Save Desert Rose v. City of Encinitas CA4/1

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NOT TO BE PUBLISHED IN OFFICIAL REPORTS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 This opinion has not been certified for publication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.

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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.

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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.)
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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.

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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.

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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.

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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]."

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 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
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 "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.)

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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."

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 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."

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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
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 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."

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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.

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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

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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.

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 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