Save Desert Rose v. City of Encinitas CA4/1 ( 2015 )


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  • Filed 10/28/15 Save Desert Rose v. City of Encinitas CA4/1
    NOT TO BE PUBLISHED IN OFFICIAL REPORTS
    California Rules of Court, rule 8.1115(a), prohibits courts and parties from citing or relying on opinions not certified for
    publication or ordered published, except as specified by rule 8.1115(b). This opinion has not been certified for publication
    or ordered published for purposes of rule 8.1115.
    COURT OF APPEAL, FOURTH APPELLATE DISTRICT
    DIVISION ONE
    STATE OF CALIFORNIA
    SAVE DESERT ROSE,                                                  D066218
    Plaintiff and Respondent,                                 (Super. Ct. No. 37-2013-00044139-CU-
    JR-NC)
    v.
    CITY OF ENCINITAS,
    Defendant;
    WOODRIDGE FARMS ESTATES, LLC,
    Real Party in Interest and Appellant.
    APPEAL from a judgment of the Superior Court of San Diego County, Judith F.
    Hayes, Judge. Reversed.
    Coast Law Group, Marco A. Gonzalez and Chris C. Polychron for Appellant and
    Real Party in Interest.
    DeLano & DeLano, Everett L. DeLano III and M. Dare DeLano for Plaintiff and
    Respondent.
    Woodridge Farms Estates, LLC (Woodridge) appeals from the trial court's
    judgment and writ of mandate in favor of Save Desert Rose (SDR), ruling that the City of
    Encinitas (the City) should have required the preparation of an environmental impact
    report (EIR) under the California Environmental Quality Act (CEQA) (Pub. Resources
    Code, § 21000 et seq.)1 for a residential development proposed by Woodridge rather than
    adopting a mitigated negative declaration. We conclude that based on the project
    description in the mitigated negative declaration, there is no substantial evidence in the
    administrative record to support a fair argument that Woodridge's proposed project may
    have a significant effect on the environment within the meaning of CEQA. Accordingly
    we reverse the judgment and direct the trial court to enter an order denying the petition
    for writ of mandate.
    I.
    FACTUAL AND PROCEDURAL BACKGROUND
    In 2009, Woodridge filed an application seeking approval from the City's planning
    commission of a tentative map and the issuance of a design review permit for a real estate
    development on a 7.87-acre lot in the City, located in the community of Olivenhain (the
    Project).2 The Project would subdivide a 7.87-acre lot currently used as a commercial
    1     Unless otherwise indicated, all further statutory references are to the Public
    Resources Code.
    2      Approval for the construction plans for the proposed homes was not sought in the
    application at issue here and will presumably be sought in later applications to the City.
    2
    equestrian facility into 16 single-family residential lots, with one private street
    cul-de-sac.3
    The Project includes the removal of the equestrian facilities (stables, riding rings
    and associated outbuildings), grading of the site, creation of street improvements,
    dedication of a public recreational trail for equestrian use, installation of drainage and
    stormwater treatment facilities, and the planting of landscaping. As relevant here, as part
    of the grading and landscaping activity, the Project would remove up to 34 trees within
    the Project site, primarily consisting of eucalyptus and pine species,4 and those trees
    would be replaced by 48 tree species that are fire resistant and noninvasive.
    The Project parcel is zoned for residential development and is bordered by a
    residential neighborhood on the south and west. Located along the northern and eastern
    boundaries of the parcel is a .56-acre wetland and riparian habitat, consisting of a natural
    3      Although not directly relevant to our resolution of this appeal, we note that in
    proposing to divide the Project site into 16 residential lots, Woodridge sought to take
    advantage of the density bonus law set forth in Government Code, section 65915, which
    allows for development of more dense subdivisions than would otherwise be permitted by
    local development standards when the developer commits to build a certain amount of
    affordable housing units as part of the subdivision. Based on the density bonus law, the
    Project would be built with a density that adds four units above the number of units that
    would otherwise have been allowed by the City's general plan.
    4      We note that the record is unclear about how many mature trees currently exist on
    the Project site, and how many will have to be removed in connection with the grading
    work. Although City staff comments identified 34 existing trees to be removed, the
    Landscape Concept Plan in the record, dated October 10, 2012, states that there are 31
    existing mature trees on the site, including 17 eucalyptus trees. The Landscape Concept
    Plan also indicates the location of the current trees, several of which may be outside of
    the area proposed to be graded, and states that "existing mature trees must be preserved to
    the greatest extent feasible within the easements for" the adjacent streets.
    3
    drainage channel that is an unnamed tributary of Escondido Creek. There is currently no
    buffer between the equestrian facility and the wetland. Consequently, the wetland is a
    poorly developed riparian habitat, with the presence of numerous nonnative plant species
    and lack of vegetation in some areas, and it supports a low diversity and number of
    animal species, none of which are sensitive species.
    According to the City's General Plan and Municipal Code, a 50-foot-wide buffer
    generally should be used for proposed development adjacent to riparian wetland areas,
    but in some cases smaller buffers may be appropriate.5 Here, the Project proposal
    includes a 25-foot buffer and other measures to protect the wetland habitat. Included in
    these additional measures are two items recommended by the United States Fish and
    Wildlife Service and the California Department of Fish and Game6 as a condition to their
    approval of the use of a 25-foot buffer for the Project: (1) a fence at least six feet high
    5      The City's general plan states that "50 foot wide buffers should be provided
    adjacent to riparian areas. In some cases, smaller buffers may be appropriate, when
    conditions of the site as demonstrated in a site specific biological survey, the nature of the
    proposed development, etc., show that a smaller buffer would provide adequate
    protection; and when the Department of Fish and Game has been consulted and their
    comments have been accorded great weight." The City's municipal code states that
    "riparian wetland areas . . . shall require a minimum 50 foot wide buffer, unless the
    applicant demonstrates that a buffer of lesser width will protect the resources of the
    wetland, based on site-specific information. Such information shall include, but is not
    limited to, the type and size of the development and/or proposed mitigations (such as
    planting of vegetation or construction of fencing) which will also achieve the purposes of
    the buffer. . . . The California Department of Fish and Game and the U.S. Fish and
    Wildlife Service . . . shall be consulted in such buffer determinations." (Encinitas Mun.
    Code, § 30.34.040B3b.)
    6      As of January 1, 2013, the California Department of Fish and Game is known as
    the California Department of Fish and Wildlife. (Fish & G. Code, § 37.)
    4
    constructed between the Project and the wetland; and (2) the implementation of a wetland
    enhancement plan.
    After receiving Woodbridge's application, the City staff prepared an initial study
    pursuant to CEQA, summarizing and evaluating the various technical studies that were
    prepared for the Project by outside consultants.7 The initial study concluded that the
    Project could have a significant environmental effect on biological resources,
    specifically, as relevant here, (1) possible impacts to any sensitive raptor nests, including
    Cooper's Hawks, that may be present in the eucalyptus trees to be removed from the
    Project site; and (2) indirect impacts to sensitive wetland habitat due to the location of
    future development adjacent to the natural drainage channel.8 The initial study
    7        As explained in the CEQA Guidelines, "(a) [f]ollowing preliminary review, the
    lead agency shall conduct an initial study to determine if the project may have a
    significant effect on the environment." (Cal. Code Regs., tit. 14, § 15063.) As part of the
    initial study, the City completed an initial study checklist pursuant to appendix G of the
    CEQA Guidelines which "contains an ' " 'Environmental Checklist Form' . . . designed to
    be used as an initial study to determine if a project may have a significant effect on the
    environment." ' . . . ' "The checklist consists of sample questions divided into categories
    of potential physical impacts a project may have." ' " (Keep Our Mountains Quiet v.
