.
Although the number of people temporarily present at the project site, which is a
state-designated Very High Fire Hazard Severity Zone, would increase,
implementation of the required traffic control plan ensures that emergency access
is maintained. The proposed project does not otherwise increase the risk of wildfire
in the area.
Therefore, with compliance with laws and regulations, implementation of the
proposed project would not result in significant cumulative impacts related to
hazards and hazardous materials.
9. Hydrology and Water Quality: This DEIR section evaluates the potential impacts
to hydrology and water quality conditions from implementation of the proposed
project.
The cumulative impact area for hydrology and water quality for the proposed
project is the South Santa Monica Bay Watershed.
New development and redevelopment can result in increased stormwater runoff
and increased urban pollutants in stormwater runoff from project sites. Projects
must include BMPs to reduce impacts to water quality and hydrology in compliance
with local ordinances and NPDES permit requirements. Specifically, the Project
must develop and comply with the requirements of a CGP (because it disturbs 1
acre or more of soil during construction), the Los Angeles County Municipal
Separate Storm Sewer System (MS4) Permit, and the Rancho Palos Verdes
Municipal Code. The preparation, approval, and implementation of a project-
specific SWPPP consisting of stormwater control measures during construction
will be required to minimize water quality impacts. Additionally, stormwater control
measures will be required to minimize increases in runoff so they do not exceed
regulatory requirements or the capacity of downstream storm drain system.
The project must also consider impaired receiving waters and Total Maximum
Daily Loads (TMDL) of pollutants for receiving waters. The TMDL program is
designed to identify all constituents that adversely affect the beneficial uses of
water bodies and then identify appropriate reductions in pollutant loads or
concentrations from all sources so that the receiving waters can maintain/attain
the beneficial uses in the Los Angeles Regional Water Quality Control Board Basin
Plan. Thus, by complying with TMDLs, the project will comply with overall water
quality regulatory requirements for the South Santa Monica Bay Watershed.
Because the proposed project would comply with the CGP and the Los Angeles
County MS4 Permit, implement construction and operational BMPs pursuant to a
SWPPP, and implement storm water control measures to reduce the volume of
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stormwater runoff and pollutants of concern in stormwater runoff, the cumulative
hydrology and water quality impacts of the proposed project a would be less than
significant.
Therefore, the proposed project’s incremental hydrology and water quality impacts
would not be cumulatively considerable.
10. Land Use and Planning: This DEIR section analyzes the existing land uses on the
project site and in its vicinity, as well as the consistency of the proposed project
with surrounding land uses and the relevant policy and planning documents.
Because the proposed project does not consist of any new development and will
not result in changes to existing uses on the project site, the land uses would
remain consistent with General Plan land use designations. Additionally, the
proposed project will require a Grading Permit and Coastal Development Permit
pursuant to the Rancho Palos Verdes Municipal Code (RPVMC), and any policy,
ordinance, or regulation adopted by the City, including the agreement between the
City and Coastal Commission. The Project is in the City Council’s jurisdiction
pursuant to Chapter 17.79 of the RPVMC.
The proposed project and all related projects are required to adhere to City
regulations designed to reduce and/or avoid impacts related to land use and
planning, particularly hazards. With compliance with these regulations, impacts
related to land use and planning would be less than cumulatively significant.
Therefore, implementation of the proposed project would not result in a significant
cumulative impact related to land use and planning.
11. Noise: This DEIR section evaluates the potential short-term and long-term noise
impacts associated with the construction and maintenance of the proposed
Project. A cumulative noise or vibration impact would occur if multiple sources of
noise and vibration combine to create impacts in close proximity to a sensitive
receptor.
The cumulative impact area for noise related to the proposed project is the
immediately surrounding area.
Noise impacts from on-site activities associated with the project would be a
function of the noise generated by construction equipment based on equipment
location, sensitivity of nearby land uses, and the timing and duration of construction
activities. Construction activities are expected to occur Monday through Friday
between 7 a.m. and 6 p.m. and Saturdays between 9 a.m. and 5 p.m.
Construction noise impacts to the nearest homes were calculated according to
equipment noise levels and usage factors define d by the Federal Highway Agency
(FHWA) Roadway Construction Noise Model. The proposed project would not
generate a substantial temporary or permanent increase in ambient noise levels in
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the project vicinity exceeding the standards established in the General Plan or
Noise Ordinance.
Construction activity can also result in varying degrees of ground vibration,
depending on the equipment used and the distance for receptors. Construction -
related vibration impacts for various types of equipment were calculated based on
measurements published by the Federal Transit Administration. Vibration impacts
from the proposed project would be created from the operation of heavy off -road
equipment. The proposed project would not expose persons to generation of
ground-borne vibration or ground-borne noise levels above the FHWA thresholds.
The proposed project and all related projects are required to adhere to City
regulations designed to reduce and/or avoid impacts related to noise. Regulatory
compliance measures require the contractor to adhere to the limitation of allowable
construction times provided in Section 17.56.020 of the City’s Municipal Code.
With compliance with regulations, impacts related to noise would be less than
cumulatively significant. The hydrauger system will be implemented during
construction to extract groundwater, relieve artesian pressure, and slow down the
landslide. The Engineer-of-Record and the team monitoring the groundwater
extraction process will determine the frequency required to pump groundwater and
control/minimize any noise issues related to the water extraction process during
and after construction.
