Jensen v. City of Santa Rosa

Filed 5/1/18; Certified for Publication 5/24/18 (order attached)

IN THE COURT OF APPEAL OF THE STATE OF CALIFORNIA

FIRST APPELLATE DISTRICT

DIVISION FOUR

CHARLES T. JENSEN et al.,
Plaintiffs and Appellants,
A144782
v.
CITY OF SANTA ROSA, (Sonoma County
Super. Ct. No. SCV255347)
Defendant and Respondent;
SOCIAL ADVOCATES FOR YOUTH,
Real Party in Interest and Respondent.

This case arises from the City of Santa Rosa’s (City) decision to turn a 69-bed
defunct hospital into a facility called the Dream Center (sometimes “Project”), which
would house 63 young adults, ages 18 to 24, and would provide individual and family
counseling, education and job training, a health and wellness center serving the
community for ages 5 through 24, and activities for residents, including a pottery
throwing area, a half-court basketball area, and a garden to be tended by the residents.
The Dream Center was sponsored and largely funded by real party in interest, Social
Advocates for Youth (SAY).1 Two neighbors, Charles T. Jensen and Robert Turley
(appellants), challenged the Project under the California Environmental Quality Act
(CEQA) (Pub. Resources Code, § 21000 et seq.) on the grounds that, among other things,

SAY and the City have filed a joint respondents’ brief. Points made in that brief
1

will be referred to as the City’s arguments, though also made on behalf of SAY.
1
noise impacts from the Project required preparation of an environmental impact report
(EIR). The City instead issued a negative declaration signifying its conclusion that the
Project would not have a significant environmental effect and an EIR would not be
required. Appellants filed a petition for writ of administrative mandate (Code Civ. Proc.,
§ 1094.5) in superior court, where the City’s decision was upheld and the requested writ
denied. This appeal followed.
On appeal, the appellants focus on two specific sources of noise they claim
required preparation of an EIR: traffic noise from the south parking lot adjacent to the
Dream Center, and noise from the residents’ outdoor recreational activities. We conclude
there is no substantial evidence supporting a fair argument there would be a significant
noise impact from those sources. The parking lot noise impacts predicted by appellants
are largely hypothetical, given the City’s parking restrictions in that lot, and appellants’
impact calculations are based on data from a different project that cannot reasonably be
applied to the Dream Center in the manner advocated by appellants. Appellants’
argument that the noise from residents’ outdoor activities would constitute a significant
environmental impact is also based on a flawed analysis. As we explain below, any noise
impacts identified by appellants were not significant under CEQA and did not require
preparation of an EIR.
I. FACTUAL AND PROCEDURAL BACKGROUND
SAY is a non-profit organization founded in 1971 by four local community leaders
aiming to provide “hope, support, and opportunity to Sonoma County youth and their
families.” SAY operates several programs and facilities in Sonoma County focusing on
three core areas: housing, counseling, and jobs.
Conceived to serve children, teens, youth, and young adults, the SAY Dream
Center planned to provide an emergency shelter with up to 12 beds for homeless youth
for up to three months, and up to 51 beds for longer term transitional housing for
residents ages 18 to 24. The Dream Center would also offer counseling services for
individuals and families, health and wellness services for individuals 5 through 24, and
education, job skills training, and job placement services for youth and young adults.
2
Those served by the Dream Center would include children who have been physically,
sexually or emotionally abused, runaways, homeless youth, former foster youth, and
homeless young adults who have been unable to afford housing or find employment.
The Dream Center was to be housed in a converted facility that was the former
Warrack Hospital on a site located in southeast Santa Rosa. The hospital had been closed
in 2008, and the building had been donated to SAY in 2012. The facility included an
existing commercial kitchen to be used for job training and meal preparation for residents
and staff. The site had earlier been developed as a medical campus, including the former
and now vacant hospital building in the center of the site, as well as separate occupied
office and medical buildings and parking areas surrounding the central building. The
Dream Center property is bordered on two sides (north and east) by streets that separate it
from its neighbors, but on the south, it is bordered by single-family homes, separated
from them by a parking area, a wooden fence, and mature landscaping. To the west it
abuts to condominium-style single-family homes and a convalescent hospital.
On August 8, 2013, SAY filed applications for a conditional use permit (CUP),
rezoning, and design review necessary to implement plans for the Dream Center. Many
prominent community members and organizations publicly endorsed the Project. Prior to
and just after the applications were filed, the City held two neighborhood meetings to
allow for public input about the Dream Center. On December 6, 2013, the City prepared
a draft Initial Study/Negative Declaration which identified no significant effects on the
environment. After a 20-day public comment period, the City prepared a revised Initial
Study/Negative Declaration with responses to comments. On January 23, 2014, the City
of Santa Rosa Planning Commission (Commission) held a public hearing on the Project.
On that day, the Commission, by unanimous vote, passed resolutions adopting the
negative declaration, recommending rezoning of eight properties as necessitated by the
Project plans, and approving the CUP.
On February 3, 2014, one neighbor of the Project, Turley, appealed the
Commission’s decision to the Santa Rosa City Council (Council), later joined by Jensen.
On March 25, 2014, the Council held a public hearing. On that day, approximately four
3
hours before the scheduled hearing, appellants’ attorney submitted by email an 11-page
letter to the Council critiquing the Initial Study. Appellants’ letter mentioned another
noise study performed by the same acoustical consulting firm at a different site in the
City, and included in the record a copy of that study (Tower Market Study). Appellants
pointed out the Tower Market estimate of the noise created by cars and trucks. They did
not, however, articulate in the letter or in their presentation at the hearing the detailed
calculations they include in their appellate briefs.
At the conclusion of the hearing, the Council, by unanimous vote, adopted two
resolutions denying the appeal, and adopting the negative declaration, making findings
and determinations, and approving the CUP. A few days later the Council amended the
Santa Rosa City Code (City Code)2 to reclassify the eight properties. The Council’s
findings included: (1) the zoning amendment is consistent with the goals and policies of
all elements of the General Plan; (2) the site is physically suitable for the Project because
the site was originally developed to house public institutional and office land uses and the
infrastructure is adequate; and (3) the proposed rezoning is consistent with General Plan
policies, including but not limited to ensuring adequate sites are available for
development of a variety of housing types for all income levels, including transitional
housing and homeless shelters, expanding the supply of housing available to lower
income households, and supporting programs that address long-term solutions to
homelessness. The Council found that granting the CUP would not constitute a nuisance
or be injurious or detrimental to the public interest, health, safety, convenience, or
welfare, or materially injurious to persons, property, or improvements in the vicinity. It
also certified the Project was reviewed in compliance with CEQA. The Project was
approved with 26 conditions of approval (COA), including posting of a contact number
for any neighborhood concerns (COA 20.G) and quarterly meetings with neighboring
residents (COA 20.I). Opposition came largely, if not exclusively, from neighbors of the