    County of Santa Clara (2015) 
    236 Cal. App. 4th 714
    , 732, citations omitted.)
    8       The initial study also noted that .06 acre of disturbed coastal sage scrub habitat
    and .06 acre of nonnative grassland habitat would be disturbed due to the fuel
    modification plan required for fire safety, but that the environmental impact of that
    habitat disturbance would be reduced to below a level of significance because, as a
    condition of approval of the Project, Woodridge was to acquire and conserve equivalent
    offsite habitat, which could be accomplished through purchasing credits from a
    mitigation bank.
    5
    recommended that these possible impacts be mitigated through measures that would be
    set forth in a mitigated negative declaration (MND) as provided by CEQA.9
    The MND proposed by City staff contained the following relevant items: (1) if
    trees are removed from the Project site during Cooper's Hawk nesting season, a qualified
    biologist shall conduct a survey three days prior to determine whether there are any active
    nests, and if so, a buffer shall be set up and no removal of those trees shall occur until the
    nesting cycle is complete; (2) a minimum 25-foot-wide biological open-space easement
    shall be recorded as shown on the tentative map between the development and the
    wetland habitat, which shall include a 25-foot buffer protected by permanent fencing,
    with no gates, to prevent intrusion by cats and other pets;10 (3) during construction of the
    Project the biological easement shall be protected with construction and silt fencing that
    shall be portrayed on the construction plans to the satisfaction of the City's planning and
    building department director; (4) a wetland enhancement plan shall be approved by the
    City's planning and building department, and shall be implemented prior to occupancy of
    9      As set forth in the CEQA Guidelines, "[a] public agency shall prepare or have
    prepared a proposed . . . mitigated negative declaration for a project subject to CEQA
    when: [¶] . . . [¶] (b) The initial study identifies potentially significant effects, but:
    (1) Revisions in the project plans or proposals made by or agreed to by the applicant
    before a proposed mitigated negative declaration and initial study are released for public
    review would avoid the effects or mitigate the effects to a point where clearly no
    significant effects would occur, and (2) There is no substantial evidence, in light of the
    whole record before the agency, that the project as revised may have a significant effect
    on the environment." (Cal. Code Regs., tit. 14, § 15070.)
    10     The open-space component of the Project, which includes wetland and wetland
    buffer areas, would total approximately 1.72 acres of the total 7.87-acre property.
    6
    the residences proposed for Project;11 (5) construction plans shall contain certain
    additional measures to protect the environment during construction, as listed; and
    (6) Project landscape plans shall be approved by the City prior to the issuance of a
    building permit and shall not contain exotic plant species that may be invasive or require
    excessive irrigation, and potential runoff shall be contained or treated within the
    development footprint.
    The planning commission held a public hearing on November 1, 2012, and
    thereafter issued a resolution denying Woodridge's application, with a three-to-two vote.
    In denying the application, the planning commission declined to adopt the MND and
    found that "the design of the subdivision or the proposed improvements are likely to
    cause substantial environmental damage or substantially or avoidably injure fish or
    wildlife or their habitat."
    Woodridge appealed the planning commission's decision to the City Council, and
    the City Council conducted public hearings on January 23 and March 13, 2013, with the
    City's staff preparing answers to several questions posed by the City Council following
    the January 23 hearing. In a resolution adopted April 17, 2013, the City approved
    11     The wetland enhancement plan provides that approximately one-half acre of exotic
    plants will be removed from the wetland habitat on the Project parcel and in a smaller
    area upstream from the parcel. Also included in the wetland enhancement plan is the
    nonwetland habitat of southern maritime chaparral, dominated by environmentally
    sensitive Nuttall's Scrub Oak vegetation, which is adjacent to the wetland area. The area
    covered by the enhancement plan will be monitored for five years to assess natural
    revegetation, and the area will be replanted with native plants if revegetation does not
    occur naturally.
    7
    Woodridge's application for the Project and formally adopted the MND. The City
    Council found that "with incorporation of the mitigation measures contained in the
    MND . . . , the proposed subdivision is not likely to cause substantial environmental
    damage or substantially or avoidably injure fish or wildlife or their habitat."
    In addition to adopting the MND, the City Council approved Woodridge's
    application with certain other conditions that are relevant here. Specifically, the City
    required that Woodridge provide the public equestrian trail proposed for the Project, and
    it required that Woodridge comply with certain engineering and geotechnical conditions,
    including compliance with stormwater management regulations and drainage
    requirements. Before any grading takes place for the Project, Woodridge is required to
    apply for and obtain a grading permit and meet several other requirements, including
    obtaining approval from the City of a plan to implement stormwater best management
    practice controls, and submit a geotechnical report.
    SDR filed a petition for writ of mandate in the trial court to challenge the City's
    adoption of the MNR, and Woodridge and the City both opposed SDR's petition. The
    trial court ruled in favor of SDR and issued a writ of mandate, setting aside the City's
    approval of Woodridge's application and adoption of the MND, and enjoining Woodridge
    from taking any step to further the Project that could result in an adverse change to the
    environment pending lawful approval from the City. The trial court's statement of
    decision concluded that "the record establishes substantial evidence existed to make a fair
    argument that the project may cause a significant adverse effect on the environment such
    that the City Council should have prepared an [EIR] instead of issuing [an MND]."
    8
    Woodbridge appeals from the trial court's judgment.
    II.
    DISCUSSION
    A.     Applicable Legal Standards
    Under CEQA, "[a]n EIR provides detailed information about the likely effect a
    proposed project may have on the environment, lists ways in which significant effects
    might be minimized and indicates alternatives to the project. (. . . § 21061.) An EIR is
    required whenever there is a ' "fair argument" ' that significant impacts may occur.
    [Citation.] [¶] When there is no substantial evidence before the lead agency that the
    project may have a significant effect on the environment, a negative declaration instead
    of an EIR, is appropriate. (. . . § 21080, subd. (c)(1).) When the initial study identifies
    potentially significant effects on the environment, but revisions in the project plans would
    avoid or mitigate the effects to insignificance, a MND is appropriate. (. . . § 21064.5.)"
    (Ocean View Estates Homeowners Assn., Inc. v. Montecito Water Dist. (2004) 
    116 Cal. App. 4th 396
    , 399.) " 'Significant effect on the environment' means a substantial, or
    potentially substantial, adverse change in the environment." (§ 21068.)12
    12       As provided in the CEQA Guidelines, " 'Significant effect on the environment'
    means a substantial, or potentially substantial, adverse change in any of the physical
    conditions within the area affected by the project including land, air, water, minerals,
    flora, fauna, ambient noise, and objects of historic or aesthetic significance. An
    economic or social change by itself shall not be considered a significant effect on the
    environment. A social or economic change related to a physical change may be
    considered in determining whether the physical change is significant." (Cal. Code Regs.,
    tit. 14, § 15382.) "The CEQA Guidelines . . . are regulations adopted by the secretary of
    the Natural Resources Agency to implement CEQA. . . . 'In interpreting CEQA, we
    9
    "Application of the fair argument standard of review presents a question of law,
    not fact, and we do not defer to the agency's or the trial court's determinations on this
    issue. [Citation.] 'Rather, we independently "review the record and determine whether
    there is substantial evidence in support of a fair argument [the proposed project] may
    have a significant environmental impact, while giving [the lead agency] the benefit of a
    doubt on any legitimate, disputed issues of credibility." ' " (Porterville Citizens for
    Responsible Hillside Development v. City of Porterville (2007) 
    157 Cal. App. 4th 885
    ,
    900.)
