HomeMy WebLinkAboutCORRESPONDENCE - 75A (COMMENT)75A
City Council Meeting Correspondence
10/15/2019
PUBLIC HEARING - APPEALING THE DECISION OF THE PLANNING COMMISSION IN APPROVING
CONDITIONAL USE PERMIT NO.2019-30 AND AMENDMENT TO VARIANCE NO.2018-10 TO ALLOW A
CAR WASH AT 301 NORTH TUSTIN AVENUE AND CONDITIONAL USE PERMIT NO.2019-31
Date of Name
Correspondence
Representative of In Favor In Opposition Comment
of RA*. of RA.*
1 10/14/2019
Andrew Sales
Yes
2 10/14/2019
Kara Grant
Yes
3 10/15/2019
Chase Russell
Russell Fischer
Yes
4 10/15/2019
Phil Bacerra
Yes
5 10/14/2019
Kara Grant
ADDITIONAL COMMENTS
Yes
S')bto-t-o •
5
1 10/14/2019
Cora Chu & Mike Deng
Santa Ana Business owner
Yes
2 10/14/2019
Yoon Hee Choe
Santa Ana Business owner
Yes
3 10/15/2019
Phung Truong
Yes
4 10/15/2019
Ebony Acosta
Yes
5 10/15/2019
Cedric Mendosa
Yes
6 10/15/2019
David Ezra Vinson
Yes
7 10/15/2019
Angel Girm
Yes
*RA - Recommended Action
Wednesday, October 16, 2019 Page 1 of 6
Date of
Name Representative of
In Favor In Opposition Comment
Correspondence
of RA*. of RA.*
28
10115/2019
Shanney Magana
Yes
29
10/15/2019
Ana Miranda
Yes
30
10/15/2019
Norma Vasquez
Yes
31
10/15/2019
Dulce Leiva
Yes
32
10/15/2019
Jose Montes De Oca
Yes
33
10/15/2019
Jonathan Navarro
Yes
34
10/15/2019
James Ruiz
Yes
35
10/1512019
Giselle Herrera
Yes
36
10/15/2019
Cindy Lopez
Yes
37
10/15/2019
Steven Flores
Yes
38
10/15/2019
Jaquelin Sanchez
Yes
39
10/15/2019
Sebastian Garcia
Yes
40
10/15/2019
Omar Navarro
Yes
41
10/15/2019
Evelyn Navarro 4
Yes
42
10/15/2019
Francesca Andrade
Yes
43
10/1512019
Nathalle Bran
Yes
44
10t15/2019
Devan Rodarte
Yes
45
10/15/2019
Max Chahla
Yes
46
10/15/2019
Rosa Tran
Yes
47
10/1512019
Yoon Hee Choe
Yes
*RA - Recommended Action
Wednesday, October 16,
2019
Page 3 of 6
Date of
Name
Correspondence
48
10/15/2019
Brenda Gutierrez
49
10/15/2019
Gabriel Fuerte
50
10/15/2019
Isaac Fuentes
51
10/15/2019
Leslie Gomez
52
10/15/2019
Angie Karoplan
53
10/15/2019
Vicky Pederson
54
10/15/2019
Khalil Chahle
55
10/15/2019
Rae Davis
56
10/15/2019
Luke Thourburgh
57
10/15/2019
Ramsey Bilbeisi
58
10/15/2019
Angela Pine
59
10/15/2019
Mark Apepe
60
10/15/2019
Jesus Peres -Soto
61
10/15/2019
Terry Quarterman
62
10/15/2019
Isabel Jimenez
63
10/15/2019
Samuel Martinez
64
10/15/2019
Aurora Penaloza
65
10/15/2019
Janet Perez
66
10/15/2019
Victoria Cananas
67
10/15/2019
Jesus Avila
*RA - Recommended Action
Wednesday, October 16, 2019
Representative of
In Favor In Opposition
of RA*. of RA.*
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Comment
Page 4 of 6
Date of
Name Representative of
In Favor In Opposition Comment
Correspondence
of RA*. of RA.*
68
10/15/2019
Elizabeth Wagensteen
Yes
69
10/15/2019
Sam Oagir
Yes
70
1011512019
Cora Chu
Yes
71
10/15/2019
Cecilia Espitla
Yes
72
10/15/2019
Marla Kamilez
Yes
73
10/15/2019
Irma Deniz
Yes
74
10/15/2019
Alicia Reyes
Yes
75
10/15/2019
Celiz Garcia
Yes
76
10/15/2019
Alebarda Alvarez
Yes
77
10/15/2019
Francisco Arreola
Yes
78
10/15/2019
Juan Ramos
Yes
79
10/15/2019
Raissa Schurawel
Yes
80
10115/2019
Alma Gonzalez
Yes
81
10/15/2019
June Lee
Yes
82
10/15/2019
Patricia Hoiles
Yes
83
10115/2019
Robert Hervath
Yes
84
10/15/2019
Silvia Canchola
Yes
85
10/15/2019
Daniel Rodriguez
Yes
86
10/15/2019
Marcia Uribe
Yes
87
10/15/2019
Douglas Miller
Yes
*RA - Recommended Action
Wednesday, October 16,
2019
Page 5 of 6
Date of
Name
Representative of In Favor In Opposition Comment
Correspondence
of RA*. of RA.*
88
10/15/2019
Annette Debs
Yes
89
10/15/2019
Joel Bruce
Yes
90
10/15/2019
James Craig
Yes
91
10/15/2019
Marquerite Berry
Yes
92
10/15/2019
ChristalOrozco
Yes
93
10/15/2019
Alice Echevarria
Yes
94
10115/2019
Diego Garcia
Yes
95
10/15/2019
Jose Antonio Soto
Yes
215
TOTAL: 100
*RA - Recommended Action
Wednesday, October 16, 2019 Page 6 of 6
10/15/19 City Council Meeting
Item 75A
COMMENT (5)
'7Gft
Lopez, Kenia
From: Andy Salas <
Sent: Friday, October 11, 2019 11:33 AM
To: eComment
Cc: Administration Gabrieleno Indians; Matthew Teutimez; gabrielenoindians@yahoo.com
Subject: URGENT: City Council Meeting, October 15th - Regarding 301 Tustin Ave
Attachments: 301 Tustin Ave -City of Santa Ana_ Appeal_10-2019.pdf
Dear City Council,
Please see the attached letter of concern from the Tribal Council of the Gabrieleno Band of Mission Indians -
Kizh Nation.
We respectfully request review of our letter of concern and would like to be contacted for further discussion.
Sincerely,
Andrew Salas, Chairman
website: www,gabrielenoindians.org
to
GA5KIE:LE,N(D SAND OF MISSION INDIANS - KIZH NATION Historicallt)
Lnown as The San Gabriel band of Mission Indians recognized fry the State of
California as the aboriginal tribe of the Los Angeles basin
City of Santa Ana
Clerk of the Council
ecomments@santa-ana.org
City Council Meeting - Re: Project located at 301 North Tustin Ave
As the Tribal Chairman of the Gabrieleno Band of Mission Indians-Kizh Nation, we have grave concerns regarding
the proposed amendment to the project site. In good faith, the City and our Tribal government engaged in a government -
to -government consultation as mandated by SB18. We provided historical maps, ethnographic and historical
documentation, and our oral history showing the sensitivity of the area. As a result, the City concurred for "the
implementation of the mitigation measures for Cultural Resources, Hazards, and Tribal Cultural Resources."
Now that the applicant has changed the scope of the project, it appears the City has deemed the project no longer
meets the criteria for mitigating measures. We completely disagree with that rational. Ground disturbance is ground
disturbance, regardless what CEQA criteria the project is categorized. Whenever there is ground disturbance, the
potential for cultural resources is always a concern. For the City to presume our Tribal Cultural Resources are no longer
at risk due to a categorical change is an insult to our Native rights.
We have always tried to impress upon lead agencies "we are here to work alongside of you, not against you." Our
goal is to avoid any adversarial relationship as we know our paths will cross in the future. We respectfully request the City
to reinstate the mitigating measure on the project site. Our only concern is during ground disturbance. Once the ground
disturbance phase is completed, we will sign off on the project so your project can move forward. Our sole intent is the
protection and preservation of our Tribal Cultural Resources.
Respectfully,
Andrew Salas, Chairman
Gabrieleno Band of Mission Indians - Kizh Nation (626) 926-4131
Andrew Salas, Chairman Nadine Sales, Vice -Chairman
Albert Pere , treasurer I
Martha Gonzalez Lemos, treasurer II
Dr. Christina Swindall Martinez, secretary
Richard Gradias, Chairman of the council of Elders
PO box393 Covina, CA 9172) www wa6rielenoindians@yakoo.com
"7S A
Lopez, Kenia
From: Kara Grant <
Sent: Monday, October 14, 2019 11:27 AM
To: eComment
Cc: Kelaher, Selena
Subject: CITY COUNCIL MEETING 10/15 - Comments Submitted re Appeal Application No.
2019-03
Attachments: Comments re Appeal Hearing - re CEQA - 101419 FINAL.pdf, CEQA- Notice of Intent to
File CEQA Petition - FINAL - 101319.pdf,, City - EIR re Transit Zoning Code.pdf
Please find the attached comments submitted for the appeal hearing before the City Council on October 15, 2019,
regarding Appeal Application No. 2019-03 (Russell Fischer Commercial Center Project).