2
On our own motion, we take judicial notice of the City Code, available online at
http://qcode.us/codes/santarosa (as of May 1, 2018). (Evid. Code, §§ 452, subd. (b) &
459.)
4
Dream Center, including appellants. On March 27, 2014, the City filed a Notice of
Determination reflecting adoption of the negative declaration without mitigation
measures.
On April 23, 2014, appellants filed a petition for writ of administrative mandate in
Sonoma County Superior Court, which was heard on January 8, 2015. The court denied
the petition. This timely appeal followed.
II. DISCUSSION
A. The Applicable Law
1. CEQA’s Requirements
Whenever a proposed project “may have a significant effect on the environment,”
the lead agency considering approval of the project must prepare an EIR. (Pub.
Resources Code, § 21151, subd. (a).) CEQA defines a significant effect on the
environment as “a substantial, or potentially substantial, adverse change in any of the
physical conditions within the area affected by the project,” including impacts on
“ambient noise.” (Guidelines,3 § 15382; Pub. Resources Code, §§ 21060.5, 21151,
subd. (b).) Appellants focus their appeal on increased noise levels at the southern border
of the Project resulting from outdoor recreational activities at the Dream Center
(gardening, pottery throwing, and basketball) and use of its south parking lot.
2. The “Fair Argument” Standard Applicable to the City
The standard for determining whether an EIR must be prepared is whether there is
substantial evidence in the record to support a “ ‘fair argument’ ” that a project may entail
significant environmental effects, even if there is other substantial evidence there will not
be such an impact. (Stanislaus Audubon Society, Inc. v. County of Stanislaus (1995) 33
Cal.App.4th 144, 151 (Stanislaus Audubon Society); Sierra Club v. County of Sonoma
(1992) 6 Cal.App.4th 1307, 1316; Guidelines, § 15064.) “The ‘fair argument’ test is
derived from [Public Resources Code] section 21151, which requires an EIR on any