    The party challenging an agency's decision not to prepare an EIR "has the burden
    of proof 'to demonstrate by citation to the record the existence of substantial evidence
    supporting a fair argument of significant environmental impact.' [Citation.] 'Unless the
    administrative record contains this evidence, and [petitioners] cite[] to it, no "fair
    argument" that an EIR is necessary can be made.' " (Parker Shattuck Neighbors v.
    Berkeley City Council (2013) 
    222 Cal. App. 4th 768
    , 778.) In this context, as set forth in
    the CEQA Guidelines, " '[s]ubstantial evidence' . . . means enough relevant information
    and reasonable inferences from this information that a fair argument can be made to
    support a conclusion, even though other conclusions might also be reached. . . .
    Argument, speculation, unsubstantiated opinion or narrative, evidence which is clearly
    erroneous or inaccurate, or evidence of social or economic impacts which do not
    accord the Guidelines great weight except where they are clearly unauthorized or
    erroneous.' " (Center for Biological Diversity v. Department of Fish & Wildlife (2015)
    
    234 Cal. App. 4th 214
    , 226, fn. 3, citations omitted.)
    10
    contribute to or are not caused by physical impacts on the environment does not
    constitute substantial evidence," and "[s]ubstantial evidence shall include facts,
    reasonable assumptions predicated upon facts, and expert opinion supported by facts."
    (Cal. Code Regs., tit. 14, § 15384, subds. (a), (b).)13
    If the petitioner demonstrates substantial evidence to support a fair argument of a
    significant effect on the environment "the reviewing court must set aside the agency's
    decision to adopt a negative declaration or a mitigated negative declaration as an abuse of
    discretion in failing to proceed in a manner as required by law." (Citizens for
    Responsible and Open Government v. City of Grand Terrace (2008) 
    160 Cal. App. 4th 1323
    , 1332.)
    B.     Alleged Unmitigated Environmental Impacts Identified by SDR
    As it did in the trial court, SDR identifies several different categories of alleged
    significant environmental impacts from the Project, which it contends required that the
    City prepare an EIR rather than adopt the MND. Specifically, SDR identifies alleged
    impacts on (1) biological resources; (2) aesthetics, views and community character;
    (3) water quality and drainage; (4) traffic; (5) neighborhood streets and safety; and
    (6) parking. We consider each of these categories in turn.
    13     Similarly, as stated in section 21080, subdivision (e): "(1) [S]ubstantial evidence
    includes fact, a reasonable assumption predicated upon fact, or expert opinion supported
    by fact. [¶] (2) Substantial evidence is not argument, speculation, unsubstantiated
    opinion or narrative, evidence that is clearly inaccurate or erroneous, or evidence of
    social or economic impacts that do not contribute to, or are not caused by, physical
    impacts on the environment."
    11
    1.     Biological Resources
    SDR's argument concerning the Project's impact on biological resources focuses
    on the two categories that the City's initial study also identified as potential significant
    environmental impacts prior to the adoption of the MND, namely, the possible harm to
    nesting raptors in the eucalyptus trees on the Project site and (2) the impact to the wetland
    habitat from the residential development proposed by the Project.
    a.      Impact on Raptors of Tree Removal
    Concerning the removal of the trees that are currently on the Project site, SDR
    contends that the administrative record supports a fair argument that the removal of those
    trees will have a significant negative effect on sensitive raptor species. In support of its
    argument, SDR points to the 2009 biological report prepared for the initial study, which
    states that the Project site contains "[n]umerous [e]ucalyptus trees that could potentially
    serve as nesting sites for Cooper's Hawks," a sensitive bird species. SDR also points to
    two neighborhood residents' general comments about "the value of the on-site trees for
    habitat."14
    We reject SDR's contention that the record raises a fair argument of significant
    impact from the Project on Cooper's Hawks or other sensitive raptors. Initially, we note
    14     One neighborhood resident wrote that "[t]he cutting down of the numerous trees
    on the property will have a negative impact. They should be replaced on [a] one to one
    basis with native trees with the goal to diminish the visual impact of the project and
    replace nesting sites." (Italics added.) Another neighborhood resident recalled that when
    he was building a house on his property he was instructed not to cut down Eucalyptus
    trees because "these trees provided raptor nesting."
    12
    that during the biological survey of the site — which consisted of eight visits over the
    course of one and half years — there was no evidence of Cooper's Hawks, their nests, or
    any other sensitive raptor species or avian nests. Second, although it is undisputed that
    Cooper's Hawks use eucalyptus trees during the nesting season, there is no evidence in
    the record that eucalyptus tree nesting habitat is in short supply in the area surrounding
    the Project site such that removal of the trees on the site would significantly impact the
    ability of Cooper's Hawks to nest in the area. Instead, the sole concern regarding
    Cooper's Hawks in the biological assessment report prepared for the Project is that
    nesting Cooper's Hawks may be impacted if trees are removed during nesting season;
    there is no concern expressed about loss of eucalyptus tree habitat in the area. Third,
    SDR acknowledges that the MND addresses the possible harm to any nesting Cooper's
    Hawks that may build nests on the Project site prior to construction by providing that,
    immediately before the eucalyptus trees are scheduled to be removed, a biologist will
    determine whether Cooper's Hawks are currently nesting in the trees, and if so, tree
    removal will be delayed until after the nesting cycle is complete. Accordingly, as any
    nesting Cooper's Hawks will be undisturbed by the Project and there is no evidence
    eucalyptus tree habitat is in short supply in the surrounding area, the record does not
    support a fair argument that the Project will have a significant negative impact on
    Cooper's Hawks or other sensitive raptors.15
    15     In discussing the impact of the Project on biological resources, SDR also mentions
    the fact that several Torrey Pine trees on the Project site will be removed, but it does not
    point to any evidence in the record showing that removal of those trees would have a
    13
    b.     Impact on Wetland Habitat
    SDR's argument regarding the Project's possible impact on the wetland habitat
    bordering the Project site on the north and east focuses on evidence in the record
    pertaining to whether it would have been better for the City to require a 50-foot-wide
    buffer rather than a 25-foot-wide buffer between the housing development and the
    wetland habitat. As we will explain, based on the applicable standard for determining
    whether a significant effect on the environment has been identified, the evidence that
    SDR relies upon does not raise a fair argument that the Project will significantly impact
    the wetland habitat.