Please confirm receipt of these comments (3 documents in total).
Thank you,
Kara Grant
KARAI.GRANT
Attorney at Law
This communication, including any attachments, may contain confidential and/or proprietary information (and, in some cases
information protected by either or both doctrines of attorney -client privilege and attorney work -product), and is intended only
for the individual(s) or entity or entities to whom the communication is addressed. Any review, dissemination, or copying of
this email by anyone other than the intended recipient(s) is strictly prohibited. If you are not an intended recipient, please
contact the sender by reply email, and delete and destroy all copies of the original message,
KARA GRANT LAW
17595 Harvard, Suite C-202 39 Irvine, California 92614
tel 1 949.579.9330 fax 1 949.769.6689 email I kara@grant-law.net
VIA E-MAIL
October 14, 2019
City of Santa Ana
Attn: Clerk of the Council
20 Civic Center Plaza — M30
Santa Ana, CA 92701
eomments@santa-ana.org
skelaherC(�sanfa-atut.org
RE: Comments for the Hearing Before the City Council on Appeal Application
No. 2019-03 — Russell Fischer Commercial Center Project — 325 & 301 North
Tustin Avenue.
Dear Mayor Miguel A. Pulido and Members of the Council:
The City of Santa Ana, along with the project owner/applicant, Russell Fischer, LP, as well as
representative of the owner/applicant, Richard Finkel of Bundy -Finkel Associates (collectively, the
"Applicant'), have attempted to evade environmental review under the California Environmental
Quality Act ("CEQA") by analyzing and approving a project in piecemeal fashion. In 2016, the
Applicant initially applied to obtain changes to the general plan and zoning (for multiple properties) so
the Applicant could demolish all existing uses on 301 and 325 N. Tustin Avenue and build a new gas
station, convenience store and retail building (the "Original Project'). The results of an Initial Study
required the City to adopt a Mitigated Negative Declaration to comply with CEQA, and granted the
approvals requested. The City was required to adopt an MND because absent mitigation measures the
Original Project would have a substantial impact on the environment, including due to hazardous
materials released during demolition of the existing structures and due to Native American cultural and
historical resources during grading and construction.
In 2019—at the last minute before development —the Applicant submitted a "revised plan"
which proposed to "replace" the proposed retail building on 301 N. Tustin with a massive automated car
wash (the "Revised Project'). The City proceeded to ignore the portions of the project that had already
been implemented —including the general plan and zoning changes —determined the Revised Project
was categorially exempt from CEQA (which was not available because of, among other things, the
general plan and zoning changes), and abandoned the previously adopted MND as well as the
Mitigation Monitoring and Reporting Program ("MMRP") adopted to implement the mitigation
measures. Such a scheme is prohibited by CEQA.
CEQA requires the City to conduct subsequent environmental review following the MND based
on the substantial changes to the Original Project by the addition of the car wash. CEQA does not
authorize the City to proceed with the project but abandon the MND and MMRP previously adopted
simply because they revised a portion of what was previously proposed and approved. Moreover, even
if CEQA allowed the City to evaluate the Revised Project anew, the City is required to include the entire
project in the review, including the portions already completed such as the general plan and zoning
amendments. When the entire project is included, the City is precluded from invoking the categorical
exemption selected. Further, the addition of the car wash will have substantial impacts on the
environment requiring the preparation of an Environmental Impact Report ("EIR"), subsequent EIR,
MND or subsequent MND. But even without the impacts from the car wash, the substantial
environmental impacts identified as part of the original MND still apply to the Revised Project, which
precludes the City from utilizing a categorical exemption for the Revised Project regardless of how it is
analyzed.
In the attached Notice of Intent to File a Petition for Writ of Mandate for Violations of the
California Environmental Quality Act, and the Draft Petition for Writ of Mandate attached as Exhibit A
thereto, the Petitioners seek a writ of mandate from the California Superior Court to set aside the Notice
of Exemption, Environmental Review No. 2019-69 (the "NOE") filed by the City, to set aside the City's
determination that the Project, including the Revised Project at 301 N. Tustin Avenue, Santa Ana, in the
County of Orange, is categorically exempt from CEQA environmental review as an in -fill development
project pursuant to 14 Cal. Code Regs. Sec. 15332, and to order Respondents to conduct environmental
review, including the preparation of an FIR, Subsequent EIR, MND, or Subsequent MND, as required
by CEQA. The Petition also seeks to set aside all other approvals the City has granted for the Revised
Project, including Conditional Use Permit No. 2019-30, Amendment to Variance No. 2018-10, and
Conditional Use Permit No. 2019-31, for failing to comply with CEQA.
In addition, this Petition requests that the Court compel Respondents to provide public notice of
all CEQA determinations, all public hearings or meetings discussing a CEQA determination with
adequate time for the public to meaningfully participate, and further to provide notice to businesses and
residents within a sufficient radius of the Revised Project so that interested parties may meaningfully
prepare and appear to protect their interests, and Respondents may receive important input from the
public, including those affected by the Revised Project.
On September 9, 2019, Respondents improperly approved the Revised Project and filed the NOE
the following day, September 10, 2019. Petitioners requested the City to withdraw the NOE in light of
the pending Appeal to the City Council, but the City refused this request. This forced the petitioners to
file the CEQA petition to preserve their rights in light of the 35-day statute of limitations prescribed
under CEQA section 21167(d). Petitioners opposition to the Project concerning the City's CEQA
violations are further discussed in the attached Petition.
The attached Notice and Petition are submitted to the City as written comments in addition to
this letter for the October 15, 2019 hearing on the Appeal of the Russell Fischer Commercial Center
Project (Appeal Application No. 2019-03). The comments are submitted on behalf of Petitioners, Santa
Ana Needs Equity (SANE), William Conklin, Karina Conklin, and Yoon Hee Choe. The FIR excerpt
from a different City project attached is also submitted in support of these written comments and in
support of Appeal Application No. 2019-03.
Sincerely,
Kara E. Grant
Attorney at Law
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KARA GRANT LAW
KARA E. GRANT, SBN 252825
17595 Harvard, Suite C-202
Irvine, CA 92614
t 949.579.9330
e kara@grant-law.net
Attorneys for Petitioners
SUPERIOR COURT OF THE STATE OF CALIFORNIA
COUNTY OF ORANGE
SANTA ANA NEEDS EQUITY, an
unincorporated association; WILLIAM
CONKLIN, an individual; KAREVA
RANGEL CONKLIN, an individual; YOON
HEE CHOE, an individual,
Petitioners,
V.
CITY OF SANTA ANA; THE CITY
COUNCIL OF THE CITY OF SANTA ANA;
PLANNING COMMISSION OF THE CITY
OF SANTA ANA; and DOES 1 through 20,
inclusive,
Respondents.
RICHARD KEITH FINKEL; BUNDY-
FINKEL ARCHITECTS; RUSSELL
FISCHER, LP; CHASE RUSSEL; and ROES
1 through 20, inclusive,
Real Parties in Interest
NO.
TICE OF INTENT TO FILE
RIFIED PETITION FOR WRIT OF
,NDATE FOR VIOLATION OF THE
LIFORNIA ENVIRONMENTAL
ALITY ACT ("CEQA") AND
MPLAINT FOR INJUNCTIVE
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TO THE CITY OF SANTA ANA; THE CITY COUNCIL OF THE CITY OF SANTA
PLANNING COMMISSION OF THE CITY OF SANTA ANA:
PLEASE TAKE NOTICE that under Section 21167.5 of the California Public
Resources Code, Petitioners Santa Ana Needs Equity, an unincorporated association, William
Conklin, an individual, Karina Rangel Conklin, an individual, and Yoon Hee Choe, an individual
(collectively, the "Petitioners"), intend to file a petition under the provisions of the California
Environmental Quality Act ("CEQA") against Respondents the City of Santa Ana, a California
Municipal Corporation, the City Council of the City of Santa Ana, and the Planning Commission
of the City of Santa Ana, challenging (1) the determination that the commercial development
ect at Tustin Avenue and Fourth Street in Santa Ana (including the recently approved
development of 325 N. Tustin Avenue and 301 N. Tustin Avenue) (the "Project") is categorically
exempt from environmental review under CEQA as an in -fill development project pursuant to
Section 15332 of CEQA (14 Cal. Code Regs. § 15332), (2) the adequacy of the notice of the
Planning Commission hearing concerning the Project, and (3) that Respondents may approve the
Project without further environmental review under CEQA and/or the preparing a subsequent
environmental review document, and without compliance with the Mitigated Negative Declaration
and Mitigation Monitoring and Reporting Program previously adopted for the Project, as more
fully described in the Petition for Writ of Mandate and Complaint for Injunctive Relief attached
hereto as Exhibit "A" and incorporated herein by reference.
DATED: October 1.3, 2019
Respectfully submitted,
KARA GRANT LAW
By:
Kara E. Grant NV
Attorneys for Pe i ioners
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NOTICE OF INTENT TO FILE CEQA PETITION
CAA
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KARA GRANT LAW
KARA E. GRANT, SBN 252825
17595 Harvard, Suite C-202
Irvine, CA 92614
t 949.579.9330
e kara@grant-law.net
Attorneys for Petitioners
SUPERIOR COURT OF THE STATE OF CALIFORNIA
COUNTY OF ORANGE
SANTA ANA NEEDS EQUITY, an
unincorporated association; WILLIAM
CONKLIN, an individual; KARINA
RANGEL CONKLIN, an individual; YOON
HEE CHOE, an individual,
Petitioners,
V.