3
The Guidelines for the Implementation of the California Environmental Quality
Act, California Code of Regulations, title 14, § 15000 et seq. (Guidelines).
5
project which ‘may have a significant effect on the environment.’ That section mandates
preparation of an EIR in the first instance ‘whenever it can be fairly argued on the basis
of substantial evidence that the project may have significant environmental impact.’
(No Oil, Inc. v. City of Los Angeles (1974) 13 Cal.3d 68, 75.) If there is substantial
evidence of such impact, contrary evidence is not adequate to support a decision to
dispense with an EIR. [Citations, including Guidelines, § 15064, subds. (g), (h).]
Section 21151 creates a low threshold requirement for initial preparation of an EIR and
reflects a preference for resolving doubts in favor of environmental review when the
question is whether any such review is warranted.” (Sierra Club, at pp. 1316–1317.)
Nevertheless, if the lead agency determines there is no substantial evidence in the whole
record before it that the project will have a significant effect on the environment, the
agency may issue a negative declaration. (Pub. Resources Code, § 21080, subd. (c)(l).)
3. Determining Whether an Impact is Significant
“The determination of whether a project may have a significant effect on the
environment calls for careful judgment on the part of the public agency involved, based
to the extent possible on scientific and factual data. An ironclad definition of significant
effect is not always possible because the significance of an activity may vary with the
setting. For example, an activity which may not be significant in an urban area may be
significant in a rural area.” (Guidelines, § 15064, subd. (b); see also id., subd. (c);
National Parks & Conservation Assn. v. County of Riverside (1999) 71 Cal.App.4th
1341, 1358.) “The lead agency has substantial discretion in determining the appropriate
threshold of significance to evaluate the severity of a particular impact.” (Mission Bay
Alliance v. Office of Community Investment & Infrastructure (2016) 6 Cal.App.5th 160,
192.)
The Guidelines encourage agencies to develop “thresholds of significance” to aid
them in determining when an environmental effect is significant. A threshold 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 the agency and compliance with which means the effect normally will be
6
determined to be less than significant.” (Guidelines, § 15064.7, subd. (a).) Thresholds of
significance are not used to determine automatically whether a given effect will or will
not be significant. Instead, thresholds of significance are indicative only that an
environmental effect that crosses the threshold “ ‘will normally be determined to be
significant,’ ” while effects not crossing the threshold “ ‘normally will be determined to
be less-than-significant’ ” by the agency. (Protect the Historic Amador Waterways v.
Amador Water Agency (2004) 116 Cal.App.4th 1099, 1108–1109; Guidelines, § 15064.7,
subd. (a).) Sample questions are set forth in Appendix G, printed following Guidelines
Public Resources Code section 15387, which may be considered “thresholds of
significance.” (See San Francisco Baykeeper, Inc. v. State Lands Com. (2015)
242 Cal.App.4th 202, 227.) CEQA does not set numeric noise thresholds in Appendix G.
The City marked all of the Appendix G threshold criteria either “no impact” or “less-
than-significant impact.”
4. Standard of Review
Appellants insist we must independently exercise our judgment in our review of
the City’s decision to issue a negative declaration. They argue application of the “fair
argument” standard is a question of law, and deference to the agency’s determination is
not required. (Stanislaus Audubon Society, supra, 33 Cal.App.4th at p. 151.) But this is
at best an oversimplification. “The fair argument standard Guidelines section 15064,
subdivision (f)(1), sets forth applies by its terms to determinations of a lead agency, not
of a court.” (Berkeley Hillside Preservation v. City of Berkeley (2015) 60 Cal.4th 1086,
1112.)
Rather, a city’s “decision to issue a negative declaration . . . is reviewed for
‘prejudicial abuse of discretion,’ which ‘is established if the agency has not proceeded in
a manner required by law or if the determination or decision is not supported by
substantial evidence’.” (Save the Plastic Bag Coalition v. City of Manhattan Beach
(2011) 52 Cal.4th 155, 171; see also, Clews Land & Livestock, LLC v. City of San Diego
(2017) 19 Cal.App.5th 161, 198 (Clews).) “ ‘Judicial review of these two types of error
differs significantly: While we determine de novo whether the agency has employed the
7
correct procedures, scrupulously enforcing all legislatively mandated CEQA
requirements, we accord greater deference to the agency’s substantive factual
conclusions. [Citation.] In CEQA cases, as in other mandamus cases, we independently
review the administrative record under the same standard of review that governs the trial
court.’ ” (San Francisco Baykeeper, Inc. v. State Lands Com., supra, 242 Cal.App.4th at
p. 216; see generally, Gentry v. City of Murrieta (1995) 36 Cal.App.4th 1359, 1374–1375
(Gentry); Quail Botanical Gardens Foundation, Inc. v. City of Encinitas (1994)
29 Cal.App.4th 1597, 1602–1603 [courts employ “a hybrid, quasi-independent standard
of review” in which their “ ‘function is to determine whether substantial evidence
supported the agency’s conclusion as to whether the prescribed ‘fair argument’ could be
made’ ”].) Put otherwise, “[a] city’s decision to rely on [a negative declaration] under
CEQA is reviewed for abuse of discretion under the ‘fair argument’ standard.” (Wollmer
v. City of Berkeley (2009) 179 Cal.App.4th 933, 939.) The petitioner bears the burden of
proof to demonstrate by citation to the record the existence of substantial evidence
supporting a fair argument of significant environmental impact. (Porterville Citizens for
Responsible Hillside Development v. City of Porterville (2007) 157 Cal.App.4th 885, 899
(Porterville Citizens).)
B. The Santa Rosa Noise Ordinance
City Code section 17-16.030 sets forth certain “base” ambient noise levels tied to
the character of various parts of the City: “The following criteria will be used as a base
(ambient noise level) from which noise levels can be compared.”
Sound Level A (decibels) Community
Zone Time Environment Classification
R1 and R2 10 p.m. to 7 a.m. 45
R1 and R2 7 p.m. to 10 p.m. 50
R1 and R2 7 a.m. to 7 p.m. 55
Multi-family 10 p.m. to 7 a.m. 50
Multi-family 7 a.m. to 10 p.m. 55
Office & Commercial 10 p.m. to 7 a.m. 55
Office & Commercial 7 a.m. to 10 p.m. 60
Intensive Commercial [fn omitted] 10 p.m. to 7 a.m. 55
Intensive Commercial 7 a.m. to 10 p.m. 65
Industrial Anytime 70
Appellants in earlier procedural phases of their challenge have treated the above
listed “base” levels as maximum allowable noise levels for the times of day indicated.
8
But that is not correct. Rather, as the City Code states, the base levels are intended to be
used for comparative purposes. The values reflected in the table above represent standard
or normally acceptable noise levels for the zones and times indicated. As we construe the
City Code, they do not constitute thresholds of significance.
Certain noise-generating sources are governed by specific maximum decibel (dB
or dBA)4 levels in the Noise Ordinance, such as noise generated by mechanical
equipment, which must not exceed 5 dBA Leq more than the base levels identified above.5
(City Code, § 17-16.120.) The City Code dictates no standard numeric measure
expressed in decibel levels for other types of noise involved at the Dream Center, such as
parking lot noise or the residents’ recreational activities. As SAY’s noise expert told the
Council, “the noise ordinance actually only regulates machinery and equipment. It
doesn’t regulate outdoor use such as the pottery area, such as the basketball court, that
sort of thing.” Those types of noise, he explained, are governed by the General Plan,
which allows up to 60 dBA Ldn6 in residential neighborhoods. Even from that level the

4
The designation dBA, as distinguished from dB (decibel), indicates an A-
weighted value. The “A-weighted” noise level attempts to mimic the disruptive effect of
noise on the human ear by deemphasizing the very low and very high frequency
components of noise. The noise level meters used in the Noise Study filtered noises so
that the dBA values they registered were A-weighted.
5
Other regulated sound sources include radios and televisions, drums, hawkers,
animals and leaf-blowers. (City Code, §§ 17-16.070 to 17-16.125.) Amplified sound is
similarly regulated. (City Code, §§ 17-16.160 to 17-16.210.) There is also a numeric
limitation on noise from vehicles that corresponds to the Vehicle Code standards. (City
Code, § 17-16.150.)
6
Ldn, the average day/night noise level, is the average A-weighted noise level
during a 24-hour day, obtained after addition of 10 decibels to levels measured in the
night between 10:00 p.m. and 7:00 a.m. This measure reduces the highs and lows within
the decibel range and allows comparison using only one value. A related metric, known
as Leq, or “equivalent noise level,” is the average A-weighted noise level during any
given measurement period, typically of 15 minutes’ duration or more. For residential
areas, the City Code uses measurement periods to separately designate allowable noise
values for day, evening and nighttime hours. (City Code, § 17-16.030.)
9
noise expert said, “you can go up about five decibels” before a significant impact would
occur.
We conclude the noise sources concerned in this appeal are governed by City
Code section 17-16.040, an issue we determine de novo. (Clews, supra, 19 Cal.App.5th
at p. 185.) That section establishes a set of criteria to be considered in determining
whether a noise impact violates the Noise Ordinance, in which the level of noise is but
one factor: “[I]t is unlawful for any person to willfully make or continue, or cause to be
made or continued, any loud, unnecessary, or unusual noise which disturbs the peace or
quiet of any neighborhood or which causes discomfort or annoyance to any reasonable
person of normal sensitiveness residing in the area. [¶] The standards which shall be
considered in determining whether a violation of the provisions of this section exists shall
include, but not be limited to the following:
(A) The level of noise;
(B) The intensity of the noise;
(C) Whether the nature of the noise is usual or unusual;
(D) Whether the origin of the noise is natural or unnatural;
(E) The level and intensity of the background noise, if any;
(F) The proximity of the noise to residential sleeping facilities;
(G) The nature and zoning of the area within which the noise emanates;
(H) The density of the inhabitation of the area within which the noise emanates;
(I) The time of the day or night the noise occurs;
(J) The duration of the noise;
(K) Whether the noise is recurrent, intermittent or constant;
(L) Whether the noise is produced by a commercial or noncommercial
activity.” (City Code, § 17-16.040.)