    When conducting an analysis under CEQA to determine whether the record
    supports a fair argument of a significant impact on the environment, "impacts of a
    proposed project are ordinarily to be compared to the actual environmental conditions
    existing at the time of CEQA analysis." (Communities for a Better Environment v. South
    Coast Air Quality Management Dist. (2010) 
    48 Cal. 4th 310
    , 321.) Under this rule, "the
    baseline for CEQA analysis must be the 'existing physical conditions in the affected area'
    . . . that is, the ' " real conditions on the ground." ' " (Ibid., citations omitted.) An
    analysis under CEQA " 'must focus on impacts to the existing environment, not
    hypothetical situations' " because "[a]n approach using hypothetical allowable conditions
    significant effect on the environment. Indeed, the only evidence in the record is to the
    contrary. Specifically, the biological assessment report states that "there are no major or
    critical populations of Torrey Pines in the City of Encinitas, only scattered individuals,
    most of which have been planted," and "[s]ince the ten Torrey Pines on-site are believed
    to be planted, rather than naturally occurring, the loss of these ten trees is not considered
    significant. Therefore, no mitigation for their loss is proposed."
    14
    as the baseline results in 'illusory' comparisons that 'can only mislead the public as to the
    reality of the impacts and subvert full consideration of the actual environmental impacts,'
    a result at direct odds with CEQA's intent." (Id. at p. 322.)
    Here, as we have explained, the record shows that there is currently no buffer
    between the equestrian facility on the Project site and the wetland habitat. Indeed, some
    of the equestrian facilities are within a few feet of the wetland habit. Further, the wetland
    habitat is of poor quality because it contains numerous exotic species and, in some places,
    lacks vegetation. It is against this baseline condition that we must assess whether the
    record supports a fair argument that the Project will have a significant negative impact on
    the wetland habitat.16
    The record establishes that the measures included in the Project to protect the
    wetland habitat will improve the habitat over its current condition. The Project will
    16      SDR points out that Woodridge recently performed restoration work in the
    wetland habit in response to a notice of violation issued to Woodridge under the City's
    grading ordinance in 2011. Specifically, the notice of violation was issued by the City
    after a neighborhood resident reported seeing employees of the equestrian facility
    disturbing the wetland habitat by diverting some of the water flow with a tractor and
    encroaching on it with rabbit hutches, clotheslines, and a vegetable garden. As a result of
    the notice of violation, Woodridge agreed to remove all of the encroaching items and to
    restore the area of the wetland disturbed by the water flow diversion by removing exotic
    species in the impacted area, monitoring for regrowth of native plants, and planting
    certain native plants. SDR argues that Woodridge's restoration work in response to the
    notice of violation has changed the baseline condition of the wetland habitat in a manner
    that is significant for the CEQA analysis. We disagree. The undisputed evidence in the
    record shows that the restoration work agreed to by Woodridge in response to the notice
    of violation was minimal and did not change the essential degraded condition of the
    wetland habit as a whole. Most significantly, there is still no buffer between the
    equestrian facility and the wetland habitat, and Woodridge was to remove exotic species
    only from a limited area disturbed by the tractor activity.
    15
    create a 25-foot-wide buffer where none currently exists, dedicated as an open-space
    easement; a six-foot-tall fence will be constructed to further protect the wetland habitat
    from disturbance; a wetland enhancement plan will be implemented to remove exotic
    plant species and promote the growth of native wetland vegetation; and the harmful
    effects of urban runoff into the wetland habitat will be addressed by the City's
    requirement that the Project comply with up-to-date stormwater management and
    drainage standards. None of these measures to protect the wetland habitat exists as part
    of the current baseline condition.
    Nevertheless, SDR contends that the record supports a fair argument that the
    Project will significantly and negatively impact the wetland habitat due to comments in
    the record concerning the proposal of a 25-foot-wide buffer rather than a 50-foot-wide
    buffer. However, as we will explain, these comments do not support SDR's argument
    because they are directed to a different issue, namely whether the City should have
    required a 50-foot buffer for the Project over a 25-foot buffer, rather than whether the
    Project will have a significant negative impact on the baseline environmental condition of
    the wetland habitat as it currently exists.
    The main evidence upon which SDR relies is a letter from biologist Anita M.
    Hayworth. Hayworth stated that based on the scientific literature regarding the use of
    buffers to protect wetland habitats, "much of the sediment and nutrient removal occurs
    within the first 15 to 30 feet of the buffer but that having a wider buffer, up to 100 feet or
    more, is able to remove pollutants more consistently. A number of studies indicate . . .
    that no buffers of 25 feet or less were functioning fully to reduce disturbance to the
    16
    wetlands." (Italics added.) Hayworth explained that "a wetland buffer of 50 feet . . .
    would provide improved protection of the wetlands from human disturbance and other
    indirect impacts that can occur with a development." (Italics added.) However,
    Hayworth's comments that it is preferable to use a wider buffer are not evidence of a
    possible significant impact on the baseline environmental condition of the wetland habitat
    for at least two reasons.
    First, currently no buffer exists between the equestrian facility and the wetland
    habitat. Thus, even though Hayworth may be correct that a 50-foot-wide buffer would
    provide more protection of the wetland habitat than a 25-foot-wide buffer, a buffer of any
    width would still be an improvement to the protection of the wetland habitat. Indeed,
    Hayworth does not state that a 25-foot buffer will fail to provide any protection to the
    wetland habitat; she simply states that a wider buffer would provide improved protection.
    Second, Hayworth's comments do not take into account the other measures that are
    incorporated into the Project to protect the wetland habitat, the use of which the state and
    federal wildlife agencies concluded made a 25-foot buffer an adequate width to protect
    the wetland habitat. Specifically, Hayworth does not account for the fact that the buffer
    will provide protection to the wetland habitat in conjunction with (1) a six-foot high fence
    separating the development from the wetland habitat, (2) a wetland restoration plan that
    will remove exotic species and promote the growth of native riparian plants;17 and
    17     Hayworth does acknowledge that the Project includes a wetland enhancement
    plan, but she discounts its value based on an inaccurate understanding of what it entails.
    Hayworth refers to the wetland enhancement plan as a passive restoration plan which
    17
    (3) the installation of up-to-date stormwater management and drainage measures which
    will direct urban runoff away from the wetland habitat.
    SDR also relies on the comments of two local conservation groups regarding the
    benefits of having a 50-foot-wide buffer. A letter from the San Elijo Lagoon
    Conservancy states, "The proponent of the reduction claims that the 25 feet will be
    restored to a higher quality habitat than currently exists on the site. This may be the case,
    but ecologically a 50[-foot] buffer not restored protects the creek better than the proposed
    modification."18 A letter from The Escondido Creek Conservancy states that a 50-foot
    buffer should be required, asserting without any further support or analysis that a
    25-foot-wide buffer "may" negatively affect the environment, and expressing concern for
    the environmental impact to downstream areas, such as lagoons and beaches.
    intends "to rely on 'Mother Nature'," an approach she contrasts with "ecological
    restoration," which "does address invasive exotic species" and "plac[es] plants in the
    ground." Here, as we have explained, the Project's wetland enhancement plan includes
    removal of exotic species, monitoring, and planting of native plants if necessary for
    revegetation.
    18      The letter from the San Elijo Lagoon Conservancy is also unpersuasive because it
    relies on a misunderstanding of the facts. Referring to the notice of violation that the
    City issued to Woodridge, the letter states that "the past practices that impacted the first
    25 feet have been stopped through a cease and desist order for Encinitas code
    enforcement." As we have explained, the record establishes that Woodridge's response to
    the notice of violation did not serve to significantly remediate the ecological damage to
    the wetland caused by being located next to the equestrian facility without a buffer.
    Instead, Woodridge took the limited steps of removing some encroaching items and
    restoring the native plants in the area impacted by the recent diversion of the water flow
    with a tractor in the wetland habitat.