CITY OF SANTA ANA; CITY COUNCIL
OF THE CITY OF SANTA ANA;
PLANNING COMMISSION OF THE CITY
OF SANTA ANA; and DOES 1 through 20,
inclusive,
Respondents.
RICHARD KEITH FINKEL; BUNDY-
FINKEL ARCHITECTS; RUSSELL
FISCHER, LP; CHASE RUSSEL; and ROES
1 through 20, inclusive,
Real Parties in Interest
NO.
PETITION FOR WRIT OF
FOR VIOLATION OF THE
VIA ENVIRONMENTAL
ACT ("CEQA") AND
NT FOR INJUNCTIVE
PETITION FOR WRIT OF MANDATE
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Petitioners Santa Ana Needs Equity (SANE), William Conklin, Karina Rangel Conklin and
Yoon Hee Choe (collectively, "Petitioners"), allege the following:
I.
The City of Santa Ana, along with the developer, have attempted to evade
environmental review under the California Environmental Quality Act ("CEQA") by analyzing
and approving a project in piecemeal fashion. In 2016, the developer initially applied to obtain
changes to the general plan and zoning (for multiple properties) so the developer could demolish
all existing uses on 301 and 325 N. Tustin Avenue and build a new gas station, convenience store
and retail building (the "Original Project"). The City was required to adopt a Mitigated Negative
to comply with CEQA and granted the approvals requested. The City was required to
adopt an MND because absent mitigation measures the Original Project would have a substantial
impact on the environment, including due to hazardous materials released during demolition of the
existing structures and due to Native American cultural and historical resources during grading
and construction. In 2019—at the last minute before development —the developer submitted a
"revised plan" which proposed to "replace" the proposed retail building on 301 N. Tustin with a
massive automated car wash (the "Revised Project"). The City proceeded to ignore the portions of
the project that had already been implemented --including the general plan and zoning changes —
determined the Revised Project was categorially exempt from CEQA (which was not available
because of, among other things, the general plan and zoning changes) and abandoned the
adopted MND as well as the Mitigation Monitoring and Reporting Program ("MMRP")
21 adopted to implement the mitigation measures. Such a scheme is prohibited by CEQA.
22 2. CEQA requires the City to conduct subsequent environmental review following the
23 MND based on the substantial changes to the project by the addition of the car wash. CEQA does
24 not authorize the City to abandon the MND previously adopted. Moreover, even if CEQA
25 allowed the City to evaluate the Revised Project anew, the City is required to include the entire
26 project in the review, including the portions already completed such as the general plan and zoning
27 amendments. When the entire project is included, the City is precluded from invoking the
28 categorical exemption selected. Further, the addition of the car wash would have substantial
2
PETITION FOR WRIT OF MANDATE
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4
impacts on the environment requiring the preparation of an Environmental Impact Report ("EIR" ),
subsequent EIR, MND or subsequent MND. But even without the impacts from the car wash, the
substantial environmental impacts identified as part of the original MND still apply to the Revised
which precludes the City from utilizing a categorical exemption for the Revised Project
5 11 regardless of how it is analyzed.
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Petitioners seek a writ of mandate from this Court to set aside the Notice of
Exemption, Environmental Review No. 2019-69 (the "NOE") filed by the City of Santa Ana, the
City Council of the City of Santa Ana, the Planning Commission of the City of Santa Ana, and
Does 1 through 20 (collectively referred to as, "Respondents" or the "City"), to set aside
Respondents' determination that the Revised Project, including the Revised Project at 301 N.
Tustin Avenue, Santa Ana, in the County of Orange, is categorically exempt from CEQA
environmental review as an in -fill development project pursuant to 14 Cal. Code Regs. Sec.
15332, and to order Respondents to conduct environmental review, including the preparation of an
Subsequent EIR, MND, or Subsequent MND, as required by CEQA.
15 4. This Petition also seeks to set aside all other approvals Respondents have granted
16 for the Revised Project, including Conditional Use Permit No. 2019-30, Amendment to Variance
17 No, 2018-10, and Conditional Use Permit No. 2019-31, for failing to comply with CEQA.
18 5. In addition, this Petition requests that the Court compel Respondents to provide
19 public notice of all CEQA determinations, all public hearings or meetings discussing a CEQA
20 determination with adequate time for the public to meaningfully participate, and further to provide
21 notice to businesses and residents within a sufficient radius of the Revised Project so that
22 interested parties may meaningfully prepare and appear to protect their interests, and Respondents
23 may receive important input from the public, including those affected by the Revised Project.
24 6. On September 9, 2019, Respondents improperly approved the Revised Project and
25 filed the NOE the following day, September 10, 2019. Accordingly, this Petition is filed within
26 the 35-day statute of limitations prescribed under CEQA section 21167(d).
27 ///
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3
PETITION FOR WRIT OF MANDATE
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II. PARTIES, JURISDICTION AND VENUE
Petitioner, Santa Ana Needs Equity (SANE), is an unincorporated association made
up of residents, business owners and businesses in the City of Santa Ana with a geographic nexus
Ito the proposed Revised Project. SANE is comprised of individual members, including the
individual petitioners who reside, own property, or work in the vicinity of the Revised Project and
are affected by the Project's environmental impacts as well as other impacts. SANE is organized
seek fairness and comprehensive economic and environmental equity in Santa Ana's urban
planning, including protecting the interest of the residents, businesses and property owners from
the environmental impacts of the Revised Project and the failure to assess and mitigate
environmental impacts.
8. Petitioners William Conklin and Karina Rangel Conklin are concerned citizens who
together own commercial property in Santa Ana, located at 2035 N. Tustin Avenue. Petitioners
are also co -owners of a business at that property, called Speedie Clean Express Car Wash
("Speedie Wash"). Speedie Wash is located only 1.1 miles from the proposed Project on the same
side of the same street. The Conklins and their business will be adversely affected by the Revised
Project, including its environmental impacts. Petitioners' interests are unique and will be directly
impacted by the Project. The Petitioners as well as the general public will suffer direct harm if
are permitted to approve the Project without first conducting environmental review
in violation of CEQA.
9. Petitioner Yoon Hee Choe, DDS, is a concerned citizen who owns the property
located at 171 N. Tustin Avenue, which is immediately adjacent to the proposed Revised Project.
Petitioner Choe is a licensed dentist and operates a dental and medical practice in the office
building on her property. Petitioner Choe has one tenant who operates a massage business.
Petitioner Choe's interests are unique because of the extremely close proximity of the car wash
tunnel to her building, where she operates a sensitive use, which cannot tolerate vibrations or
noise, and thus will be directly and severely impacted by the environmental impacts of the
Revised Project. According to the plans for the Revised Project, the 4,354-square foot car wash
tunnel that is part of the Revised Project will run the entire length of the property boundary shared
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with Petitioner Choe, and the distance between the exterior wall of the car wash tunnel on 301 N.
Tustin Avenue, and the exterior wall of Petitioner Choe's dental office building on 171 N. Tustin
Avenue is inches away, as shown in Real Party in Interest's elevations for the new massive car
wash below.
Petitioner Choe's
building and dental
office
M
10. Respondents are the lead public agency that erroneously issued the challenged NOE,
and subsequently took discretionary actions to approve the Revised Project.
11. Petitioners are ignorant of the true names and capacities of the respondents named
herein as DOES 1 through 20, and therefore, names those respondents by such fictitious names.
Petitioners will amend this Petition and Complaint to allege their true names and capacities when
ascertained. The City of Santa Ana, the City Council of the City of Santa Ana, the Planning
Commission of the City of Santa Ana, and Does 1 through 20 are collectively referred to herein as
"Respondents" or the "City".
12. Real Party in Interest, Richard Keith Finkel of Bundy -Finkel Associates is identified
as the "Applicant" on the challenged NOE.
13. Real Party in Interest, Bundy -Finkel Associates is also identified as the "Applicant"
on the challenged NOE.
14. Real Party in Interest, Russell Fischer, LP, is identified as the "Applicant" on
PUK WKrl VN N ANDAIL
zI
various other Project documents, including but not limited to, the Notice of Public Hearing Before
the Santa Ana Planning Commission, for the September 9, 2019 hearing on various entitlements
3 11 for the Project.
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15. Real Party in Interest, Chase Russell is also identified as the "Applicant" on certain
City documents in connection with the Project.
16. Petitioners are ignorant of the true names and capacities of the real parties in interest
named herein as ROES 1 through 20, and therefore, names those real parties in interest by such
fictitious names. Petitioners will amend this Petition and Complaint to allege their true names and
capacities when ascertained. Richard Keith Finkel, Bundy -Finkel Associates, Russell Fischer LP,
Chase Russell, and ROES 1 through 20 are collectively referred to herein as "Real Parties."