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 C. The Noise Study
To assess the noise impacts of the Project on the surrounding residences, SAY
hired Fred Svinth of Illingworth & Rodkin, Inc., an engineering firm specializing in
acoustics and air quality. Svinth performed a Noise Study for the Project, concluding
there were no significant noise impacts. The Noise Study was incorporated into the
Initial Study for the Project by the City and relied upon in reaching its decision to issue a
negative declaration.
In considering noise impacts, Svinth explained that allowances must be made for
the difference between the more disruptive effect of noise at night versus during the day.
To take account of these differences, experts calculate a “day/night average noise level”
(Ldn) by adding 10 dBA to the nighttime measured noise level stated as an equivalent
noise level (Leq). Svinth calculated an overall two-day day/night average noise level of 52
dBA Ldn. A sound level meter at the southwest corner of the Project area showed slightly
higher readings, resulting in a calculated value of 53 dBA Ldn.
The Noise Study pointed out that under the General Plan, “[s]ingle family
residential uses are considered to be normally acceptable in areas with a noise
environment of Ldn of less than 60 dBA and conditionally acceptable in areas exposed to
an Ldn of 55 to 70 dBA.”
In addition to the “base ambient noise levels” established under City Code section
17-16.030, as reflected in the Table on page 8, above, Svinth reported actual measured
noise levels: hourly daytime noises at the south border of the Project ranged from 45 to
56 dBA (7 a.m. to 10 p.m.), and average hourly nighttime noise levels (10 p.m. to 7 a.m.)
ranged from 41 to 47 dBA.7 Svinth did not break out a separate evening noise level and

7
The noise measurements for the Noise Study were made during a 48-hour period
in August of 2011, long before the Dream Center project was proposed. Two sound level
meters, one at the southern property line of the Project near the southeast corner, and one
at the southwest corner, recorded historical measurements. These were used in the Noise
Study, since there had been no major changes in the neighborhood in the interim.
Warrack Hospital had been closed in 2008, so the noise level measurements taken in
2011 and used in the Noise Study showed results with an empty hospital building.
11
did not calculate separate equivalent noise levels for daytime and nighttime noise (Leq).
Instead, Svinth consistently used the day/night average to assess noise impacts. (See
fn. 6, ante.)
He explained that a greater increase in noise levels is tolerated in areas that are
quieter, such as the Dream Center neighborhood, which remain under the base noise
levels specified in the Noise Ordinance. For such projects, a 5 dBA Ldn increase in
existing noise would establish the noise impact threshold, while for projects in noisier
areas, where the existing ambient noise level was above the base levels set forth in the
City Code, an addition of 3 dBA Ldn would mark the noise significance threshold. Svinth
explained at the Council hearing that these dBA increases in noise do not by themselves
establish a violation of the Noise Ordinance; they are but a threshold for a CEQA
determination of significance.
In his Noise Study, Svinth identified “significance criteria” for the Project,
drawing upon the sample questions propounded in Appendix G to the Guidelines. We
are concerned with criteria one and three: “1) A significant noise impact would result if
the project would expose persons to or generate noise levels that would exceed applicable
noise standards presented in the General Plan or Noise Ordinance;” and “3) A significant
impact would be identified if operation of, or traffic generated by, the project would
substantially increase noise levels, or exceed Noise Ordinance limits at sensitive receivers
in the vicinity. Considering that the existing noise environment at noise sensitive uses on
the project periphery are below the normally acceptable noise level standard, a substantial
increase would occur if noise levels with the project would be 5 dBA Ldn or greater above
existing conditions.” As we read the document, criterion one defers to pre-existing
standards in the Noise Ordinance and General Plan, while criterion three sets forth a
numeric significance threshold.
Since Svinth had calculated an existing Ldn of 52 at the south border and 53 at the
southwest tip of the Project, applying Svinth’s third criterion, we infer the Project would
cross the significance threshold if the projected Ldn exceeded 57 dBA at the southern
boundary or 58 dBA Ldn at the southwest tip of the Project. Svinth compared the impact
12
of outdoor activities (a maximum of 53 Ldn) and traffic noise (a maximum increase of
1 dBA Ldn) to the existing Ldn levels at the Project and concluded there was no significant
impact.
Svinth limited his analysis of traffic noise to additional traffic on the streets
surrounding the Dream Center based on the assumption there would be no use of the
parking lot on the southern border of the Project after regular operating hours. This
assumption was reinforced by the City when it imposed on the Project a COA that
allowed only SAY employees to park in the south lot, and only during the day.
D. Appellants’ Fair Argument Theory on Noise Levels
1. Appellants’ Arguments
Appellants urge us to abandon Svinth’s use of Ldn calculations and to use Leq
calculations instead, which would result in three separate points of comparison for
daytime, evening and nighttime noise. Appellants seek to persuade us there is a fair
argument that the existing ambient noise levels utilized in the noise analysis should have
been reduced below the values specified in the Noise Ordinance because the vicinity of
the Dream Center was an exceptionally quiet neighborhood. Then, using a methodology
employed by Svinth in a different noise study prepared for a different project in a
different part of town, they contend significant noise impacts originating from the
parking lot and outdoor activities would increase ambient noise levels 5 dBA Leq or more,
which they contend would constitute a “significant impact” requiring an EIR.8
Employing an averaging technique ostensibly derived from the Tower Market
Study, and working with a chart (not easily decipherable) from the Noise Study,
appellants purport to have calculated the existing ambient noise levels for the Project.
These calculations were not a part of the Noise Study, were not presented to the City in
the appeal process, and no expert has confirmed their accuracy. The numbers do not