    18
    The comments from both conservation groups are vague and unsupported by any
    scientific studies. More importantly, they fail to provide evidence of a significant impact
    to the environment for the purposes of a CEQA analysis on the same grounds as
    Hayworth's comments: (1) they state that a 50-foot-wide buffer is preferable to a
    25-foot-wide buffer, although the current baseline condition is no buffer, which provides
    no protection to either the wetland habitat or the downstream lagoons and beaches;
    (2) and they fail to account for the other measures that the Project will implement to
    protect the wetland habitat and that will act in conjunction with the 25-foot buffer to
    protect the environment.
    2.     Aesthetics, Views and Community Character
    The next category that SDR identifies as being significantly impacted by the
    Project is "aesthetics, views, and community character."
    a.     Impacts on Aesthetics and Views
    SDR discusses aesthetics and views together, with the argument that mature trees
    currently on the property will be cut down, impacting the "scenic resources" of the
    neighborhood. A CEQA analysis properly takes into account the aesthetic impact of a
    proposed project. "Under CEQA, it is the state's policy inter alia to '[t]ake all action
    necessary to provide the people of this state with . . . enjoyment of aesthetic, natural,
    scenic, and historic environmental qualities.' (§ 21001, subd. (b); italics added.) The
    CEQA initial study checklist asks four questions as to aesthetic impact, including
    whether a project will '[s]ubstantially degrade the existing visual character or quality of
    the site and its surroundings.' . . . [¶] Thus, courts have recognized that aesthetic issues
    19
    'are properly studied in an EIR to assess the impacts of a project.' " (Pocket Protectors v.
    City Of Sacramento (2004) 
    124 Cal. App. 4th 903
    , 936-937, citations omitted.)
    With respect to the Project's impact on aesthetics and views, SDR argues that the
    public's view of the property from the surrounding streets and recreational trails will no
    longer be of an equestrian facility with mature trees, but will be of newly built houses and
    newly installed landscaping, impacting the visual quality of the site and its surroundings.
    In support of its argument, SDR identifies photographs in the record showing that a
    person walking on a public recreational trail near the property currently has a view of
    mature trees when looking toward the property.
    We reject SDR's argument because the Project, as proposed, will sufficiently
    mitigate for the removal of trees on the property to address the impact that tree removal
    will have on the visual character of the site. Although the grading of the site for the
    Project will require the removal of 34 trees, the landscaping plan for the Project includes
    the planting of 48 new trees. The view from the neighborhood of the Project site will not
    be of a barren and unattractive lot as SDR suggests, but rather of a property that contains
    more trees than it formerly did.
    b.     Impacts on Community Character
    With respect to the Project's impacts on community character, SDR argues that
    having a residential development on the site rather than an equestrian facility will
    significantly change the character of the neighborhood. Specifically, SDR argues that the
    loss of a horse boarding facility will impact community character, as the record contains
    evidence that Olivenhain is an equestrian-friendly community, with 21 miles of horse
    20
    trails in the area and 371 residents owning horses, and thus has "the 'feeling of country.' "
    As we will explain, SDR fails to identify a significant impact to the environment with
    respect to community character.
    For one thing, the loss of a commercial enterprise, such as the horse boarding
    facility at issue here, is not an impact on the environment for the purposes of CEQA.
    (South Orange County Wastewater Authority v. City of Dana Point (2011) 
    196 Cal. App. 4th 1604
    , 1614 (South Orange County Wastewater Authority).)
    Moreover, although SDR contends that the Project is inconsistent with the
    equestrian nature of the community, equestrian uses in the neighborhood will actually be
    enhanced by the Project because the Project will build and dedicate a public equestrian
    trail through the Project site, where none existed before. Despite SDR's focus on the
    current equestrian use of the Project site, it is undisputed that the Project site is zoned for
    residential use and the surrounding neighborhood is residential. Thus, the development
    of the Project as single-family residences, with a portion of the property dedicated to a
    public equestrian trail, is fully consistent with the existing character of the neighborhood
    as a residential area focused on equestrian activities.
    3.     Water Quality and Drainage
    Relying on comments by Richard Horner, an expert in urban stormwater
    management, who reviewed certain documents concerning the stormwater management
    and drainage plans for the Project, SDR contends (1) the Project's stormwater
    management system, as currently planned, may not be adequate to prevent water runoff
    into the wetland habitat, resulting in a significant impact to the environment; and
    21
    (2) without an adequate erosion control system in place during construction, the wetland
    habitat could be damaged by erosion while the Project is being built. We discuss each
    issue in turn.
    a.   Stormwater Management Plan
    As an initial matter, it is important to note that the main documents specific to the
    Project upon which Horner based his understanding of the Project's stormwater
    management plan were (1) a Preliminary CEQA Drainage Study by Construction Testing
    and Engineering, Inc. (CTE, Inc.), dated April 1, 2010; (2) a Water Quality Technical
    Report by CTE, Inc., dated November 15, 2011; and (3) the tentative map for the Project.
    Horner stated that the stormwater management plans that he reviewed were too
    preliminary and not well-developed enough to determine whether they would adequately
    protect the environment. One thing Horner pointed out was that according to a United
    States Department of Agriculture (USDA) survey, the soil occurring in the vicinity of the
    Project includes a type of soil ("hydrologic soil group D"), which may not be infiltrative
    enough to make bioretention basins a proper choice for stormwater management, but that
    soil testing of the Project site had not been conducted to determine how much hydrologic
    soil group D was present.
    Horner summarized his analysis of the problems with the stormwater management
    plans, as reflected in the documents he reviewed, as follows: "The stormwater
    management plan rests principally on bioretention facilities, which work primarily by
    infiltrating runoff to the soil, also with some evaporation. The developer proposes this
    system on a site with soils that have not been characterized by adequate site-specific
    22
    testing, but that appear to have an extensive hydrologic soil group D component, the least
    infiltrative soils. The intention, apparently, is to use underdrains in some facilities, surely
    the ones thought to be in those D soils. However, without careful site investigation, it is
    little more than a guess if a given location will be in D or the more favorable B soils
    shown in the USDA survey. A bioretention cell in the D setting without an underdrain is
    very likely to fail by not retaining its influent runoff but instead discharging it on the
    surface. The [P]roject should not be considered for approval until the site soils and
    hydrogeology are thoroughly investigated . . . and the resulting information applied in a
    thorough reconsideration of the stormwater management plan." Based on this statement,
    Horner does not say that it is impossible to design an adequate stormwater management
    plan for the Project. Instead, he takes the position that the existing plan should be more
    closely considered, and perhaps revised, after soils testing is completed to determine the
    presence of hydrologic soil group D.
    Woodridge's engineering firm, CTE, Inc., responded to Horner's letter. It agreed
    with Horner that when excess hydrologic soil group D is present, it is not proper to rely
    solely on infiltration-based stormwater best management practices. However, CTE, Inc.
    pointed out that according to the standards that Woodridge is required to follow by the
    City, "if during grading it is determined that the post-compaction condition of soils where
    bio-retention basins will be located do not provide adequate infiltration characteristics,
    [Woodridge] would be required by the City to apply amendments to achieve necessary
    soils structure and percolation rates of between 0.5 and 3 inches per hour." Further, CTE,
    23
    Inc. explained that "according to the City's [Stormwater M]anual, all bioretention
    facilities are required to install underdrains to convey water that cannot infiltrate."