17. Venue is proper in this Court as this lawsuit arises out of findings that the Project
exempt from environmental review under CEQA, that decision occurred within the County of
13 Orange, by Respondents City of Santa Ana, and the Project at issue is located at 325 & 301 N.
14 Tustin Avenue, in the City of Santa Ana, County of Orange.
15 18. Respondents' actions and failures to act, which gave rise to this Petition, occurred in
16 Orange County, California. The Project is located within Orange County, California. The
17 environmental effects resulting from the Project will impact businesses and residents of the City of
18 Santa Ana, located in the County of Orange.
19 19. Petitioners provided Respondents written notice of the commencement of these
20 proceedings prior to filing this Petition for Writ of Mandate in compliance with section 21167.5 of
21 1 the Public Resources Code. A true and correct copy of the proof of service for that notification is
22 attached to this Petition as Exhibit A.
23 III. STANDING
24 20. Petitioners have standing to assert the claims alleged in this Petition because they
25 are beneficially interested in this matter, as required by Code of Civil Procedure section 1086.
26 Petitioners have a direct and beneficial interest in Respondents' compliance with laws bearing
27 upon approval of the Project. These interests will be directly and adversely affected by the
28 Project, which violates the law as set forth in this Petition and would cause substantial harm to the
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environment and the quality of life in the surrounding community and economic viability
of surrounding businesses. In addition, unless the relief requested herein is granted, the
environment will be adversely affected and injured by Respondents' failure to perform any
environmental review of the Project under CEQA, and by approving the Project.
21. Petitioners actively participated in the City's administrative approval process in an
attempt to ensure Respondents complied with CEQA and all other applicable laws prior to the
close of the September 9, 2019 public hearing on the Project, and before issuance of the NOE, and
thus fully exhausted administrative remedies. (Pub. Resources Code, § 21177, subd. (a).)
22. CEQA allows a petitioner who objected to a project to allege in a writ petition all
deficiencies asserted by others. (Citizens for Clean Energy v. City of Woodland (2014) 225
Cal.App.4th 173, 191.) Petitioners and other interested individuals and businesses made oral and
comments that were submitted to the City before and at the September 9, 2019 Planning
Commission hearing at which Respondents approved the Project.
IV. STATUTE OF LIMITATIONS
23. A challenge to a determination that a project is exempt must be filed within 35 days
after the notice of exemption was filed. (Pub. Res. Code § 21167(d); 14 Cal Code Regs §
15112(c)(5).)
24, Petitioners filed an appeal of Respondents NOE and Project approvals on September
19, 2019, which will be heard by the City Council on October 15, 2019. Although Petitioners'
Appeal is still pending, Respondents filed aNOE concerning the Project on September 10, 2019,
and thus triggered the 35-day statute of limitations to challenge a determination that the Project is
exempt. (Pub. Res. Code § 21167(d).). Accordingly, Petitioners filed the instant Petition to
their rights to challenge the NOE and related determinations.
25. Thus, Petitioners filed this Petition prior to the expiration of any applicable statute
26 of limitations.
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V. PRIVATE ATTORNEY GENERAL DOCTRINE
26. Petitioners bring this action as private attorney generals pursuant to Code of Civil
section 1021.5, and any other applicable legal theory, to enforce important rights
4 affecting the public interest.
5 27. Issuance of the relief requested in this Petition will confer a significant benefit on
6 the general public by requiring Respondents to carry out their duties under CEQA and other
7 applicable laws before approving the Project.
8 28. Issuance of the relief requested in this Petition will also result in the enforcement of
9 important rights affecting the public interest by compelling Respondent to engage in a legally
10 adequate analysis of the Project, and to ensure that the public has a meaningful opportunity to
11 review and comment on the impacts and mitigation measures for the Project.
12 29. The necessity and financial burden of enforcement make an award of attorneys' fees
13 appropriate in this case. Without this Petition, Respondents and Real Parties will proceed with
14 development of a Project that will cause significant, unmitigated environmental impacts that might
15 otherwise have been reduced or avoided through legally adequate environmental review, and the
16 adoption of feasible mitigation measures.
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18 V1. STATEMENT OF FACTS
19 A. Uses of 301 And 325 N. Tustin Avenue Before the Proposed Project
20 30. Real Parties in Interest and project applicant have had a development project
21 pending for the neighboring properties located at 325 N. Tustin Avenue and 301 N. Tustin Avenue
22 since 2016. These properties are located in between the intersection of N. Tustin Avenue and
23 Fourth Street and the 55 Freeway offramp into Santa Ana. Currently, a gas station with a small,
24 attached automated car wash, and a convenience store is located on 325 N. Tustin Avenue, as
25 shown below.
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31. Until approximately June 2019, a single building operated as a restaurant was
located on 301 N. Tustin Avenue. A photo of 301 N. Tustin Avenue with the restaurant and the
adjacent properties (the gas station to the left, and a dentist's office and massage business to the
right) is shown below.
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B. Russel Fisher Proposes the Original Project
32. In 2016, Real Party in Interest, Richard Finkel, representing Real Party in Interest
and Project Applicant, Russell Fischer LP — a car wash owner and developer that has "been in the
car wash industry for 30 years and operates six locations in Orange County" — originally submitted
applications to the City for the following:
a. "a general plan amendment to re -designate the property at 301 North Tustin
Avenue from Professional and Administrative Office (PAO), to General
Commercial (GC), and amendment application to rezone the properties at 301 and
325 North Tustin Avenue from Professional (P) to General Commercial."
b. To demolish the restaurant at 301 North Tustin and build a "multi -tenant
commercial building with a drive -through window service."
c. To demolish the existing uses at 325 North Tustin —a small gas station,
convenience store and small car wash — and build a larger gas station and large
convenience store (hereinafter, the "Original Project').
33. Meetings were held to explain the Original Project to the public, particularly nearby
businesses and residents. A Sunshine Ordinance Community Meeting for the Original Project was
held on December 13, 2016, because approval of that project required a General Plan Amendment
to re -designate 301 N. Tustin Avenue from Professional & Administrative Office to General
Commercial, and a Zoning Amendment to rezone 301 N. Tustin Avenue and 325 N. Tustin
Avenue from Professional to General Commercial (C2). The Sunshine Meeting notice provided
as follows:
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PRRTN EKSNIf
Russell Fischer Partnership
16061 Beach Boulevard
Huntington Beach, CA 92647
(714)842-4453
Cordially Invites yo� a Community Information meeting for:
301 & 325 N Tustin Ave.
A proposed new commercial center
Including a Gas Station with a 2,80L
..' s.f. Convenience Store and a 7,500
s.f. Multi -tenant Retail Building.
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Meeting Information
Date: Tuesday, 12/13/16
Location: El Ranchito Restaurant
.+ 2201 E First St,
Santa Ana
Tlmo- 5-1n ry m to R nn n m
34. Respondents posted the following mockup for the Original Project on its website:
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C. The City Conducts CEQA Environmental Review for the Original Project
35. In a letter to Respondents dated June 12, 2018, Mr. Andrew Salas, Chairman of the
Gabrieleho Band of Mission Indians — Kizh Nation (the "Mission Indians Letter"), requested a
consultation regarding the Original Project pursuant to Senate Bill 18 (SB 18), Government Code
Section 65352.3. The Mission Indians Letter states in pertinent part, that the Original Project "lies
within our ancestral tribal territory, meaning descending from, a higher degree of kinship than
traditional or cultural affiliation. Your project is located within a sensitive area and may cause a
substantial adverse change in the significance of our tribal cultural resources ... to avoid adverse
effects to our triable cultural resources, we would like to consult with you and your staff to
provide you with a more complete understanding of the prehistoric use(s) of the project area and
the potential risks for causing a substantial adverse change to the significance of our triable
cultural resources."
36. Respondents conducted environmental review of the Original Project, and finding
project could have a significant environmental impact on tribal cultural resources at 325 and
15 301 N. Tustin Avenue, Respondents adopted the MND and MMRP to safeguard those resources
16 during construction of the Revised Project. The Gabrielefio Mission Indians identified 301 & 325
17 N. Tustin Avenue as a sensitive location in light of their oral and written history, identified it as
18 such for Respondents, and informed' Respondents that "to avoid adverse effects to [their] tribal
19 cultural resources," through mandatory environmental review and a mitigation monitoring and
20 reporting program to avoid "the potential risks for causing a substantial adverse change to the
21 significance of [their] tribal cultural resources."
22 37. Respondents prepared an Initial Environmental Study in connection with the
23 Original Project. The Initial Study found "at least one impact that is either `Potentially Significant
24 Impact' or `Less Than Significant with Mitigation Incorporated" including Cultural Resources,
25 Hazards and Hazardous Materials, Tribal Cultural Resources and Mandatory Findings of
26 Significance. In August 2018, Respondents made a determination based on the Initial Study that
27 "the proposed project could have a significant effect on the environment, there will not be a
28 significant effect in this case because the mitigation measures described on an attached sheet have
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been added to the project. A MITIGATED NEGATIVE DECLARATION will be prepared."
(italics added.)
38. Respondents found that there were a number of items that would result in a
significant impact on the environment and it was only less than significant with mitigation
measures that would be imposed as part of the MND. Respondents found that absent the
mitigation measures the project would "cause a substantial adverse change in the significance of
an archeological resource," "directly or indirectly destroy a unique paleontological resource or site
or unique geological feature," and "disturb any human remains including those interred outside of
formal cemeteries." Respondents also found that absent required mitigation measures, the project
would "create a significant hazard to the public or the environment through the routine transport,
use, or disposal of hazardous materials," "create a significant hazard to the public or the
environment through reasonably foreseeable upset and accident conditions involving the release of
hazardous materials into the environment" and "emit hazardous emissions or handle hazardous or
acutely hazardous materials, substances, or waste within on -quarter mile of an existing proposed
school."