8
This is a slight distortion of Svinth’s statement that an increase of 5 dBA Ldn
would establish a noise threshold, but they argue based on the Tower Market Study that
an increase of 5 dBA Leq would not just establish a noise effect threshold, but a noise
level maximum that could not be exceeded without preparation of an EIR.
13
appear in the administrative record and first appeared in appellants’ reply brief in
superior court. For that reason alone, we would be justified in ignoring appellants’
calculations.9 (See Code Civ. Proc., § 1094.5, subd. (e); Western States Petroleum Assn.
v. Superior Court (1995) 9 Cal.4th 559, 571, 573 [traditional mandamus]; Porterville
Citizens, supra, 157 Cal.App.4th at pp. 893–899 [same].) As the City rightly observes,
by manipulating data and drawing conclusions from charts and numbers in the two noise
studies, appellants have cast themselves in the role of noise experts. But even if we were
to accept these base level calculations at face value, as we shall discuss, the remainder of
appellants’ assumptions and calculations casts the sum of their work into doubt and
prevents us from finding there is a fair argument that an EIR is required.
2. The Tower Market Noise Study
The Tower Market Study, also prepared by Svinth, assessed impacts occasioned
by development of a 24-hour convenience market and gas station in a different, more
densely populated part of Santa Rosa, where existing noise levels were higher than in the
area of the Dream Center and higher than the base ambient noise levels in the Noise
Ordinance.10 Despite the differences in setting, appellants point to the Tower Market
Study as an alternative means of analyzing noise impacts, and they claim if the Tower
Market method had been used in analyzing noise impacts from the Dream Center, it
would have revealed substantial evidence of a fair argument that noise would create a

9
Issuance of a conditional use permit is a quasi-judicial function properly
reviewed by administrative mandate (Harrington v. City of Davis (2017) 16 Cal.App.5th
420, 434), which is how appellants proceeded in this case. Appellants made no showing
under Code of Civil Procedure section 1094.5, subdivision (e), either in the trial court or
in this court.
10
Because the Tower Market neighborhood was zoned multi-family, we infer it
was more densely populated than the area to the south of the Dream Center. Hence, the
base ambient noise levels under the Noise Ordinance were 55 dBA during the day,
55 dBA in the evening, and 50 dBA at night (City Code, § 17-16.030; see Table on p. 8,
ante.) Pre-existing conditions at the Tower Market site already exceeded those levels.
(See fn. 12, post.)
14
significant environmental impact along the Project’s southern border from parking lot
noise and residents’ outdoor activities.
Appellants use the Tower Market Study in two different ways. First, they urge us
to adopt the methodology used by Svinth in the Tower Market Study for analysis of the
Dream Center noise impacts. Second, they borrow from the Tower Market Study specific
noise values for cars and trucks and assume these raw noise data would apply as impact
data at the southern property line of the Dream Center. Although we can agree
conceptually that the Tower Market methodology could just as well have been employed
for the Dream Center noise analysis, appellants fail to convince us the numbers they
purport to derive using that technique—and specifically the noise impacts they predict—
are creditable evidence of a significant impact under CEQA.
In the Tower Market Study, Svinth broke the day into three time periods instead of
two and used three values of Leq instead of a single Ldn value. He measured the existing
base ambient noise level for each period of the day with two meters, one at the nearest
property line and another at an outdoor area of public common use. We will focus on the
effects at the nearest property line, which also showed the biggest impacts. Svinth then
added 5 dBA Leq to each period’s actual base ambient noise level to get the Leq at which
the threshold of significance would be crossed, which he called the “site specific
(adjusted) allowable noise levels.”11 Finally, Svinth compared the predicted noise from
Tower Market operations to the site specific allowable noise levels. He then concluded
that noise from Tower Market operations could exceed the maximum allowable Leq
during some periods, and recommended mitigation measures to reduce those impacts.
The Tower Market Study also recognized a decibel value for vehicles: noise from
a passing car going 15 mph would range from 55-65 dBA at 25 feet, and trucks would
generate noise in the range of 60-80 dBA at 50 feet, depending upon the type of truck. It