    As a condition for proceeding with the grading of the site, Woodridge is required
    to show compliance with the City's Stormwater Manual, which contains specific and
    detailed regulations for the design and implementation of a stormwater management plan,
    including those requirements for bioretention basins and soil infiltration characteristics
    discussed by CTE, Inc. Further, Woodridge must supply the City with a geotechnical
    report prior to obtaining a grading permit. Therefore, based on CTE, Inc.'s comments in
    response to Horner, and the requirement that the Project comply with applicable
    stormwater regulations, we conclude that the issues raised by Horner are not sufficient to
    raise a fair argument that the Project will have significant effect on the environment due
    to stormwater runoff. As CTE, Inc. explained, all of the issues raised by Horner are
    addressed either in the Project documents themselves, or through the City's conditions for
    approval of the Project, which require that Woodridge comply with detailed stormwater
    regulations prior to obtaining a grading permit.
    To the extent that Horner found that the Water Quality Technical Report by CTE,
    Inc., dated November 15, 2011, was not detailed enough to establish that Woodridge
    would meet the applicable stormwater quality regulations, CTE, Inc. explained that
    "[p]rior to the issuance of a grading permit, the City . . . will require a revised [Water
    Quality Technical Report] detailed for construction purposes." Indeed, the City's specific
    conditions for approving the Project include the following statement: "The preliminary
    'Water Quality Technical Report' dated November 15, 2011 by CTE, Inc. as well as the
    24
    preliminary grading plan drawings demonstrate that [applicable stormwater management
    plan] compliance generally can be achieved. However, this report and the preliminary
    drawings are not accepted as the final sizing and design of the required [stormwater
    management] facilities. This project shall be subject to stormwater quality regulations in
    effect at the time of issuance of grading permit." As explained in the City's conditions
    approving the Project, the requirements which Woodridge must meet for the grading
    permit to be issued are set forth in detailed applicable regulations, including the
    Hydromodification Management Plan section of the City's Stormwater Manual, best
    management practice methods, and additional requirements from the State Water
    Resources Control Board. SDR has identified no evidence in the record suggesting that
    Woodridge will be unable to comply with the applicable regulatory requirements in the
    more detailed stormwater management plan that it submits as a condition of obtaining a
    grading permit.
    SDR argues that the Water Quality Technical Report submitted for the purpose of
    CEQA review impermissibly defers the specification of a detailed stormwater
    management plan to a later stage of Project construction. We disagree. When
    considering whether a proposed project adequately mitigates possible environmental
    impact under CEQA, "[d]eferral of the specifics of mitigation is permissible where the
    local entity commits itself to mitigation and lists the alternatives to be considered,
    analyzed and possibly incorporated in the mitigation plan." (Defend the Bay v. City of
    Irvine (2004) 
    119 Cal. App. 4th 1261
    , 1275.) As relevant here, "a condition requiring
    compliance with regulations is a common and reasonable mitigation measure, and may be
    25
    proper where it is reasonable to expect compliance." (Oakland Heritage Alliance v. City
    of Oakland (2011) 
    195 Cal. App. 4th 884
    , 906 (Oakland Heritage Alliance).) Following
    this principle, case law holds that when project documents require a developer to prepare
    a project water quality plan to reduce discharge into stormwater runoff, including " 'best
    management practices,' " and the developer must comply with applicable codes, policies
    and practices to reduce runoff, a project does not impermissibly defer mitigation of
    possible environmental impact. (Endangered Habitats League, Inc. v. County of Orange
    (2005) 
    131 Cal. App. 4th 777
    , 795-796.) Here, where the City "has specified the criteria to
    be met," by identifying applicable stormwater regulations in its conditions for approval of
    the Project, and there is no basis in the record for concluding that Woodridge will not be
    able to comply with the applicable regulations, the level of detail of the Project's
    stormwater management plan "is sufficient at this early stage of the planning process."
    (Defend the Bay, at p. 1276.)19
    19     SDR relies on Communities for a Better Environment v. City of Richmond (2010)
    
    184 Cal. App. 4th 70
    and Preserve Wild Santee v. City of Santee (2012) 
    210 Cal. App. 4th 260
    to argue that Woodridge is required to submit a more detailed stormwater
    management plan for the purpose of CEQA review, instead of relying on a commitment
    to comply with applicable stormwater regulations and best management practices. Those
    cases are not persuasive here, as neither deals with a situation in any way similar to the
    application of well-defined preexisting stormwater management standards. Specifically,
    Communities for a Better Environment concerned the deferral of the preparation of a plan
    to mitigate greenhouse gases from a project. The court concluded that it was insufficient
    to defer the preparation of a plan when a project "merely proposes a generalized goal of
    no net increase in greenhouse gas emissions and then sets out a handful of cursorily
    described mitigation measures for future consideration" because "the perfunctory listing
    of possible mitigation measures . . . are nonexclusive, undefined, untested and of
    unknown efficacy" with "[t]he only criteria for 'success' of the ultimate mitigation plan"
    being "subjective judgment." (Communities for a Better Environment, at p. 93.)
    26
    b.     Erosion Control During Construction
    Horner's second criticism of the Project is that the documents he reviewed were
    "silent on construction-phase stormwater management" (underscoring deleted), and that
    "[w]ithout an effective erosion prevention plan, construction of the development is likely
    to increase the delivery of sediment and phosphate" to the wetland habitat and other
    bodies of water downstream.
    SDR relies on this comment to argue that construction of the Project could have a
    significant impact on the environment due to runoff during construction. We reject
    SDR's argument because documents other than those reviewed by Horner address the
    mitigation of any environmental risk from erosion during construction.
    First, the City's specific conditions for approval of the Project provides, "An
    erosion control system shall be designed and installed onsite during all construction
    activity. The system shall prevent discharge of sediment and all other pollutants onto
    adjacent streets and into the storm drain system. The City of Encinitas Best Management
    Practice Manual shall be employed to determine appropriate storm water pollution
    control practices during construction."
    Similarly, Preserve Wild Santee dealt with proposed mitigation measures for harm to a
    sensitive butterfly species. That project improperly deferred the development of a plan to
    mitigate those impacts because "it [did] not specify performance standards or provide
    other guidelines," and thus it was not possible to determine whether mitigation measures
    would be sufficient. (Preserve Wild Santee, at p. 281.) Here, in contrast, the City is
    requiring, as a condition of approval of the Project, that Woodridge comply with specific
    and well-defined stormwater regulations. (Oakland Heritage 
    Alliance, supra
    , 195
    Cal.App.4th at p. 906 ["a condition requiring compliance with regulations is a common
    and reasonable mitigation measure"].)
    27
    Second, addressing potential environmental harm from erosion during the rainy
    season, the City approved the Project on the condition that "no grading permit shall be
    issued for work occurring between October 1st of any year and April 15th of the
    following year, unless the plans for such work include details of protective measures,
    including desilting basins or other temporary drainage or control measures, or both, as
    may be deemed necessary by the field inspector to protect the adjoining public and
    private property from damage by erosion, flooding, or the deposition of mud or debris
    which may originate from the site or result from such grading operations."20
    Third, in approving the Project, the City required that Woodridge "obtain a
    grading permit prior to the commencement of any clearing or grading of the site." The
    City's municipal code requires that an application for a grading permit include erosion
    and sediment control plans, including descriptions of control measures. (Encinitas Mun.