Therefore, implementation of the proposed project would not result in a significant
cumulative impact related to noise.
12. Recreation: This DEIR section analyzes the potential recreation impacts
associated with implementation of the proposed project. This section also
addresses the proposed impacts to recreation resources with consideration of local
policies.
Implementation of the proposed project would not result in a significant cumulative
impact related to recreation. The proposed project and all related projects are
required to adhere to City regulations designed to reduce and/or avoid impacts
related to recreation. Additionally, any recreation impacts (trail closures) related to
this project will be temporary. Mitigation measures have been added to alleviate
any long-term impacts, such as swale design, trail closure notifications, and trail
repair/maintenance.
With compliance with these mitigation measures and regulations, impacts related
to recreation would be less than cumulatively significant. Therefore,
implementation of the proposed project would not result in a significant cumulative
impact related to recreation.
13. Transportation: This DEIR section analyzes the existing and project construction
transportation and circulation conditions for the proposed project and the
surrounding area, and identifies circulation impacts that may result during project
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implementation. The cumulative impact area for transportation is the City of
Rancho Palos Verdes. The majority of the vehicle trips associated with the
proposed project are temporary and would occur during construction and limited
to the permitted construction hours. Vehicle trips associated with operation,
inspection, and maintenance of the project components would be nominal. Given
the temporary nature of the majority of the project trips, there will be no cumulative
impacts. Additionally, the project will protect important City infrastructure. From a
transportation and circulation perspective, landslide remediation will provide for the
continued operation of Palos Verdes Drive South, an important transportation
circulation link connecting various communities within Rancho Palos Verdes and
beyond, including the San Pedro area and the beach cities in the South Bay . If
Palos Verdes Drive South were inoperable due to landslide activity, vehicle miles
traveled within the City would increase due to residents needing to take circuitous
routes to traverse the City.
14. Tribal Cultural Resources: This DEIR section evaluates the potential for the
proposed project to impact tribal cultural resources. Potential impacts to other
cultural resources, including historic and non-Native American archaeological
resources, are evaluated in the Cultural Resources section of the DEIR.
The cumulative impact area for tribal cultural resources for the proposed project is
the City of Rancho Palos Verdes. Potential impacts of the proposed project to
unknown tribal cultural resources, when combined with the impacts of past,
present, and reasonably foreseeable projects in Rancho Palos Verdes, could
contribute to a cumulatively significant impact due to the overall loss of tribal
cultural remains unique to the region. However, each development proposal
received by the City is required to undergo environmental review pursuant to
CEQA. If there were any potential for significant impacts to tribal cultural resources,
an investigation would be required to determine the nature and extent of the
resources and identify appropriate mitigation measures. When resources are
assessed and/or protected as they are discovered, impacts to these resources are
less than significant.
As such, implementation of tribal cultural resources monitoring and mitigation
measures would ensure that the proposed project, together with cumulative
projects, would not result in a significant cumulative impact to tribal c ultural
resources.
15. Utilities and Service Systems: This DEIR section describes the potential for the
project to require the relocation or construction of new or expanded water,
wastewater treatment, stormwater drainage, electric power, natural gas, or
telecommunications facilities.
The cumulative impact area for utilities and service systems related to the
proposed project is SoCalGas and SCE’s service area.
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Implementation of the proposed project would not result in a significant cumulative
impact related to utilities and service systems. This includes significant
environmental effects as a result of relocation or construction of new or expanded
water, wastewater treatment, or storm water drainage; electrical power; natural
gas, or telecommunication facilities.
The proposed project and all related projects are required to adhere to City
regulations designed to reduce and/or avoid impacts related to utilities and service
systems. Furthermore, the landslide remediation project is designed to control land
movement and protect the integrity of existing utilities and service systems. With
compliance with these regulations, impacts related to utilities and service systems
would be less than cumulatively significant.
Therefore, implementation of the proposed project would not result in a significant
cumulative impact related to utilities and service systems.
16. Wildfire: This DEIR section analyzes the potential wildfire impacts associated with
implementation of the proposed project. This section also addresses the proposed
impacts to wildfire with consideration of local policies.
The cumulative impact area for wildfire related to the proposed project is the City
of Rancho Palos Verdes. The proposed project does not alter the existing wildland
fire conditions on the project site or increase the potential for wildland fires to occur.
Implementation of the proposed project would not result in a significant cumulative
impact related to wildfire. This would include responsibility areas or lands classified
as a state-designated Very High Fire Hazard Severity Zone, and whether the
project would substantially impair an adopted emergency response plan or
emergency evacuation plan. Therefore, implementation of the proposed project
would not result in a significant cumulative impact related to wildfire. Slope,
prevailing winds, and other factors would not exacerbate wildfire risks and thereby
expose project occupants to pollutant concentrations from a wildfire or the
uncontrolled spread of a wildfire; or expose people or structures to significant risks,
including downslope or downstream flooding or landslides, as a result of runoff,
post-fire slope instability, or drainage changes.
It should be noted that project implementation is expected to reduce the likelihood
that land movement could cause electrical lines to contact flammable vegetation
and start a wildfire.
The proposed project and all related projects are required to adhere to City and
state regulations designed to reduce and/or avoid impacts related to wildfire. With
compliance with these regulations, impacts related to wildfire would be less than
cumulatively significant.