11
The measured values at the property line were 61 dBA Leq during the day,
60 dBA Leq in the evenings, and 55 dBA Leq at night. By adding 5 dBA to each of those
values, Svinth calculated the “site specific (adjusted) allowable noise levels” as 66 dBA
Leq (day), 65 dBA Leq (evening) and 60 dBA Leq (night) at the multi-family property line.
15
appears from the Tower Market Study that the raw decibel levels from cars and trucks do
not translate directly to a final noise impact at the relevant point of interest, however.
Such values did not result in an 80 dBA Leq at the nearest property line in the Tower
Market Study; rather, the impact numbers were calculated as 48 to 63 dBA resulting from
cars, 56 to 66 dBA resulting from light trucks, and 62 to 75 dBA resulting from heavy
fuel trucks. Svinth did not include a calculation of the average noise from cars and trucks
at the nearest property line using either an Ldn or a day-evening-night Leq average.
3. Appellants’ Calculations Using Leq Instead of Ldn
Svinth’s Ldn calculation in the Noise Study, by definition, did not distinguish
between evening hours and nighttime hours. Appellants treat this as a flaw in the study,
perhaps, they suggest, as a result of the City’s pre-ordained decision to approve the
Dream Center project. They insinuate Svinth chose to use Ldn numbers for comparison in
his study for the very purpose of “reduc[ing] the significance of a noise impact” at the
Project.12
Appellants insist that by using Leq values for daytime, evening and night, a fair
argument can be made that noise from the Dream Center would create a significant
environmental impact in the residential neighborhood on its southern border. The trial
court called the Leq versus Ldn argument a “distinction without a difference,” and we tend
to agree. The two methods of presenting noise evidence are simply different means of
averaging noise levels for more meaningful comparison and would not be expected to
cause a significant difference in result when considering noise impacts.

12
Svinth stated in his Noise Study that he would “use Leq for purposes of
determining noise with respect to the base ambient noise levels,” but then consistently
used single day/night average (Ldn) values instead. Appellants would have us treat this as
a sleight of hand by Svinth, accusing him of unjustifiably “switch[ing]” his mode of
analysis to intentionally “reduce the significance of a noise impact.” We take a less
jaundiced view of Svinth’s work. We defer to the City’s implied assessment that Svinth
was credible and his work was performed with integrity. (See Stanislaus Audubon
Society, supra, 33 Cal.App.4th at p. 151 [lead agency given the “benefit of a doubt on
any legitimate, disputed issues of credibility”].)
16
 Nevertheless, to come up with their own competing base dBA Leq numbers,
appellants extrapolate from measured values, calculating the existing values for the south
border of the Project as: as 49.9 dBA Leq in the daytime (7 a.m. to 7 p.m.), 47.5 dBA Leq
in the evening (7 p.m. to 10 p.m.), and 43.6 dBA Leq at night (10 p.m. to 7 a.m.) based on
actual measurements taken in 2011. They suggest using these numbers as a starting point
for assessing noise impacts, rather than the 55-50-45 dBA base levels provided in City
Code section 17-16.030. (See Table, p. 8, ante.)
Appellants then add 5 dBA to each of the three time periods in the day, reasoning
that the resulting sums would establish the maximum non-significant values for each time
period or the same sort of “site specific adjusted allowable noise levels” calculated in the
Tower Market Study, but not in the Noise Study: 54.9 dBA Leq (daytime); 52.5 dBA Leq
(evening); and 48.6 dBA Leq (night). They justify this step by reference to the Tower
Market Study, where Svinth made a similar calculation. Appellants would have us treat
these numbers as absolute maximum noise limits above which a significant impact would
be found. Svinth clarified at the Council hearing, however, that a 5 dBA increase is
considered the “threshold of significance,” not an absolute maximum. He said “60” dBA
is the allowable limit under the General Plan. He further opined, “this project will go
nowhere near that.” Hence, we question whether appellants’ calculated numbers
constitute substantial evidence of a fair argument on both legal and factual grounds.
Although they present their numbers as scientific fact, we find appellants’
calculations are essentially opinions rendered by nonexperts, which do not amount to
substantial evidence. (Gentry, supra, 36 Cal.App.4th at p. 1417 [“dire predictions by
nonexperts” not substantial evidence]; accord, Porterville Citizens, supra,
157 Cal.App.4th at p. 899.) Though appellants imply that Svinth himself approved of
their calculations and their use of data from the Tower Market Study, his actual statement
was ambiguous and cannot be read as an endorsement of calculations appellants had not

17
even performed at the time.13 On the contrary, even after considering the points raised in
their 11-page letter, Svinth confirmed at the hearing before the Council that noise impacts
from the Dream Center would not violate either the Noise Ordinance or the General Plan.
E. Parking Lot Noise
Appellants argue noise from the Project parking lot “could violate the City’s
ambient base noise level limits.” Because the COA imposed by the City does not
prohibit traffic through the south parking lot (as opposed to parking in that lot),
appellants argue “cars (or delivery trucks) would be permitted to come and go at any time
of the day or night. They would be separated from residential homes by only a wooden
fence of minimal noise attenuating character.” Even if we accept appellants’
presumption that motorists will drive through the south parking lot, we find reason to
doubt appellants’ noise impact predictions.
We begin with the obvious. At Tower Market, traffic and parking lot noise
predictably would be different from, more continuous than, and louder than in the south
parking lot of the Dream Center. It is reasonable to believe there would be a more or less
constant stream of cars arriving at and departing from a 24-hour convenience center and
gas station, including at night. There would be frequent deliveries to the market and loud
fueling trucks servicing the gas station. In contrast, cars passing through the south
parking lot of the Dream Center would be expected to do so far less frequently, delivery
truck traffic would be “minimal” or non-existent, and fuel trucks would not be in the
picture at all. The two projects are not similar and we do not feel confident importing
data from a wholly different noise study into the Dream Center study, at least in the
manner appellants ask us to use that data.