    Code, § 23.24.150.)
    Finally, as stated in the City's conditions for approval, because the Project is a
    grading project of more than an acre, it must meet additional requirements from the State
    Water Resources Control Board, which include preparing a Stormwater Pollution
    Prevention Plan for approval by the City. As Woodridge points out, a Storm Water
    20     As the City has specifically incorporated the terms of its Best Management
    Practice Manual into its condition that the Project control erosion and stormwater
    management during construction, we reject SDR's contention that the City has
    improperly deferred the specification of mitigation measures to control harm to the
    environment during construction. The Best Management Practice Manual constitutes
    measurable standards for implementing and evaluating mitigation measures during
    construction.
    28
    Pollution Prevention Plan must address all pollutants and their sources, including sources
    of sediment associated with construction and construction site erosion.
    Accordingly, based on the fact that Woodridge is required to (1) implement
    specific measures to control harm to the environment during construction based on the
    City's Best Management Practice Manual and follow additional measures during the rainy
    season; (2) submit a grading plan including detailed erosion control measures during
    construction; and (3) prepare a plan complying with State Water Resources Control
    Board's standards for controlling pollution during construction, we conclude that despite
    Horner's statement that he had not reviewed any documentation regarding an erosion
    control plan during construction, there is no basis in the record for a fair argument that
    the wetland habitat will be significantly impacted during construction of the Project.
    4.     Traffic
    In arguing that there is a fair argument that the Project will have a significant
    impact on traffic, SDR contends that an analysis submitted by a neighborhood resident
    shows that the delay at certain intersections in the area will increase to above a threshold
    level of significance which, pursuant to CEQA, the City has adopted to measure whether
    traffic impacts caused by a project will be significant, warranting the preparation of the
    traffic impact study as part of an EIR.21
    21     The CEQA Guidelines state: "Each public agency is encouraged to develop and
    publish thresholds of significance that the agency uses in the determination of the
    significance of environmental effects. A threshold of significance is an identifiable
    quantitative, qualitative or performance level of a particular environmental effect, non-
    compliance with which means the effect will normally be determined to be significant by
    29
    The City has adopted thresholds of significance for traffic impacts based on
    guidelines developed by the San Diego Regional Traffic Engineers Council (SANTEC)
    and the local chapter of the Institute of Transportation Engineers (ITE). As relevant here,
    a significant impact occurs when the level of service (LOS) at an intersection is projected
    to be degraded to LOS "E" or LOS "F" as a result of a project. In addition, a significant
    impact occurs when an intersection already operating at LOS "E" or LOS "F" is projected
    to incur an increased delay of more than two seconds. Here, the City determined in
    connection with the initial study that the Project would not have a significant impact on
    traffic using the applicable criteria.
    A neighborhood resident, Ron Katznelson, who is not a traffic engineer, but rather
    an electrical engineer, prepared and submitted a study on the traffic impacts of the
    Project. Katznelson's study focused on projected delays during peak morning hours at
    three intersections on Rancho Santa Fe Road that are controlled by three- or four-way
    stop signs. Katznelson concluded that two of the three intersections would incur an
    additional delay of over two seconds in the southbound lane during peak morning
    hours.22 Katznelson also concluded that during peak morning hours the level of service
    at one of the intersections (Rancho Santa Fe Road and Lone Jack Road) would be
    the agency and compliance with which means the effect normally will be determined to
    be less than significant." (Cal. Code Regs., tit. 14, § 15064.7, subd. (a).)
    22     Specifically, Katznelson concluded that the southbound lane at the intersection of
    Rancho Santa Fe Road and Lone Jack Road would incur an increased delay of
    4.97 seconds, and the southbound lane at the intersection of Rancho Santa Fe Road and
    El Camino del Norte would incur an increased delay of 2.47 seconds.
    30
    degraded from LOS "E" to LOS "F," and that the overall delay at the intersection
    averaging the delay in all directions would exceed two seconds. Katznelson argued
    during his testimony before the City Council that these were significant impacts that
    required the preparation of a traffic study under the threshold of significance adopted by
    the City.
    Katznelson's study was reviewed and critiqued by traffic engineers at Linscott,
    Law & Greenspan and by the City's traffic engineering division. Both reviewers
    explained that Katznelson's conclusions were flawed in several respects, two of which are
    significant here.
    First, as Linscott, Law & Greenspan and the City's traffic engineering division
    explained, Katznelson applied an erroneous standard in estimating the number of peak
    morning commute trips as 18, overestimating by three trips. Specifically, Katznelson
    improperly relied in his analysis on SANDAG's 2006 San Diego Household Travel
    Study, Final Report, which, the City engineers explained, was not intended for use as
    vehicle trip generation data. As the City's traffic engineering division explained, "the
    incorrectly derived AM peak hour trip generation estimate is carried through the entire
    analysis" performed by Katznelson.
    Second, Linscott, Law & Greenspan explained that "[a]t signalized and 'All-Way-
    STOP-Controlled (AWSC) unsignalized intersections, it is the standard of practice to use
    the overall intersection delay and LOS to represent the intersection operations in
    determining the significance of project impacts." Because the three intersections at issue
    here are all AWSC intersections, in determining the significance of the increased
    31
    intersection delay during the peak morning hours, Katznelson should not have focused on
    the delay to the southbound lane alone. Instead, the delay in each direction should have
    been averaged.23 When the increased delays in each direction are averaged and the
    traffic volume data is based on the standard industry approach (not the approach used by
    Katznelson), the increased delay is less than two seconds at all three of the intersections
    on Rancho Santa Fe Road. Linscott, Law & Greenspan's comments contain a table
    showing the result of this analysis, demonstrating that the overall increased delay at each
    of the three intersections is less than two seconds and therefore not significant under the
    applicable threshold standards.24
    23     Similarly, the City's traffic engineering division explained that "[b]ased on
    national and local standard industry practice, all-way stop control . . . intersections report
    service level and delay on an intersection basis," but Katznelson's study presented the
    "intersections . . . on an approach delay basis only."