39. As part of the Original Project (as part of the Revised Project), 325 and 301 North
Tustin were to be graded and the MND and MMRP required Real Parties to hire an expert to
a CEQA analysis for any archaeological, paleontological or geologic discoveries and to
excavate them appropriately. Similarly, Real Parties were required to allow an archaeologist to
evaluate and perform any required analysis of any discovered burial sites or sacred lands. In
addition, prior to commence of construction, Real Parties were required to "retain a Native
American Monitor to conduct a Native American Indian Sensitivity Training for construction
personnel' and "retain a Native American Monitor to be on -site during all project related, ground
disturbing construction activities (e.g. pavement removal, auguring, boring, grading, excavation,
potholing, trenching, and grubbing)."
40. Prior to demolition, Real Parties were required to conduct an asbestos survey, to
remove all asbestos as required and prepare an abatement report. Real Parties were also required
to remove all lead -based paint as specified.
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41. Further, as part of the Initial Study, Respondents were required to evaluate whether
the project would result in exposure of persons to or generation of excessive groundborne
vibrations or noise levels, if the project would expose people or generate noise levels in excess of
standards established in the local general plan or noise ordinance, or applicable standards of other
agencies, and whether the project would create a substantial temporary or periodic increase in
ambient noise levels in the project vicinity above levels existing without the project. Respondents
conducted these evaluations as part of the Initial Study for the retail building, not the car wash.
Based on the retail building (and without considering a car wash), Respondents found these items
to have a less than significant impact.
D. Respondents Approve the Original Project Along with a Mitigated Negative
Declaration and Mitigation Monitoring And Reporting Program
42. In 2018, two years after the Original Project was proposed, Respondents prepared a
Mitigated Negative Declaration, Environmental Review No. 2016-156 for the Original Project (the
"MND"), as well as a Mitigation Monitoring and Reporting Program (the "MMRP"). The MND
concluded that the Original Project would have a less than significant environmental impact with
implementation of mitigation measures to address tribal and cultural resources, and hazards,
including asbestos and lead -based paint:
i. "The [Original] Project site will be graded prior to construction, and if
during grading, it is revealed that previously unidentified archaeological,
paleontological or geologic deposits exist, an expert appropriate to the
nature of the find must be afforded the opportunity to evaluate any
additional finds and to complete an analysis in accordance with CEQA
guidelines, as amended."
ii. "If future activities in project site adversely impact previously unidentified
cultural resources, including burial sites or sacred lands, an archaeologist
will be afforded the opportunity to evaluate any additional finds and to
complete an analysis in accordance with CEQA guidelines, as amended."
iii. "Due to the age of the existing building, there is a potential that asbestos
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containing materials (ACM) and, perhaps, lead- based paint (LBP) may be
present. Exposure to either ACM or LBP may expose construction workers
and people in the vicinity of the project site to potential health risks."
43. Respondents adopted the MND and MMRP on or about November 20, 2018, and
approved the Original Project. Respondents specifically approved: (a) a resolution approving
general plan amendment No. 2018-05 to re -designate 301 N. Tustin Avenue from Professional &
Administrative Office (PAO) to General Commercial (GC), per Real Parties' request; (b) an
ordinance approving General Plan amendment 2018-08 to rezone 301 and 325 North Tustin
Avenue from Professional to General Commercial (C2); (c) a conditional use permit to allow an
eating establishment with drive -through service at 301 N. Tustin Avenue; and (d) certain variances
that pertained to 325 N. Tustin Avenue only.
E. The Developer Demolished the Restaurant on 301 N. Tustin Avenue which
Disrupts Petitioner's Dental Business
44. Petitioners are informed and believe that in or about February 2019 and May 2019,
City approved permits to demolish the restaurant on 301 N. Tustin Avenue and Real Parties
the restaurant thereafter.
17 45. Months ago, and with no prior notice to Petitioner Choe, Real Parties began
18 demolition of the restaurant building on 301 N. Tustin Avenue. The building was located roughly
19 in the middle of the site. The demolition caused such severe, jarring vibrations inside Petitioner
20 Choe's building, and such loud noise inside her building, that patients were scared and decided not
21 to continue their treatment, Petitioner Choe could not perform the exams or use sensitive, delicate
22 dental treatments because of the jarring vibrations, and because it prevented Petitioner Choe from
23 being able to focus on the precise medical tasks she was performing. During demolition,
24 Petitioner Choe was forced to close her dental practice early, start late, or was unable to take any
25 patients at all because the severe vibrations and noise made it impossible to do so.
26 46. Petitioners' tenants who operate a massage business in Petitioner Choe's building
27 on 171 N. Tustin Avenue, were also prevented from operating their business on several occasions
28 during the restaurant demolition on 301 N. Tustin Avenue, due to the extreme noise and vibrations
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heard and felt from inside the building. After one day of demolition, Petitioner Choe found a
vertical crack in an interior wall in an exam room that spans from the ceiling to the floor. This
crack was not there prior to the demolition of the restaurant building.
47. Petitioners are informed and believe that the demolition was done without
compliance with the mitigation measures imposed pursuant to the NIND. Further, neither the City
nor Real Parties have provided any evidence of such compliance.
F. With Only 10 Days -Notice to a Handful of Properties, the City Proposes to
Approve the Developer's Revised Project with a Massive Car Wash Instead
of a Retail Building and Find The Revised Project Categorically Exempt
from CEQA
48. Nine months after the Original Project was approved, Respondents posted and
mailed to only a handful of properties a "Notice of Public Hearing before the Santa Ana Planning
Commission," dated August 30, 2019 (the "August 30th Notice"). Respondents' August 30'
Notice was the very first time Respondents informed the public that the project referred to by
Respondents as the "Russell Fischer Commercial Center" and approved for 325 and 301 N. Tustin
Avenue the year prior, no longer included the Retail/Restaurant development on 301 N. Tustin
Avenue, but instead, "[s]ince the zone change, the property owner has revised the project" to
"substitute" a massive, automated carwash on 301 North Tustin, including a 4,354 square foot car
tunnel and 20 vacuum bays, for the approved retail building. The service station and
convenience store plans for 325 N. Tustin Avenue were unchanged.
49. The August 30th Notice stated that the Planning Commission would hold a Public
Hearing on September 9, 2019, and take action on three items for the "revised" project, which was
described as follows: "The applicant proposes to demolish the existing service station, car wash,
and convenience store to construct a new service station with 3,040-square foot convenience store
and new automated car wash. The project includes a request for (1) Conditional Use Permit No.
2019-30 to allow a car wash, (2) amendment to Variance No. 2018-10 to allow a reduction in the
City's yard standards, and (3) Conditional Use Permit No. 2019-31 to allow a convenience store to
operate 24 hours a day."
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50. The August 30" Notice also stated that the Revised Project was categorically
exempt from CEQA environmental review as an in -fill development project:
"[T]he project is categorically exempt from further environmental review pursuant
to CEQA Guidelines Section 15332, Class 32, In -fill Development Projects. This
exemption applies to in -fill development provided it is consistent with the General
Plan and zoning designation. The combined development site is 1.46 acres and
surrounded by urban uses. The site was previously developed with commercial uses
and has no habitat for endangered, rare or threatened species. The project will not
result in any significant impacts related to traffic, noise, air quality or water quality
according to the traffic impact analysis and with implementation of water quality
requirements."
51. Thus, even though Respondents determined in late 2018 that the Original Project for
301 N. Tustin Avenue required environmental CEQA review and adopted the MND and MMRP,
in part because 301 N. Tustin Avenue was found to be located "within a sensitive area and may
cause a substantial adverse change in the significance of [the Gabrieleno Band of Mission Indians
— Kizh Nation's] tribal cultural resources," Respondents determined that the Revised project by
substituting a massive car wash in the place of the retail building on 301 N. Tustin Avenue would
have no significant effect on the environment and did not need to comply with the previously
adopted MND. Accordingly, Respondents both posted and filed the Notice of Exemption for the
Revised Project on September 10, 2019.
G. The City Concealed the Revised Project From Petitioners and the Public
52. Prior to Respondents publishing and distributing the August 301 Notice, certain
Petitioners inquired about the project development at 301 N. Tustin Avenue because it was well
that the property owner, Real Party in Interest Russell Fischer, LP, owned six (6) car
washes in Orange County, and Real Party in Interest Richard Finkel of Bundy -Finkel Associates,
is a car wash developer that sits on the board of the Irvine Advisory Group — Carwash Consultants
- "a consultancy headed by Paul Dadgar that has specialized in all facets of the carwash industry
for over 25 years." Accordingly, astute residents and business owners like Petitioners found it
curious that a car wash owner and a car wash developer would tear down the existing car wash on
325 N. Tustin Avenue, and develop on 301 N. Tustin Avenue a multi -tenant commercial retail
center with restaurant.