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Mitigation and Monitoring Reporting Program
A Mitigation and Monitoring and Reporting Program has been prepared in compliance
with all relevant regulations. It describes the requirements and procedures to be followed
by the City to ensure that all mitigation measures adopted as part of the proposed project
will be carried out as described in this DEIR. Table 7.A in the DEIR identifies each
measure and responsible party (Attachment B).
The following categories have no potentially significant impacts; therefore, no mitigation
is required: aesthetics, air quality, energy, greenhouse gas emissions, hazards and
hazardous materials, hydrology and water quality, land use and planning, noise,
transportation/traffic, utilities and service systems, and wildfire.
For categories that have impacts that require mitigations, specific mitigations are
described in DEIR Table 7.A. These include biological resources, cultural resources,
geology and soils, recreation, and tribal cultural resources. Based on the mitigation
measures, the Project’s potential impacts would be reduced to a less than significant
level.
Project Alternatives
Project alternatives, Section 5 of the DEIR, were considered, including a no-project
alternative, as summarized below.
Alternative 1: The No Project Alternative, would involve no landslide remediation.
No remediation would occur on the project site, the existing condition of the site
would not change, and the project objectives would not be met. The proposed
discretionary actions would not be required. Due to the Landslide Moratorium, the
project site would remain undeveloped. The PBL complex would continue to move
at various rates, displacing the land seaward and continuing to damage utilities
and critical infrastructure.
Alternative 2: Consists of the elimination of the flow-reduction area (detention
basin) from the proposed project elements, but the other elements would be
implemented. Elimination of the flow-reduction basin would result in downstream
erosion and therefore loss of habitat, potential culvert damage that could hinder
traffic circulation, increased downstream velocity, and disruption to utilities. The
project objectives would not be fully met.
Other alternatives considered also did not meet project objectives or were
considered not possible. Other alternatives that were brought up during Notice of
Preparation (NOP) distribution included reducing the number of fissures to be filled
and changing the materials used for the filling, eliminating the drainage swales,
and changing the hydrauger locations. The material that would be used to fill the
fissures has been updated to no longer use fly ash and to instead use a more
appropriate material (i.e., bentonite chips and/or soil). Additionally, the design team
has conducted a fill survey and determined the appropriate number of fissures to
make a meaningful impact on landslide remediation. The design engineers will be
consulted prior to the access/infilling of cracks in sensitive areas to evaluate
whether the requirement for infilling of these cracks can be deleted. Elimination of
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the drainage swales was raised as a consideration for reducing the project
footprint. Eliminating the swales would lead to continued erosion resulting from
unmanaged run-off and drainage flows, which would impact sensitive habitats and
reduce the likelihood of an increase in the functions and values of existing water
resources, as well as result in water runoff percolation into the ground. As for
changes to the hydrauger configuration, the locations of the hydraugers moved
several times relative to the original design, and one of the hydrauger locations
was eliminated. The rest of hydraugers were shortened so that they do not
penetrate below private residences or extend beyond the City-owned land. These
amendments to the hydrauger configuration represent the bare minimums needed
to effectively slow the landslide. For the reasons stated above, these other
alternatives are not possible.
ADDITIONAL INFORMATION:
Public Noticing and Public Comments
The DEIR was released for public comment on February 9, 2023. It is available to view in
electronic format on the City’s website and in print format during regular business hours
at Rancho Palos Verdes City Hall, the Miraleste Library in Rancho Palos Verdes, and the
Peninsula Center Library in Rolling Hills Estates. Comments may be submitted in writing
to the Public Works Department at Rancho Palos Verdes City Hall (30940 Hawthorne
Blvd., Rancho Palos Verdes, CA 90275) or via email to publicworks@rpvca.gov by 4:30
p.m. on April 14, 2023.
It should be noted that a corrected Public Notice was published on February 9, 2023,
because of an incorrect email address.
More than 900 residents in the vicinity of the project received a letter with information on
where the DEIR may be viewed, the public comment period, how public comments may
be submitted, and the date and location of the DEIR public hearing.
At the conclusion of the DEIR comment period, all verbal and written comments will be
tabulated, reviewed, assessed, and responded to in the Final EIR. Staff expects to return
to the City Council with a Final EIR for certificat ion consideration after addressing all
comments. Depending on the volume and nature of comments, Staff expect s to return in
the summer of 2023.
Stakeholder Meetings
In advance of the March 21, 2023 City Council meeting, Staff intends to meet with various
stakeholders. Meetings are currently scheduled with members of the following:
• PVPLC
• Sierra Club
• California Native Plant Society
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• Heal the Bay
• Surfrider Foundation
• LA County Safe Clean Water Program
• South Santa Monica Bay Watershed Area Steering Committee
Building Resilient Infrastructure and Communities (BRIC) Grant
The proposed project is estimated to cost approximately $33 million. This cost was based
on projections estimated in 2019 and increased to factor cost of living adjustments
(COLA) and construction escalation and contingency, among other things.
Concurrently with the DEIR development, the City submitted an application to the Federal
Emergency Management Agency (FEMA) for a Building Res ilient Infrastructure and
Communities (BRIC) grant for $23.3 million, with a required non-federal match of $10
million. The grant application requires that the EIR be certified before approving grant
funds. If awarded, the FEMA funds will be available for this project on October 2, 2023,
assuming the EIR is certified.