    24      For the first time in the trial court, SDR argued that it was improper for the City to
    rely on the conclusions in Linscott, Law & Greenspan's table showing the overall delay at
    each intersection because that table is inconsistent with the figures in the worksheets
    attached to Linscott, Law & Greenspan's analysis. SDR again raises that argument on
    appeal, contending that when certain mathematical calculations are performed, the
    worksheets show that the increased delay at the intersection of Rancho Santa Fe Road
    and Lone Jack Road is 2.1 seconds, not 1.7 seconds as shown in Linscott, Law &
    Greenspan's table. This issue was not raised with the City Council, and it may therefore
    not be raised for the first time in a petition for writ of mandate challenging the City
    Council's decision. CEQA review requires exhaustion of issues at the administrative
    level as a precondition to judicial review. (§ 21177.) "To advance the exhaustion
    doctrine's purpose '[t]he "exact issue" must have been presented to the administrative
    agency . . . .' " (Sierra Club v. City of Orange (2008) 
    163 Cal. App. 4th 523
    , 535.) Here,
    although Katznelson stated in his testimony before the City Council that "even under
    their criteria for average, there's one intersection that is past 2 percent," in context it is
    clear that Katznelson was referring to his own calculations of the intersection delay at
    Rancho Santa Fe Road and Lone Jack Road, which concluded the Project would result in
    an average intersection delay of 2.08 seconds. Katznelson never raised an issue based on
    32
    Here, because Katznelson's study was found to be flawed by experts in the field, it
    does not support a fair argument of significant impact to the environment due to the
    increased traffic on Rancho Santa Fe Road. Substantial evidence under CEQA may
    include "expert opinion supported by facts" (Cal. Code Regs., tit. 14, § 15384, subd. (b))
    but does not include "unsubstantiated opinion or . . . evidence which is clearly erroneous
    or inaccurate" (id., subd. (a)). Here because Katznelson is not a traffic engineer and his
    analysis was deemed to be out of line with industry standards by traffic engineering
    experts, his study does not constitute substantial evidence. (See Lucas Valley
    Homeowners Assn. v. County of Marin (1991) 
    233 Cal. App. 3d 130
    , 157 [agency could
    properly reject evidence concerning the impact of a proposed project when the "speakers
    were not qualified to render an expert opinion"]; Cathay Mortuary, Inc. v. San Francisco
    Planning Com. (1989) 
    207 Cal. App. 3d 275
    , 281 [testimony of certain witnesses did not
    establish a disagreement among experts on environmental impacts when that testimony
    "exceeded the limits of their expertise as urban planners"]; Wollmer v. City of Berkeley
    (2011) 
    193 Cal. App. 4th 1329
    , 1352 [critique of traffic consultant's study by a layperson
    did "not rise to the level of substantial evidence supporting a fair argument of a
    reasonable possibility that the project will have a significant effect on the environment"].)
    SDR's arguments as to traffic impacts fail without the support of Katznelson's
    study to back them up. SDR argues that the Project will cause a significant impact to
    traffic because it will (1) create a delay of more than two seconds at an intersection on
    the worksheet data contained in Linscott, Law & Greenspan's analysis, and there was
    accordingly no opportunity for the record to be developed to respond to the argument and
    introduce expert testimony on the proper interpretation of the worksheets.
    33
    Rancho Santa Fe Road, and (2) it will reduce the level of service at one intersection to
    LOS "E" to LOS "F." However, as we have explained, Katznelson's study is the only
    evidence supporting those conclusions. Linscott, Law & Greenspan concluded that the
    delay at each intersection will be less than two seconds and that the level of service at
    each intersection will stay the same.25
    5.     Neighborhood Streets and Safety
    Next, SDR takes issue with the initial study's conclusion that the Project would not
    have a significant impact in the sense that it would "substantially increase hazards due to
    a design feature (e.g., sharp curves or dangerous intersections)," SDR points out that the
    preexisting public roads leading to the Project site contain curves with 15 miles per hour
    advisory speeds and blind sharp turns. Based on this evidence, SDR argues that the
    Project would have a significant impact on the safety of the neighborhood unless the City
    requires it to have a secondary access route that avoided those hazards.
    We reject SDR's argument because it does not identify a significant impact to the
    environment caused by the Project itself. Instead, SDR is describing preexisting
    hazardous roadway conditions in the surrounding neighborhood that will impact the
    25      The parties dispute whether a drop in level of service from LOS "E" to LOS "F"
    constitutes a significant impact under the threshold standards adopted by the City and
    under "Circulation Element Policy 1.3" of the City's general plan. Specifically,
    Woodridge contends that a significant impact occurs only when the level of service is
    currently at LOS "D" or better and then drops to LOS "E" or "F." SDR contends that a
    drop from LOS "E" to LOS "F" also constitutes a significant impact. We need not
    resolve this dispute, as the only qualified expert analysis of the issue in the record shows
    that the level of service at the intersection will not drop as a result of the Project.
    Katznelson's study was the only analysis showing a drop between levels of service.
    34
    safety of the access route to the Project. The new road to be built on the Project site itself
    is a short, straight, private roadway with a wide cul-de-sac turn around at the end and
    does not contain hazardous road conditions. "[T]he purpose of an EIR is to identify the
    significant effects of a project on the environment, not the significant effects of the
    environment on the project." (Ballona Wetlands Land Trust v. City of Los Angeles
    (2011) 
    201 Cal. App. 4th 455
    , 473.) Thus, " '[t]o require an EIR . . . where the proposed
    project is challenged on the basis of preexisting environmental conditions rather than an
    adverse change in the environment, would impose a requirement beyond those stated in
    CEQA or its guidelines, and is thus prohibited.' " (South Orange County Wastewater
    
    Authority, supra
    , 196 Cal.App.4th at p. 1615.)
    6.     Parking
    SDR's final argument is that the Project will cause a significant impact to the
    environment in that more vehicles will be parked on neighborhood streets, and further,
    that streets congested with parked cars could "affect emergency response vehicles
    entering and exi[]ting the Project and the surrounding area."
    Case law holds that "CEQA considers a project's impact on parking of vehicles to
    be a physical impact that could constitute a significant effect on the environment."
    (Taxpayers for Accountable School Bond Spending v. San Diego Unified School Dist.
    (2013) 
    215 Cal. App. 4th 1013
    , 1051.) However, in this case, as we will explain, SDR has
    not pointed to any evidence in the record suggesting that the Project will significantly
    impact the parking of vehicles on public streets.
    35
    SDR identifies photographs in the record showing that, at times, numerous
    vehicles are parked on the street several blocks away from the Project site. Although this
    evidence does not establish that the same conditions exist closer to the Project site, where
    residents of the Project or their visitors might park, even if such conditions also existed
    near the Project, there is no basis for concluding that the Project would significantly add
    to any existing congestion. The Project provides at least two garage parking spaces for
    each residence and a driveway surface for parking. In addition, the private road that will
    be constructed as part of the Project provides for an eight-foot-wide paved parking
    easement on the west side of the road. In light of the fact that parking for several cars
    will be available at each residence plus additional parking will be available on the private
    road, SDR has identified no basis in the record to conclude that congested parking on
    surrounding public streets will be a problem created by the Project.26
    To the extent that SDR is arguing that any additional street parking caused by the
    Project will impede ingress and egress for emergency vehicles, that possibility was
    expressly considered and rejected by fire department authorities. The fire marshal
    testified at the City Council hearing that the private road planned for the Project was 32
    feet in overall width, which afforded an adequate 24-foot-wide roadway to be used as a
    26     SDR relies on a letter from a traffic engineer, Bill Darnell, which states that "lack
    of adequate parking will result in problems for the subdivision as well as the surrounding
    residents." However, what SDR fails to point out is that Darnell recommended that the
    Project should plan for two spaces for resident parking and an additional space for guest
    parking. As we have explained, each residence will have two garage and two driveway
    spaces, and there will be additional parking along the west side of the private road,
    exceeding Darnell's recommendation.
    36
    fire lane, even with the eight-foot-wide strip of parking on one side of the roadway, and
    the cul-de-sac was designed with sufficient room at the end for the fire engines to turn
    around. SDR cites no evidence to the contrary to show that emergency vehicles would
    not be able to access the area due to any increased parking on the streets.
    DISPOSITION
    The judgment of the trial court is reversed, and the trial court is directed to enter a
    new order denying the petition for writ of mandate.
    IRION, J.
    WE CONCUR:
    MCINTYRE, Acting P. J.
    O'ROURKE, J.
    37
    

Document Info

Docket Number: D066218

Filed Date: 10/28/2015

Precedential Status: Non-Precedential

Modified Date: 4/17/2021