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53. Petitioner, Karina Conklin, visited the City Planning Department in person in early
July 2019, and specifically inquired as to whether the development at 301 N. Tustin Avenue had
changed from the Original Project approved by Respondents to a project involving a car wash.
Respondents informed Ms. Conklin that only the 2018 Original Project was before the City, and
referred her to the information page for the "Russell Fischer Commercial Center" on the City's
website. (See https;//www.sauta-ana.orR/pb/planning-divisionhnalor-Ianning_projects-and-
documents/russelI-Fischer-commercial-center). Petitioner Conlin, as a concerned Santa Ana
business owner, requested Respondents to inform her if the project changed. Despite Petitioner
Conklin's request, Respondents did not include her in the notification list for the August 30th
which was distributed only to those within 500 feet of the Revised Project.
54. Contrary to the City's representation to Petitioner Conklin, Respondents received
new development plans replacing the Retail/Restaurant portion of the project on 301 N. Tustin
Avenue with the massive Revised Project on April 26, 2019. Respondents also received payment
from Real Party in Interest and applicant Russell Fischer for review of the Revised Project on
April 26, 2019. Moreover, Respondents' Planning Department submitted a "Discretionary Action
New Submittal" memo to various City departments on May 1, 2019 regarding the newly proposed
Revised Project for 301 N. Tustin Avenue. Respondents also received a "Revised Focused Traffic
Impact Analysis Report" from Real Parties in Interest for the Revised Project on or about May 17,
2019. Respondents' project page for the "Russell Fischer Commercial Center" on the City's
website reflected the Original Project until August 29, 2019, when the Revised Project was finally
displayed — four months after Respondents received development plans and payment for the
22 Revised Project.
23 55. Respondents took active measures to conceal the evolution of the project at 301 N.
24 Tustin Avenue from the Original Project that, for over three (3) years, had been explained to the
25 public, discussed at numerous City meetings and hearings, shown to the public with site plans and
26 project mock ups, and displayed on the project page on the city's website as the Russell Fischer
27 Commercial Center up until ten (10) days before the September 9t' hearing. Moreover,
28 Respondents should have informed Petitioners that the project at 301 N. Tustin Avenue did in fact
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include a car wash when Petitioner expressly inquired in early July. These factors evidence that
the ten day notice distributed only to those within 500 feet of the Revised Project was not intended
to inform the public, but rather to conceal the drastic change in the project for 301 N. Tustin
Avenue. If Petitioners were provided adequate notice, they could have obtained experts, had
necessary studies conducted regarding the Revised Project, submitted Public Records Act requests
for project documents and materials, and had time to review and analyze the documents and plans
I for the newly proposed Revised Project, before the September 9` hearing. Respondents denied
Petitioners of this opportunity and the result was prejudicial to them.
H. Petitioners Submit Written Oppositions and Speak at the Hearing in
Opposition
56. Prior to the September 9, 2019 hearing on the Revised Project before Respondent's
Planning Commission, Petitioner Choe submitted written comments opposing the Revised Project
stating her concerns over the impact of noise and vibrations on her dental practice because of the
sensitive nature of her work and her medical equipment, as well as her tenant's massage business.
57. Petitioners William Conklin and Karina Conklin also timely submitted written
comments in opposition prior to the hearing addressing, among other things, Respondents'
violation of CEQA. Petitioners also objected that the August 301 Notice was insufficient to afford
interested persons like themselves an adequate opportunity to prepare and protect their interests.
Petitioners requested that the hearing being continued so that interested parties may have sufficient
time to obtain and review the project materials for the newly Revised Project, but Respondents'
Planning Commission denied that request.
58. Petitioner Choe appeared in person at the September 9, 2019 Planning Commission
hearing and voiced her concerns to the Board of Commissioners over the significant
environmental impacts the Revised Project will have on her property and business as an
immediately adjacent, and uniquely sensitive use.
59. Petitioners William and Karina Conklin spoke in opposition to the Revised Project
at the September 91' hearing through their representative.
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I. Respondents' Planning Commission Approves the Revised Project and
Finds it Exempt From CEQA
60. At the September 9, 2019 hearing, the City's Planning Commission approved the
Project by granting two conditional use permits, amending a variance issued for the
Original Project, and adopting Notice of Exemption, Environmental Review No. 2019-69, finding
the Revised Project categorically exempt from CEQA environmental review pursuant to Section
15332 for certain infill developments.
J. The City Posts and Files a Notice of Exemption for the Revised Project
61. On September 10, 2019, Respondents both filed and posted the NOE for the
Project, which stated the Project was categorically exempt from CEQA review pursuant
to Section 15332. The NOE states the following under "Reason(s) Why Project Is Exempt From
CEQA:" "The project is consistent with the General Plan and zoning designation. The site is 1.46
acres and surrounded by urban uses. The site was previously developed and has no habitat for
endangered, rare or threatened species. The project will not result in any significant impacts
related to traffic, noise, air quality or or [sic] water quality." Respondents did not make a single
to the potential for cultural resources or tribal cultural resources on 325 and 301 N.
17 Tustin Avenue, after August 30, 2019,.when the project proposed with the car wash publicly
18 became the Revised Project. Respondents also did not mention the hazardous substances that
19 could be released into the air from demolition, including asbestos and lead -paint.
20 K. Petitioners File an Appeal to the City Council but the City Refuses to
21 Withdraw the NOE Pending the Hearing
22 62. On September 19, 2019, Petitioners filed an appeal of the City's Planning
23 Commission's approvals of the Revised Project, including the categorical exemption
24 determination to the City Council.
25 63. California Public Resource Code section 21151 requires the City to provide an
26 appeal of the Planning Commission's categorical exemption determination to the City Council.
27 The City's CEQA guidelines provide for such an appeal as well.
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64. Petitioner requested that the City withdraw the NOE in light of the appeal to the
City Council, but the City refused.
65. The City's refusal to withdraw the NOE pending the hearing on the appeal
necessitated this writ petition in light of the 35-day statute of limitation to challenge an NOE
pursuant to Section 21167(d) of the Public Resources Code.
L. The City Engages in Prohibited Piecemealing and Fails to Conduct
Subsequent Environmental Review
66. "The foremost principle under CEQA is that the Legislature intended the act `to be
interpreted in such manner as to afford the fullest possible protection to the environment within
reasonable scope of the statutory language."' (Laurel Heights Improvement Assn. v. Regents of
University of California (1988) 47 Cal.3d 376, 390 [citing Friends of Mammoth v. Board of
Supervisors (1975) 8 Cal.3d 247, 259].)
67. To that end "`CEQA forbids `piecemeal' review of the significant environmental
impacts of a project." (Berkeley Keep Jets Over the Bay Com. v. Board of Port Comrs. (2001) 91
Cal.AppAth 1344, 1358.) "This standard is consistent with the principle that `environmental
considerations do riot become submerged by chopping a large project into many little ones —each
a minimal potential impact on the environment —which cumulatively may have disastrous
consequences."' (Laurel Heights, supra, 47 Cal.3d at p. 396.)
68. Respondents engaged in unlawful piecemealing of the Project in blatant violation of
CEQA by omitting portions of the project for which an MND and MMRP were previously
adopted, approving modifications to the Original Project without further environmental review,
and then carving out handpicked portions from the Revised Project. Respondents then defined
those handpicked selections as the "project" in order to avoid necessary further environmental
as well as compliance with the mitigation measures Respondents required for the Original
Project via the MND and MMRP. The Petitioners as well as the general public will suffer grave
harm if Respondents are permitted to continue morphing the Project, via piecemeal modifications,
and ultimately permit development of that Project without necessary mitigation measures, as they
have currently attempted and actually begun to do.
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69. For purposes of CEQA coverage, a "project' is defined as comprising "the whole of
an action" that has the potential to result in a direct or reasonably foreseeable indirect physical
I change to the environment. (14 Cal Code Regs § 15378(a).) Thus, the term "project' refers to the
I activity for which approval is sought, not to each separate governmental approval that may be
for the activity to occur. (14 Cal Code Regs §15378(c).) Accordingly, the lead agency
describe the project to encompass the entirety of the activity that is proposed for approval to
ensure that all potential impacts of the proposed project will be examined before it is approved.
(14 Cal Code Regs § I5378(a), (d).) An initial study that fails to describe the entire project is
fatally deficient: "[A] correct determination of the nature and scope of the project is a critical step
in complying with the mandates of CEQA." (Nelson v County of Kern (2010) 190 Cal.AppAth
252, 267 [county violated CEQA by not including new surface mining as part of project when
county was required to approve mining in addition to reclamation plan].)
70. In the August 9, 2018 Initial Study completed for the for the Project, Respondents
defined the originally proposed project, which was the evaluated for environmental impacts, to
include five (5) actions: (1) Development Project Approval for 325 N. Tustin Avenue and 301 N.
Tustin Avenue; (2) Conditional Use Permit for drive through services on 301 N. Tustin Avenue;
(3) Variance application for reduced landscape setback at 325 N. Tustin Avenue; (4) General Plan
Amendment to revise land use designations of two parcels from Professional Administration
Office to General Commercial; and (5) Amendment Application to change the zoning of four
parcels from Professional to General Commercial (C2). (Initial Study, p. 10.) Respondents
described the Original Project as follows:
"The proposed project will facilitate the redevelopment of a site with a 2,778-square
foot gas station convenience store, a 2,117-square foot gas pump canopy, and a
7,417-square foot multi -tenant retail building on two parcels totaling 1.46 acres in
the City of Santa Ana. The project also includes a General Plan Amendment to the
Land Use Plan Map, an Amendment Application (zone change) to the Zoning Map
on two properties of the Tustin Avenue Retail Development Project site (1.46 acres)
and three adjacent properties (2.78 acres), which together will be known as the Tustin
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Avenue Retail Project site and total approximately 4.24 acres." (Initial Study, p. 4.)