CONCLUSION:
The DEIR was prepared to analyze the proposed project’s potential impacts on the
environment; to propose mitigation measures for identified potentially significant impacts
that would minimize, offset, or otherwise reduce or avoid those environmental impacts;
and to discuss alternatives that could reduce the potentially significant impacts of the
proposed project based on the identified objectives noted at the beginning of this st aff
report.
The DEIR concludes that project implementation would not result in any impacts that are
considered significant, adverse, and unavoidable. All environmental issues analyzed in
this DEIR were determined to result in less than significant impacts, or can be reduced to
less than significant levels with the incorporation of mitigation measures.
The habitat loss resulting from the Project was anticipated and accounted for in the City’s
NCCP/HCP, which allows the loss of habitat for certain City proj ects, provided that
avoidance and minimization measures for sensitive habitats and species are
implemented. The habitat loss accounted for in the NCCP/HCP is offset by the creation
of the City’s 1,500-acre Preserve. The Preserve and the perpetual preservation and
restoration of protected habitat essentially serve as the mitigation for permanent impacts
associated with these City projects, including the landslide project.
The purpose for today’s City Council meeting is to conduct a public hearing and receive
public comments, and comments from the City Council, on the PBL Remediation Project
DEIR.
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ALTERNATIVES:
In addition to Staff recommendations, the following alternative actions are available for
the City Council’s consideration:
1. Take other action, as deemed appropriate.
2. Direct Staff to stop work on the DEIR, which would essentially stop work on the
proposed project.
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D RAFT E NVIRONMENTAL I MPACT R EPORT
F EBRUARY 2023
P ORTUGUESE B END L ANDSLIDE R EMEDIATION P ROJECT
R ANCHO P ALOS V ERDES, C ALIFORNIA
P:\PVE2202 - Portuguese Bend\DEIR\To City of RPV\From City\Revisions\7.0 MMRP_AM_LSA.docx (02/08/23) 7-3
Table 7.A: Mitigation and Monitoring Reporting Program
Mitigation Measures Responsible Party
Timing for
Mitigation
Measures
4.1: Aesthetics
There are no potentially significant impacts related to aesthetics; therefore, no mitigation is required.
4.2: Air Quality
There are no potentially significant impacts related to air quality; therefore, no mitigation is required.
4.3: Biological Resources
BIO-1 Focused Plant Survey. Prior to construction, a focused plant survey should be conducted within the final
project work areas for the following species: aphanisma, Brand’s star phacelia, Coulter’s saltbush, mesa
horkelia, Parish’s brittlescale, Santa Catalina Island desert-thorn, and south coast saltscale. Surveys should be
conducted in May/June to capture the appropriate blooming periods for these species. If an existing
population will be impacted by covered projects/activities, the project applicant will engage the Palos Verdes
Peninsula Land Conservancy (PVPLC), the City’s Palos Verdes Nature Preserve (Preserve) Habitat Manager, and
work with the Wildlife Agencies to prepare and implement a habitat restoration plan in accordance with the
habitat restoration plan guidelines in Section 7.5 of the Natural Communities Conservation Plan/Habitat
Conservation Plan (NCCP/HCP), to be approved by the City and Wildlife Agencies, that will ensure no net loss
of listed species within the population. If listed special-status plant species are found, the compensatory
mitigation plan must also be approved by the United States Fish and Wildlife Service (USFWS) and/or the
California Department of Fish and Wildlife (CDFW), as applicable.
City of Rancho Palos
Verdes and/or Project
Contractor
Prior to
construction, in
May/June
BIO-2 Pre-construction Nesting Bird Surveys. If vegetation removal, construction, or grading activities are planned
to occur within California gnatcatcher habitat during its breeding season (February 15–August 31), a pre-
construction survey will be conducted to determine nesting activity. The Community Development Director,
or designee, shall confirm that the City has retained a qualified biologist (USFWS and CDFW will be provided a
10-day period to approve the proposed biologist; if no response from USFWS and CDFW is received within 10
days, approval will be waived), who shall conduct a pre-construction nesting bird survey no more than 3 days
prior to the start of such activities. Survey results will be submitted to the Wildlife Agencies for review and
approval. If comments are not received in 10 days, the approval requirement will be waived. If nesting activity
is detected, all construction activity must occur outside of a 300-foot buffer surrounding each nest.
Reductions in the nest buffer may be possible depending on site-specific factors, in coordination with the
Wildlife Agencies. The appropriate buffer shall be determined by the qualified biologist based on species,
location, and the nature of the proposed activities. Project activities shall be avoided within the buffer zone
until the nest is deemed no longer active, as determined by the qualified biologist.
City of Rancho Palos
Verdes and/or Project
Contractor
No more than
3 days prior to the
start of vegetation
removal,
construction, or
grading activities
planned to occur
from February 15 to
August 31.