13
Appellants suggest Svinth himself approved their use of the Tower Market
Study as “valid.” Svinth said, “and then the parking, it’s kind of interesting that they
used another study that I did for a gas station for the parking lot noise. And that’s fine.
Those levels are all valid.” It is unclear how far Svinth intended to go in vouching for
appellants’ theory. We do not read his comments as endorsing appellants’ detailed
calculations or their argument that parking lot noise impacts from two very different
projects would be the same.
18
 As noted above, Svinth did set forth in the Tower Market Study that noise
associated with a passing car ranges from 55-65 dBA at 25 feet, and noise from trucks
runs as high as 60-80 dBA at 50 feet, depending on the type of truck. Because these
levels greatly exceed appellants’ calculated maximum noise levels (54.9 dBA Leq
(daytime), 52.5 dBA Leq (evening), and 48.6 dBA Leq (night)), appellants insist there is a
fair argument that traffic noise in the south parking lot would create a significant noise
impact along the southern border of the Dream Center at all times of day and night.
Appellants simply take the range of noise from cars and trucks (55-80 dBA) and assume
those numbers would apply as noise impacts at the southern border of the Dream Center.
We reject appellants’ parking lot noise arguments for three reasons: (1) we lack
confidence in appellants’ predicted noise impacts, which amount to nonexpert opinion;
(2) appellants’ predictions are based on speculation about traffic, given parking
restrictions in the south lot and the fact that the main entrance to the site is on the north
side; and (3) appellants’ reading of the Noise Ordinance is inconsistent with ours.
First, appellants use raw data from the Tower Market Study which does not
include an average noise impact calculation. That study says, “a passing car” causes
noise in the range of 55-65 dBA as it passes at 15 mph, but that says very little about
what the noise impact will be over the course of a day or an evening. To predict the noise
value over time, it would be necessary to calculate some sort of average noise level (Leq
or Ldn). This is illustrated by the fact that even at Tower Market, which undoubtedly
anticipated greater traffic passing through its parking lot, the impact at the nearest
property line was not simply calculated as 80 dBA Leq as appellants suggest it should be
at the Dream Center, arguing that noise from cars and trucks would exceed their
calculated noise thresholds by as much as 31 dBA at night. Instead, Svinth reported the
noise resulting from cars and trucks in Tower Market’s parking lot as a range of decibel
levels, none of which was as high as 80 dBA. Even if we accept as a general matter that
cars and trucks make noise in the range of 55-80 dBA, we still cannot accept appellants’
position that those dBA values can simply be imported into the Dream Center Noise
Study as noise values on the southern border. Such a view is not backed up by any expert
19
opinion and is inconsistent with the treatment of those same numbers in the Tower
Market Study. It appears to us that further refining calculations by an expert would be
necessary to predict an accurate dBA Leq or Ldn noise level at the first residential property
line.
Thus, appellants’ argument that the noise impacts from the parking lot would be
55 to 80 dBA Leq at the southern border is not supported by substantial evidence.
Substantial evidence to support a fair argument 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.” (Guidelines, § 15384,
subd. (a); Pocket Protectors v. City of Sacramento (2004) 124 Cal.App.4th 903, 927–928;
League for Protection of Oakland’s etc. Historic Resources v. City of Oakland (1997)
52 Cal.App.4th 896, 905.) Substantial evidence supporting a fair argument must be of
“ ‘ponderable legal significance . . . reasonable in nature, credible, and of solid
value.’ ” (Lucas Valley Homeowners Assn. v. County of Marin (1991) 233 Cal.App.3d
130, 142.) Appellants’ noise predictions do not meet that standard.
We further regard appellants’ arguments as resting on supposition and
hypothesis, rather than fact, expert opinion, or reasonable inference. Appellants all
but ignore the parking restriction that allows only SAY employees to park in the
south lot, and only during the day, calling it a “last minute maneuver” by the City
that leaves intact their fair argument of excess parking lot noise. Yet, there has been no
showing the COA would be ignored or ineffective, and we will not indulge appellants’
invitation to ignore it.14 Appellants emphasize the COA does not prevent cars from
driving through—as opposed to parking in—the south parking lot. They point out all of
the parking lots are connected, with no barriers between them. Therefore, they rely on
“[c]ommon sense” to suggest that residents, residents’ guests, and delivery trucks will

14
Appellants claim even if the parking restriction is enforced, the use of the south
parking lot by SAY employees during the day would have a significant noise impact on
the Project’s south side neighbors, again using the same traffic noise data from the Tower
Market Study. Because we cannot accept appellants’ use of this data as impact data at
the southern boundary, we reject this contention as well.
20
drive through the south parking lot to get to other parking areas or places within the
Dream Center complex. Appellants argue these hypothetical trips could happen at “any
time of day or night” because the COAs do not impose any time restrictions on driving
through the Project’s south parking area. We reject these suppositions as not supported
by substantial evidence.
The fact is the parking supply on site is more than adequate to accommodate the
proposed new uses by the Dream Center, in addition to existing ongoing uses, and the
south parking lot provides only a small part of the parking supply. The main entry to the
Dream Center is on the north side of the site. Most of the residents of the Dream Center
are not expected to own cars or to use parking spaces and are not permitted to park in the
south lot at all. The maximum number of visitors on site requiring parking at any one
time will be 15, and visitors will not be allowed to park in the south lot. In addition, there
is no reason trucks would need to drive through the south parking lot to access the
loading zone. Delivery trucks would normally access the site via the main entrance on
the north side of the property. And of course, the noisiest of the Tower Market trucks—
those bringing fuel to the gas station—would have no business at the Dream Center
whatsoever. Hence, appellants’ prediction that trucks and cars will drive through the
south parking lot at all hours of the day and night is most improbable and not a fair
inference from the evidence. Similarly, appellants’ doubt about whether drivers will
choose to abide by the no parking rule is pure speculation.
Finally, we disagree with appellants to the extent they suggest a 5 dBA Leq
increase over pre-existing conditions would constitute a violation of the Noise Ordinance
under Svinth’s first criterion. We construe the Noise Ordinance as providing a more
flexible and qualitative approach than appellants acknowledge. The decision whether a
noise violation has occurred depends on multiple factors, not simple numeric
calculations, including the intensity of the sound, whether the sound emanates from a
natural or unnatural source, is usual or unusual, what time of day it occurs, and its
duration. (City Code, § 17-16.040.) Given our interpretation of the City Code, we do not
agree with appellants’ setting a hard-and-fast maximum noise level at 5 dBA above
21
existing levels. Svinth told the Council the maximum noise level for the neighborhood
around the Dream Center was 60 dBA Ldn under the General Plan. The noise generated
by traffic in the Dream Center’s south parking lot would not approach that level,
appellants’ nonexpert speculation notwithstanding. We conclude appellants have
presented no substantial evidence of a fair argument that noise from the south parking lot
would create a significant environmental impact.
F. Noise from Dream Center Recreational Activities
SAY planned outdoor recreation areas for the Dream Center’s young residents,
including a community garden, a half-court basketball area,15 and a pottery throwing area.
The pottery throwing area was approximately 90 feet from the southern boundary of the
Dream Center, the garden was approximately 105 feet from that border, and the
basketball court was approximately 300 feet from it. Basketball was the noisiest of the
activities, but the Noise Study concluded the basketball court would create less noise at
the southern border than the pottery and gardening activities because it was located
farther away. A COA allowed participants to engage in these activities only during the
day (no later than 9:00 p.m.). No outdoor amplified music was allowed at any time.
Because Dream Center residents would be allowed to engage in these pastimes
until 9:00 p.m., and based on appellants’ own calculated maximum allowable ambient
noise level of 52.5 dBA Leq between 7:00 p.m. and 9:00 p.m., appellants claim to identify
a potentially significant noise impact in the evening hours from Dream Center
recreational activities. But that prediction relies on a range of dBA values, without
timeframes assigned, not expressed as Leq or Ldn averages. According to the Noise Study,
the outdoor activities at the Project could create noise in the following ranges: Pottery
Making: 48-55 dBA; Community Gardening: 54-57 dBA; Basketball: 50-52 dBA. No