71. Respondents expressly describe the Original Project to include "the demolition of
the existing gas station, gas canopy, and carwash at 325 N. Tustin Avenue and demolition of the
existing restaurant building at 301 N. Tustin Avenue." (Initial Study, p. 10.)
72. Respondents September 24, 2018 staff report to the Planning Commission
concerning the Original Project recommended approval of the General Plan Amendment sought by
Parties in Interest because it would "create an approximately 4-acre General Commercial
area at the northeast and southeast corners of Tustin Avenue and Fourth Street," and the zone
change because it would "create a continuous block of commercial uses that will stimulate the
economy in the area." (Staff Report, September 24, 2018.)
73. The "Determination" reported by Respondents in the Initial Study was that the
Original Project would have a less than significant effect on the following environmental areas
mitigation measures incorporated: cultural resources, hazards and hazardous materials, and
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will have a significant effect on these environmental areas. The specific mitigation
measures adopted for the Original Project are discussed supra in this Petition.
74. Thereafter, Respondents prepared the MND for the Original Project,' as well as the
MMRP (SCH # 2018081033). Respondents (City Council) adopted Resolution No. 2018-081
adopting the MND and MMRP on November 20, 2018. The Resolution states that the MND
"concluded that the [Original] [P]roject would have a less than significant environmental impact
with implementation of mitigation measures. Mitigation measures are included to address cultural
resources, hazards, and tribal and cultural resources." The Resolution further states that the "City
Council has, as a result of its consideration and the evidence presented at the hearings on this
matter, determined that, as required pursuant to the California Environmental Quality Act (CEQA)
' To date, Petitioner have been unable to review the MND because Respondents have failed to produce the
MND in response to a Public Records Act Request submitted by Petitioners on September 12, 2019, as well
as several other informal requests. The MND is not available on the City's website, nor is it available on
the State Clearinghouse Website.
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and the State CEQA Guidelines, the MND adequately addresses the expected environmental
impacts of this [Original] [P]roject."
75. On or about May 20, 2019, Real Parties in Interest applied for, and Respondents
issued, a demolition permit for the demolition of the restaurant building on 301 N. Tustin Avenue.
The demolition occurred in approximately June 2019 and has since been completed.
76. On September 10, 2019, Respondents filed and posted the NOE (Notice of
Environmental Review No. 2019-69), which states the "project" is categorially
exempt from CEQA review pursuant to Section t5332 of the CEQA Guidelines, as in -fill
development project. In the NOE, Respondents now define the "proposed project" as:
"Demolition of the existing service station, car wash and convenience store to construct a new
service station with 3,040-square foot convenience store and new automated car wash."
77. The "project" as defined in the NOE deviates significantly from the Original
Project, for which the Initial Study, MND and MMRP were adopted. The revised "project" adds
the following: (1) Application for Conditional Use Permit No. 2019-30 to allow a car wash on 301
Tustin Avenue; (2) Application for Amendment to Variance No. 2018-10 to allow a reduction
16 II in the City's yard standards for 301 N. Tustin Avenue because Variance No. 2018-10 only applied
17 to 325 N. Tustin Avenue — the retail/restaurant development on 301 N. Tustin Avenue did not
18 require a variance; and (3) Application for Conditional Use Permit No. 2019-31 to allow a
19 convenience store to operate 24 hours a day. The project location is identified in the NOE as 301
20 N. Tustin Avenue and 325 N. Tustin Avenue, which are now referenced as within "the General
21 Commercial (C2) zone."
22 78. Respondents improperly omit the following major components of the Original
23 Project from the revised project description: (1) General plan amendment No. 2018-05 to change
24 the designation of the 301 N. Tustin Avenue, 431 N. Tustin Avenue, and 2321 East Fourth Street
25 to General Commercial; (2) Zoning Amendment Application No. 2018-08 to change the zoning of
26 the properties at 301 N. Tustin Avenue, 325 N. Tustin Avenue, 401 N. Tustin Avenue, and 2320
27 East Fourth Street to C2; (3) the retail and restaurant development on 301 N. Tustin Avenue; (4)
28 Variance No. 2018-10 to allow a reduction in the City's yard standards; and (5) demolition of the
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restaurant building on 301 N. Tustin Avenue.
79. Respondents' revised project definition set forth in the NOE is a blatant attempt to
circumvent CEQA by piecemealing the project, and by avoiding subsequent environmental review
by CEQA when a project undergoes significant modifications after initial NIND approval.
unlawful and prejudicial efforts are evident from the record. For instance, Respondents
erroneously assume that the project is located on properties zoned C2, and with a General Plan
designation of General Commercial, when these applications and approvals were major
components of the Original Project. In fact, development of the proposed car wash on 301 N.
Tustin Avenue could not occur without those approvals.
80. Per the NOE, Respondents improperly abandoned the MND and the MMRP adopted
for the Original Project only months before, and claim as of September 10, 2019, that the revised
project is categorially exempt from CEQA review as an in -fill development project. Accordingly,
Respondents are permitting Real Parties to proceed with development of the revised project
without complying with any of the mitigation measures identified in the MND and MMRP for
cultural and tribal and cultural resources, as well as hazards.
81. Because the Revised Project for purposes of CEQA must include all of the
component parts, including the general plan amendment and zone change already completed, the
Revised Project cannot qualify for the infill categorical exemption. As discussed above, the in -till
development exemption is subject to five limitations including that the project must be consistent
with the applicable general plan designation and all applicable general plan policies, as well as
with any applicable zoning designation and regulation (14 Cal Code Regs §15332(a)). As a matter
of law, a project that includes a general plan amendment or a zone change —as was the case
here —is not eligible for the exemption.
82. Respondents actions constitute piecemeal project approval prohibited under CEQA,
and negate Respondents' determination that the project is categorically exempt as an in -fill
development project because Respondents cannot carve out the General Plan Amendment and
Zoning Amendment from the project in order to rely on the result of those approvals to satisfy the
requirements for the in -fill exemption. The General Plan Amendment and Zoning Amendment are
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a significant part of the Revised Project, which includes the proposed modifications to develop a
car wash on 301 N. Tustin Avenue instead of the retail center, because the car wash could not have
been developed on the property without those changes. Commercial development of those
properties is the exact reason Real Parties applied for the General Plan Amendment and the
Zoning Amendment because the neither the Original Project, nor the Revised could be developed
those initial approvals.
7 83. The revised project is also inconsistent with the City's General Plan Goals and
8 Policies because the car wash development will not promote economic growth, sales tax revenue,
9 or jobs, and it is aesthetically unappealing at an identified gateway to the City.
10 84. In addition, Respondents were required to determine whether subsequent
11 environmental review of the Original Project was required in light of the modifications Real
12 Parties requested in 2019 as part of the Revised Project—i.e. the substitution of the car wash for
13 the retail building. If Respondents determined that no subsequent environmental review was
14 mandated by the modifications, then the MND and MMRP remained in effect and compliance
15 with the mitigation measures set forth therein was required. If Respondents determined that
16 further environmental review was necessary in light of the Modifications, then CEQA required
17 Respondents to adopt a subsequent environmental review document.
18 85. Further environmental review was required here because the addition of a massive,
19 automated car wash in the Revised Project creates environmental concerns that are distinct from
20 those associated with a retail building and were not considered in Respondents' Initial Study in
21 connection with the Original Project, or the MND. For example, the retail building in the Original
22 Project would produce no significant impacts on noise, vibration or traffic. In contrast, the
23 addition of the car wash development on 301 N. Tustin Avenue constitutes a substantial change in
24 light of, among other things, the vibrations, noise and traffic impacts the car wash will generate,
25 and that the car wash tunnel will be constructed merely inches from a highly sensitive use as a
26 dental office on 171 N. Tustin Avenue.
27 86. Subsequent environmental review was necessary to analyze whether the Revised
28 Project will have a significant impact on vibrations.
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87. Vibration is sound radiated through the ground. Groundborne noise is rumbling
sound caused by the vibration of room surfaces. According to the EPA's technical guideline on
vibrations, the dental office constitutes a "critical area" that requires lower vibration levels to be
acceptable. The preferred values for Petitioner Choe's office are: 0.0050 (z-axis), 0.0036 (x- and
y-axes), with maximum values of 0.010 (z-axis), 0.0072 (x- and y-axes). Petitioner Choe stated in
her written comments opposing the Car Wash Project, that her medical/dental machinery and
equipment and highly sensitive hand pieces such as the drill for nerve treatment, will cease to
function even at very low vibration levels.