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BIO-3 Worker Environmental Awareness Program (WEAP) Training. Prior to commencing construction, the City’s
Community Development Director, or designee, shall confirm that a Worker Environmental Awareness
Program training shall be conducted by the City-approved qualified biologist to include the following: (1) the
potential presence of covered species and their habitats, (2) the requirements and boundaries of the project,
(3) the importance of complying with avoidance and minimization measures, (4) environmentally responsible
construction practices, (5) identification of sensitive resource areas in the field, and (6) problem reporting and
resolution methods. Training construction crews on special-status species identification and applicable
standards and regulations would help avoid impacts to special-status species that are known to occur in
habitats adjacent to the Project Site by identifying those areas where special-status species have potential to
be present and specifying procedures that would be implemented to avoid impacts to such species. This
training is intended educate all construction personnel on the relevant federal, State, and local laws related to
regional special-status species known to occur in adjacent habitat types, particularly habitat associated with
the Preserve. The training session shall include training on identification of species that may be found on or
adjacent to the Project Site, the status of those species, and any legal protection afforded to those species.
Measures that are being implemented to protect those species shall also be explained. Personnel shall be
advised to report any special-status species promptly to the construction manager.
City’s Community
Development Director,
or designee
Prior to the
groundbreaking
BIO-4 Construction Site Housekeeping. Impacts to habitat subject to permanent and temporary construction
disturbances and other types of ongoing project-related disturbance activities shall be minimized by adhering
to the following avoidance and minimization measures, in accordance with the City’s NCCP/HCP for the
duration of construction activities:
Construction staging areas will be located at least 15 meters (50 feet) away from the Preserve boundary
and natural drainages. No-fueling zones will extend a minimum distance of 15 meters (50 feet) from all
drainages and away from the Preserve boundary.
Temporary impacts to native vegetation will be restored with native vegetation appropriate to the physical
condition of the site within 60 days of the completion of construction.
Project-related vehicles shall observe a daytime speed limit of 10 miles per hour (mph) throughout the
project site. Nighttime construction is not permitted unless the City Manager determining that nighttime
work is necessary to address public health and safety concerns. Off-road traffic outside of designated
project sites shall be prohibited.
To prevent inadvertent entrapment of animals during the construction phase of a project, all excavated,
steep-walled holes or trenches more than 2 feet deep shall be covered at the close of each working day by
plywood or similar materials. If the trenches cannot be closed, one or more escape ramps constructed of
Project Contractor During construction
activities
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earthen fill or wooden planks shall be installed. Before such holes or trenches are filled, they shall be
thoroughly inspected for trapped animals. In the case of trapped animals, escape ramps or structures shall
be installed immediately to allow the animal(s) to escape.
For the duration of construction activities, all food-related trash items such as wrappers, cans, bottles, and
food scraps shall be disposed of in securely closed containers and removed at least daily from the
construction site.
Pets, such as dogs or cats, shall not be permitted on the Project Site during construction to prevent
harassment, injury, or death of wildlife in the project vicinity.
Use of rodenticides and herbicides on project sites shall be restricted to prevent primary or secondary
poisoning of predators and the depletion of prey populations on which they depend. All uses of such
compounds shall observe label and other restrictions mandated by the United States Environmental
Protection Agency, the California Department of Food and Agriculture, and other State and federal
legislation.
BIO-5
Erosion Control and Amphibian Exclusionary Fencing. Grading and construction resulting in ground
disturbance shall occur within the typical dry season (April 15–October 15), as feasible, to avoid erosion and
sedimentation impacts to nearby creeks and water quality. Prior to commencing construction, the City’s
Community Development Director, or designee, shall verify that project plans require the project contractor
to install adequate erosion and sedimentation barriers (e.g., silt fencing, as described below) prior to ground
disturbance to prevent any sediment-laden runoff or debris from entering adjacent waterways or the Pacific
Ocean during the wet season or periods of rain. This silt fencing shall also serve as a temporary barrier to
further minimize the potential for special-status amphibians and other wildlife to enter work areas during
construction. The barriers shall consist of 3-foot-tall silt fencing buried to a depth of at least 6 inches below
the soil surface along the outer limits of all work areas (or as otherwise required by the stormwater pollution
and prevention plan (Stormwater Pollution Prevention Plan [SWPPP and BMPs) These barriers shall be
inspected daily by construction personnel and maintained and repaired as necessary for the duration of
construction to ensure they are functional and are not a hazard to wildlife on the outer side of the fence. A
City approved qualified biologist shall monitor all fence installation. All barriers shall be removed following
completion of construction.
City’s Community
Development Director,
or designee
Prior to
commencing
construction
(ground
disturbance)
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BIO-6 Defining Construction Staging Areas and Regulating Access to the Preserve. During construction, it is
required that the construction footprint be clearly defined with flagging and/or fencing, which will be
removed upon completion. Additionally, when accessing the Preserve, authorized vehicle operators shall take
measures to avoid and minimize, to the maximum extent possible, environmental damage, including damage
to habitat and covered species. Existing Preserve roads or trails that accommodate authorized vehicles in the
Preserve should be used wherever practical while minimizing authorized vehicle trips overall within the
Preserve. Any unavoidable access routes outside existing trails that can accommodate authorized vehicles or
construction areas should be clearly marked. Any new recreational trails, trails that can accommodate
authorized vehicles, and utility corridors will be located in areas that avoid/minimize impacts to covered
species, habitat fragmentation, and edge effects. The width of construction corridors and easements shall be
reviewed and approved by the City prior to use, and said footprint shall be minimized to the maximum extent
possible.