15
Respondents claim the basketball court was eliminated from the Dream Center
plans after the Project was approved and suggest in their respondents’ brief we take
judicial notice of that fact. They did not file a separate motion as required by rule
8.252(a), California Rules of Court. Hence, we do not take judicial notice and do not
consider the issue relating to basketball noise to be moot.
22
specific Leq numbers were assigned to these activities corresponding to times of day.
Again, Svinth used the values of 51 dBA Ldn for basketball and 53 dBA Ldn for gardening
and pottery making. The southern border already was subject to 52 dBA Ldn, and the
southwest corner was 53 dBA Ldn, so the Noise Study concluded these activities would
not create significant environmental impacts, which Svinth confirmed in person at the
Council hearing. In fact, Svinth said his Noise Study had overstated the impact of noise
from outdoor activities by calculating use for longer hours than residents would typically
use the facilities.
Nevertheless, appellants claim noise from gardening activities and making pottery
would conceivably exceed the existing ambient noise level by 5 dBA or more, either
bringing it, they argue, into direct violation of the Noise Ordinance under Svinth’s
criterion one, or raising noise levels “substantially” under criterion three. (See also
Guidelines, Appendix G, XII(a), foll. § 15387.) Appellants’ vague and hard-to-grasp
methodology appears to require us to compare the highest possible predicted noise levels
from the outdoor activities to appellants’ own calculated maximum allowable noise
levels, rather than comparing an average noise value, such as the Ldn used by Svinth, with
the base levels identified in the City Code. (City Code, § 17-16.030.) We cannot regard
this as a legitimate factual or scientific basis for finding a significant impact, and it is not
supported by expert opinion. In any case, the noise increases identified by appellants do
not amount to violations of the Noise Ordinance or the General Plan under Svinth’s
criterion one. As we have explained, noise from Dream Center recreational activities is
governed by the multi-factor approach of City Code section 17-16.040.
Even under Svinth’s criterion three, which does set a numeric significance
threshold of 5 dBA Ldn above existing ambient noise levels, and even assuming a 5 dBA
Leq increase above existing conditions would similarly cross the noise significance
threshold, appellants have not presented substantial evidence that noise from gardening
and throwing pottery will cross that threshold. We detect very little science behind
appellants’ arguments and cannot draw any conclusions about significance from the
numbers they provide, without expert interpretation. Appellants have identified no
23
substantial evidence in the administrative record that these activities would create noise
impacts above the criterion three threshold.
The City’s determination of no significant impact and its approval of a negative
declaration were supported by substantial evidence in the form of Svinth’s Noise Study.
We cannot say the City abused its discretion by failing to proceed in the manner required
by law under CEQA.
III. DISPOSITION
The judgment is affirmed. Respondents shall recover their costs on appeal.

24
 _________________________
Streeter, Acting P.J.

We concur:

_________________________
Reardon, J.

_________________________
Schulman, J.*

*
Judge of the Superior Court of California, City and County of San Francisco, assigned
by the Chief Justice pursuant to article VI, section 6 of the California Constitution.

25
Filed 5/24/18

CERTIFIED FOR PUBLICATION

IN THE COURT OF APPEAL OF THE STATE OF CALIFORNIA

FIRST APPELLATE DISTRICT

DIVISION FOUR

CHARLES T. JENSEN et al.,
Plaintiffs and Appellants,
A144782
v.
CITY OF SANTA ROSA, (Sonoma County
Super. Ct. No. SCV255347)
Defendant and Respondent;
SOCIAL ADVOCATES FOR YOUTH, ORDER CERTIFYING OPINION
Real Party in Interest and Respondent. FOR PUBLICATION

THE COURT:
The opinion in the above-entitled matter filed on May 1, 2018, was not certified
for publication in the Official Reports. For good cause, the requests for publication are
granted.
Pursuant to California Rules of Court, rules 8.1105 and 8.1120, the opinion in the
above-entitled matter is ordered certified for publication in the Official Reports. Listing
of counsel is attached hereto.

Dated: _________________ ________________________________
Streeter, Acting P.J.

1
Jensen v. City of Santa Rosa (A144782)

Trial court: Sonoma County Superior Court
Trial judge: Hon. Elliot Lee Daum
Counsel:
Botz Cody Law, Theodore J. Cody, and Sarah Botz for Appellant.

City Attorney of Santa Rosa and Molly Dillon, Assistant City Attorney for
Respondent City of Santa Rosa.

Law Office of Rose M. Zoia and Rose M. Zoia for Real Party in Interest and
Respondent Social Advocates for Youth.

2