Project Contractor During construction
BIO-7 Coastal Sage Scrub (CSS) Restoration Program. In order to ensure the best effort to minimize any potential
impacts to the CSS habitat present in the project area, the City shall retain a qualified biologist to develop a
project-specific restoration program for CSS and Saltbush Scrub according to the guidelines provided in
Section 7.5 of the NCCP/HCP. The restoration plan shall also address the native planting to occur within the
swales and low-flow reduction area. Both project components will be lined with geofabric conducive to
planting of native material. Prior to selecting appropriate planting material, the City will consult with the
PVPLC regarding the native plant mix and source for obtaining native plants and seeds. Temporary impacts to
native vegetation will be restored with native vegetation appropriate to the physical condition of the site
within 60 days of the completion of construction
City of Rancho Palos
Verdes
Within 60 days of
the completion of
construction
BIO-8 Pre-construction Palos Verdes Blue Butterfly Surveys. If vegetation removal, construction, or grading
activities are planned to occur within the flight season of the Palos Verdes blue butterfly (PVB) (late January
through early May), a pre-construction survey will be conducted to determine the presence of any PVB host
plants in all suitable habitat within the proposed project impact areas. If host plants are identified, a 5-foot
buffer around the host plants will be avoided if feasible. If avoidance of host plants is not feasible, focused
PVB surveys will be conducted. If PVB is discovered during surveys, the PVPLC, in coordination with the
Wildlife Agencies, will be provided the opportunity to relocate any and all larvae, pupae, or adults. Occupied
PVB host plants will be avoided when possible. Occupied habitat will be defined as host plants, including a 5-
foot buffer, within a 50-foot buffer around any PVB observation.
City of Rancho Palos
Verdes and/or project
contractor
Prior to
commencing
construction
(ground
disturbance)
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BIO-9 Mitigation Measure MM-BIO-9, Retaining a Qualified Biologist. Prior to commencing construction, the City
shall retain the services of a qualified biologist. The USFWS and CDFW will be provided a 10-day period to
approve the proposed biologist. If no response from USFWS and CDFW is received within 10 days, approval
will be waived. The Project Biologist shall monitor all project-related ground-disturbing construction activities
and assist the City with implementation of all biological resource mitigation measures.
City of Rancho Palos
Verdes
Prior to
commencing
construction
(ground
disturbance)
4.4: Cultural Resources
MM CUL-1 Retaining a Qualified Archaeologist. Prior to commencing construction, the City of Rancho Palos Verdes (City)
shall retain the services of a Qualified Archaeologist meeting the Secretary of the Interior’s Standards. During
project-related ground-disturbing construction activities all initial ground-disturbing work shall be monitored
by the City’s Archeologist (i.e., an Archaeological Resources Monitor) proficient in artifact and feature
identification in monitoring contexts.
City of Rancho Palos
Verdes
Prior to
commencing
construction and
during project-
related ground-
disturbing
construction
activities
MM CUL-2 Worker Environmental Awareness Program (WEAP). Prior to commencing construction activities (and thus
prior to any ground disturbance on the proposed project site), the City’s Qualified Archaeologist shall conduct
initial Worker Environmental Awareness Program (WEAP) training of all construction personnel, including
supervisors, present at the outset of the project construction work phase, for which the lead contractor and
all subcontractors shall make their personnel available. This WEAP training will educate construction
personnel on how to work with the Qualified Archaeologist to identify and minimize impacts to archaeological
resources and maintain environmental compliance. This WEAP training will educate the monitor(s) of
construction procedures to avoid construction-related injury or harm. This training may be performed
periodically, such as for new personnel coming on to the project as needed.
City’s Qualified
archaeologist and
Project Contractor
Prior to
commencing
construction
activities (ground
disturbance)
MM CUL-3 Monitoring During Ground-Disturbing Activities. Prior to commencing construction, the Project Contractor
shall provide the City’s Qualified Archaeologist with a schedule of initial potential ground-disturbing activities.
A minimum of 48 hours’ notice will be provided to the consultant prior to commencement of any initial
ground-disturbing activities, such as vegetation grubbing or clearing, grading, trenching, or mass excavation.
The Qualified Archaeologist shall be present on site at the commencement of ground-disturbing activities
related to the project. The Qualified Archaeologist shall observe initial ground-disturbing activities and, if
determined appropriate, adjust the number of monitors as needed to provide adequate observation and
oversight. The Qualified Archaeologist will have stop-work authority to allow for recordation and evaluation of
Project Contractor 48 hours prior to
initial ground-
disturbing activities
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finds during construction. The Qualified Archaeologist will maintain a daily record of observations to serve as
an ongoing reference resource and to provide a resource for final reporting upon completion of the project.
The City’s Qualified Archaeologist, Project Contractor, and subcontractors, and the City shall maintain a line of
communication regarding schedule and activity such that the monitor is aware of all ground-disturbing
activities in advance in order to provide appropriate oversight.
MM CUL-4 Discovery of Previously Unidentified Archaeological Materials. In the event of the discovery of previously
unidentified archaeological materials, the Project Contractor shall immediately cease all work activities within
an area of no less than 50 feet of the discovery. After cessation of excavation, the Project Contractor shall
immediately contact the City. The discovery of any cultural resource within the project area shall not be
grounds for a project-wide “stop-work” notice or otherwise interfere with the project’s continuation except as
set forth in this paragraph. In the event of an unanticipated discovery of archaeological materials during
construction, the City’s Qualified Archaeologist shall evaluate the significance of the materials prior to
resuming any construction-related activities in the vicinity of the find. If the Qualified Archaeologist
determines that the discovery constitutes a significant resource under CEQA and cannot be avoided, the City
shall implement an archaeological data recovery program.
Project Contractor During construction
and in the event of
the discovery of
previously
unidentified
archaeological
materials
MM CUL-5 Archaeological Resources Monitoring Report. Withing 60 days of the completion of all ground-disturbing
activities, the City’s Archaeologist, serving as the City’s Archaeological Monitor, shall prepare an
Archaeological Resources Monitoring Report summarizing all monitoring efforts and observations, as
performed, and any and all prehistoric or historic archaeological finds, as well as providing follow-up reports
of any finds to the South Central Coastal Information Center (SCCIC), as required.
City’s Qualified
archaeologist
Within 60 days of
the completion of
all ground-
disturbing activities
4.5: Energy
There are no potentially significant impacts related to energy; therefore, no mitigation is required.
4.6: Geology and Soils
MM PAL-1 Paleontological Resources Monitor. The City of Rancho Palos Verdes (City) shall retain the services of a
Qualified Paleontologist meeting the Secretary of the Interior’s Standards prior to commencing construction
activity and require that all initial ground-disturbing work be monitored by paleontological specialists
(Paleontological Resources Monitor) proficient in fossil identification in monitoring contexts.
City of Rancho Palos
Verdes
Prior to
commencing
construction
activity (ground
disturbance)
MM PAL-2 Paleontological Mitigation Plan. Prior to commencing construction activity, the City’s qualified Paleontologist
shall prepare a Paleontological Mitigation Plan (PMP) outlining procedures for paleontological data recovery
for the proposed project and submitted to the City for review and approval. The development and
implementation of the PMP shall include consultations with the applicant’s engineering geologist as well as a
City’s Qualified
Paleontologist
Prior to
commencing
construction
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requirement that the curation of all specimens recovered under any scenario shall be conducted through an
appropriate repository agreed upon by the City. All specimens become the property of the City unless it
chooses otherwise. If the City accepts ownership, the curation location may be revised. The PMP shall include
developing a multilevel ranking system, or Potential Fossil Yield Classification (PFYC), as a tool to demonstrate
the potential yield of fossils within a given stratigraphic unit. The PMP shall outline the monitoring and salvage
protocols to address paleontological resources encountered during ground-disturbing activities as well as the
appropriate recording, collection, and processing protocols to appropriately address any resources
discovered. The cost of data recovery is limited to the discovery of a reasonable sample of available material.
The interpretation of reasonableness rests with the City.
activity (ground
disturbance)
MM PAL-3 Final Paleontological Mitigation Report. At the completion of all ground-disturbing activities, the City’s
Qualified Paleontologist shall prepare a final paleontological mitigation report summarizing all monitoring
efforts and observations, as performed in line with the PMP, and all paleontological resources encountered, if
any. The Paleontologist consultant shall also provide follow-up reports of any specific discovery, if necessary.
City’s Qualified
Paleontologist
At the completion
of all ground-
disturbing activities
4.7: Greenhouse Gas Emissions
There are no potentially significant impacts related to land use and greenhouse gas emissions; therefore, no mitigation is required.
4.8: Hazards and Hazardous Materials
There are no potentially significant impacts related to hazards and hazardous materials; therefore, no mitigation is required.
4.9: Hydrology and Water Quality
There are no potentially significant impacts related to hydrology and water quality; therefore, no mitigation is required.
4.10: Land Use and Planning
There are no potentially significant impacts related to land use and planning; therefore, no mitigation is required.
4.11: Noise
There are no potentially significant impacts related to noise; therefore, no mitigation is required.
4.12: Recreation
REC-1 Swale Design. Prior to finalizing the design of any of the project’s components, the Project Engineer shall
confirm that trails affected by construction activities are restored to their pre-construction condition is
acceptable to the City’s Director of Recreation and Parks. Rerouting /reconstruction of trails shall be reviewed
and approved by the Project Engineer, and provided to the Palos Verdes Peninsula Land Conservancy (PVPLC)
for their input.
The Project Engineer
and the Project
Contractor
Prior to finalizing
the design of any of
the project’s
components
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REC-2 Trail Closure Notifications. Fifteen days prior to the anticipated closure of any designated trails within the
Abalone Cove Park and Reserve or Portuguese Bend Reserve, the Project Engineer, and/or designee, shall
notify the City’s Recreation and Parks Department in order to notify PVPLC and provide adequate notice to
the public about any expected trail closures during project construction. The public will be notified of closures
via the City’s and the PVPLC’s websites, the City’s listserv and social media platforms, and use of on-site signs
at relevant entries to the Palos Verdes Nature Preserve and at closure locations.
The Project Engineer,
and/or designee
15 days prior to the
anticipated closure
of any designated
trails within the
Abalone Cove
Shoreline Park and
Reserve or
Portuguese Bend
Reserve
REC-3 Trail Repair/Maintenance. If Preserve trails become damaged or require maintenance resulting from the
project, the City will coordinate with the PVPLC, to repair trails in accordance with the City Council-adopted
Natural Community Conservation Plan/Habitat Conservation Plan (NCCP/HCP) and the Preserve Public Use
Master Plan (PUMP).
City of Rancho Palos
Verdes
If Preserve trails
become damaged
or require
maintenance
resulting from the
project
4.13: Transportation/Traffic
There are no potentially significant impacts related to transportation and traffic; therefore, no mitigation is required.
4.14: Tribal Cultural Resources
MM TCR-1 Tribal Cultural Resources Monitoring. Prior to the commencement of construction, City of Rancho Palos
Verdes (City) approved qualified archaeologist to monitor all ground-disturbing activities associated with the
project, including, but not limited to, grading, excavating, clearing, leveling and backfilling. The evaluation
shall be conducted by an archaeologist meeting the Secretary of the Interior’s Professional Qualifications
Standards for prehistoric archaeology (National Park Service 1983) and qualified to identify subsurface tribal
cultural resources. The archaeologist shall observe all ground-disturbing activities on the project site at all
times the ground-disturbing activities are taking place. If ground-disturbing activities are simultaneously
occurring at multiple locations on the project site, an archaeologist shall be required to monitor each location
where the ground-disturbing activities are occurring.
Prior to the commencement of any ground-disturbing activities at the project site, the City, or its successor,
shall notify any California Native American tribes that have informed the City that they are traditionally and
culturally affiliated with the geographic area of the proposed project that ground-disturbing activities are
about to commence and invite the tribe(s) to observe the ground-disturbing activities if the tribes wish to
monitor, at their own expense.
Project Contractor, Prior to the
commencement of
construction
(ground
disturbance) and
during construction
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In the event that any subsurface objects or artifacts that may be tribal cultural resources are encountered
during the course of the ground-disturbing activities, all such activities shall temporarily cease within the area
of discovery, the radius of which shall be determined by the qualified archeologist, until the potential tribal
cultural resources are properly assessed and addressed pursuant to the process set forth below:
1. Upon a discovery of a potential tribal cultural resource, an applicant, or its successor, shall immediately
stop all ground-disturbing activities and contact the following: (1) all California Native American tribes that
have informed the City that they are traditionally and culturally affiliated with the geographic area of the
proposed project; (2) and the City’s Community Development Department, Planning Division.
2. If the City determines, pursuant to Public Resources Code Section 21704 (a)(2), that the object or artifact
appears to be a tribal cultural resource in its discretion and supported by substantial evidence, the City
shall provide any affected tribe a reasonable period of time, not less than 14 days, to conduct a site visit
and make recommendations to the applicant, or its successor, and the City regarding the monitoring of
future ground-disturbing activities, as well as the treatment and disposition of any discovered tribal
cultural resources.
3. The City, shall implement the tribe’s recommendations if a qualified archaeologist, retained by the City
concludes that the tribe’s recommendations are reasonable and feasible.
4. In addition to any recommendations from the applicable tribe(s), the City-approved qualified archeologist
shall develop a list of actions that shall be taken to avoid or minimize impacts to the identified tribal
cultural resources substantially consistent with best practices identified by the Native American Heritage
Commission (NAHC) and in compliance with any applicable federal, State, or local law, rule, or regulation.
5. If the City, does not accept a particular recommendation determined to be reasonable and feasible by the
qualified archaeologist, the City, may request mediation by the City’s mediator. The mediator must have
the requisite professional qualifications and experience to mediate such a dispute. The City shall make the
determination as to whether the mediator is at least minimally qualified to mediate the dispute. After
making a reasonable effort to mediate this particular dispute, the City may: (1) require that the
recommendation be implemented as originally proposed by the archeologist; (2) require that the
recommendation, as modified by the City, be implemented as it is at least equally effective to mitigate a
potentially significant impact; (3) require a substitute recommendation to be implemented that is at least
equally effective to mitigate a potentially significant impact to a tribal cultural resource; or (4) not require
the recommendation to be implemented because it is not necessary to mitigate any significant impacts to
tribal cultural resources. The City shall pay all costs and fees associated with the mediation.
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6. The City may recommence ground-disturbing activities outside of a specified radius of the discovery site so
long as this radius has been reviewed by a qualified archaeologist and determined to be reasonable and
appropriate.
7. The City may recommence ground-disturbing activities inside of the specified radius of the discovery site
only after it has complied with all the recommendations developed and approved pursuant to the process
set forth in Items 2 through 5, above.
8. Copies of any subsequent prehistoric archaeological study, tribal cultural resources study, or report
detailing the nature of any significant tribal cultural resources, remedial actions taken, and disposition of
any significant tribal cultural resources shall be submitted to the South Central Coastal Information Center
(SCCIC) at California State University, Fullerton, and to the NAHC for inclusion in its Sacred Lands File.
Notwithstanding Item 8, above, any information determined to be confidential in nature by the City
Attorney’s Office, shall be excluded from submission to the SCCIC or the general public under the provisions of
the California Public Records Act and the California Public Resources Code (PRC).
4.15: Utilities and Service Systems
There are no potentially significant impacts related to utilities and service systems; therefore, no mitigation is required.
4.16: Wildfire
There are no potentially significant impacts related to wildfire; therefore, no mitigation is required.
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