88. The vibrations generated by the car wash are "serious environmental impacts" that
Respondents should have evaluated in a subsequent environmental review document when they
revised the Original Project to include a car wash. This is particularly true because of the unique
location of the 4,354 square -foot car wash tunnel on 301 N. Tustin Avenue, only inches from the
dental office building on 171 N. Tustin Avenue, and the opening of the tunnel towards the
sidewalk and professional business uses across the street. (See supra, site plan image, p. 5.) A
vibration impact assessment needed to be performed and considered before the Revised Project
was approved. Similarly, the extremely close proximity of the car wash tunnel to the Petitioner
Choe's building is unusual and thus mandates further assessment and evaluation so that mitigation
measures may be incorporated into the project, including for construction, if possible, and as
conditions to any project approvals. The vibration and noise disturbance Petitioner Choe suffered
during the restaurant demolition at 301 N. Tustin Avenue, which was significantly further away
from her building than the mere inches to the tunnel of the new car wash, evidences the unusual
circumstances of the Revised Project and need for these evaluations prior to any approvals for the
Project.
89. The Revised Project will have a significant impact on noise by the addition of a
massive, automated car wash. According to the Environmental Protection Agency ("EPA"), Noise
levels are generally considered low when they are below 45 dBA, moderate in the 45 to 60 dBA
range, and high above 60 dBA. The car wash will operate from 7:00 am to 7:00 or 8:00 pm, seven
days per week, and will service up to 30,000 cars per month. Prior to its demolition in 2019, 301
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N. Tustin Avenue was developed with a restaurant located in the center of the property and had
been used as such since 1965. The generation of noise from the industrial equipment used within
the car wash tunnel, the twenty (20) vacuum bays, the extremely close proximity of the tunnel to a
highly sensitive use, and the location of the car wash primarily surrounded by office/professional
uses, is unique. The car wash will have a significant effect on the surrounding environment
especially, Petitioner Choe's property and medical and dental practice, as well as her tenant's
massage business, pedestrian traffic directly in front of the tunnel, and professional/business office
directly across the street.
90. Immediately prior to filing this Petition, Petitioners became informed and on that
believe that Respondents disclosed for the first time that a noise study had been performed
for the car wash portion of the Revised Project. The LSA Noise Impact Analysis dated July 2019
I (the "LSA Noise Study") cites two (2) of Respondents' conditions of approval for the Revised
Project:
Conditions of Approval
The City requires that the following conditions of approval be met:
21, Submit a technical noise study prepared by a firm specializing in noise studies to the City for
review by the Planning Division, Police Department, and Code Enforcement Division that
demonstrates that the existing exterior noise levels and that the proposed design and
equipment of the car wash will conform to City noise ordinances, and the General Plan, and
will minimize noise impacts on adjacent properties.
22, A condition of approval for the project will include a requirement for the applicant to submit
a noise study based on updated field measurements within one month of commencement
of operations (issuance of a certificate of occupancy), and again on the one-year anniversary
of the commencement of operations, to ensure compliance with the City's noise ordinances.
(LSA Noise Study, p. 8.)
91. The LSA Noise Study goes on to state: "This analysis has been prepared to satisfy
Condition of Approval 21." (LSA Noise Study, p. 10.) The LSA Noise Study determines that
there are no surrounding sensitive uses because they are all commercial and office uses. (Id. at p.
11.) The City's general plan noise element provides that the desirable maximum noise level for
commercial land use is 65 decibels and the maximum acceptable noise level is 70 decibels. "The
City of Santa Ana does not currently have specific requirements for commercial and medical
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office uses within its Municipal Code." (LSA Noise Study, p. 19.)
92. The LSA Noise Study found that the "noise levels measured at the end of the car
wash tunnel' alone would be 81.9 dBA 13 feet away in the direction of the businesses across the
street and 73.7 dBA 20 feet from the end of the tunnel "90 degrees off-center"—i.e. on the other
side of Petitioner Choe's dental office. No noise analysis was performed from the interior of
Choe's building, or to assess the noise impact on the interior of her building from noise
emanating through the wall of the tunnel, which is only inches away. The LSA Noise Study also
failed to consider the vibrations that would be generated, and how they would be felt inside her
building.
93. Petitioners are informed and believe that Respondents have never before cited to or
disclosed the LSA Noise Study because since its creation in July 2019, Respondents removed
Condition 21 to the CUP approval. The Condition of Approval for the car wash as set forth in the
attachments to the staff report for the September 9, 2019 Planning Commission hearing on the
Revised Project only require compliance with "City noise ordinance standards," and no longer
the General Plan (the Noise Element) as it did when LSA prepared the Noise Study in July
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"Prior to Building & Safety Division plan check submittal, the Applicant shall
submit a technical noise study prepared by a professional firm specializing in
preparation of noise studies to the City for review by the Planning Division, Police
Department, and Code Enforcement Division that demonstrates that the proposed
design and equipment of the car wash will conform to City noise ordinances and
will minimize noise impacts on adjacent properties. The Applicant shall, to the best
of his or her abilities and at his or her sole cost, utilize the same noise specialists
employed at the Applicant's other location(s) to prepare the noise readings and
studies. Prior to issuance of a permanent certificate of occupancy, the Applicant
shall hold a "soft opening" to test all noise -generating equipment onsite and make
adjustments as necessary to bring the equipment into compliance with City noise
ordinance standards, to the satisfaction of the Planning and Building Agency and
Police Department. The Applicant shall submit an updated and revised noise study
based on updated field measurements within one (1) month of commencement of
operations, and again on the one-year anniversary of the commencement of
operations, to ensure compliance with the City's noise ordinances."
(CUP 2019-30, Condition to Approval, No. 11)
94. Accordingly, with respect to noise, Respondents' have conditioned approval of the
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CUP for the car wash on compliance with nothing because, as LSA pointed out, the Noise
Ordinance does not have "specific requirements for commercial and medical office uses." (LSA
3 11Noise Study, p. 19.)
4 95. There will be a significant impact on noise for the surrounding environment,
5 including but not limited to, business uses and pedestrian traffic, as there is no specific
6 requirement that noise remain below any certain level or comply with any specific standard.
7 96. Petitioners' expert conducted a peer review of Real Parties' traffic analysis and
8 found it deficient in that it used outdated and incomplete data that, when corrected, would show
9 the Revised Project will have a significant impact on traffic, including increasing the collision rate
10 at the intersection of N. Tustin Avenue and Fourth Street beyond what it currently is, which is
11 significantly higher than would be expected for this type of intersection. Specifically, "[t]he ten
12 year average collision rate at this intersection is 0.37 collisions per million entering vehicles ...
13 [and] the most recent collision rate during the past three years (2016-2018) the collision rate has
14 increased to 0.43 collisions per million entering vehicles." (Id.) Significantly, RKE found that
15 "any increase in traffic generated by the proposed [Car Wash] [P]roject could potentially increase
16 the collision rate at this intersection." (RK- Engineering, Peer Review of the Revised Project
17 revised Traffic Study, dated May 17, 2019, prepared by Linscott, Law & Greenspan, Appendix B,
18 SWITRS data for Intersection of N. Tustin Ave. and 4r' Street.)
19 M. The Revised Project does not Qualify for the Infill Exemption
20 97. Respondents violated CEQA by erroneously finding the Revised Project
21 categorically exempt as an in -fill development project pursuant to Section 15332 of the CEQA
22 Guidelines.
23 98. CEQA section 15332 specifies the five requirements for a project to qualify for the
24 in -fill development exemption, which are:
25 (a) The project is consistent with the applicable general plan designation
26 and all applicable general plan policies as well as with applicable zoning
27 designation and regulations;
28 (b) The proposed development occurs within city limits on a project site of
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no more than five acres substantially surrounded by urban uses;
(c) The project site has no value as habitat for endangered, rare or
threatened species;
(d) Approval of the project would not result in any significant effects
relating to traffic, noise, air quality, or water quality; and
(e) The site can be adequately served by all required utilities and public
services. (State CEQA Guidelines Section 15332.)"
99. The Revised Project does not qualify for the in -fill categorical exemption because
the project, within the meaning of CEQA, includes the general plan amendment and zone change,
were part of the Original Project and are necessary for the development of the Revised
12 100. The Revised Project also does not qualify for a categorical exemption because
13 Respondents have already determined that the Original Project —including the portions that
14 remain in the Revised Project —require an MND and mitigation measures to avoid significant
15 impacts on the environment. In addition, CEQA does not permit a project to be modified
16 following the adoption of an MND and then for a categorical exemption to be approved so that the
17 MND can be disregarded.
18 101. The Revised Project also does not qualify for the categorical exemption because the
19 Revised Project would result in significant effects relating to traffic, noise, vibrations, and air
20 quality.
21 102. In addition, the Revised Project cannot be approved as categorically exempt because
22 it falls into three exceptions.
23 103. CEQA section 15300.2 contains a list of exceptions to the exemptions. Relevant
24 here:
25 a. "all exemptions ... are inapplicable when the cumulative impact of successive
26 projects of the same type in the same place, over time is significant." (subd. (a).)
27 b. "a categorical exemption shall not be used for an activity where there is a
28 reasonable possibility that the activity will have a significant effect on the
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environment due to unusual circumstances." (subd. (b).)
c. "a categorical exemption shall not be used for a project which may cause a
substantial adverse change in the significance of a historical resource."
104. A categorical exemption is also not available because there are unusual
circumstances that will have a significant effect on the environment in connection with the
Revised Project, including but not limited to (a) the proximity of the car wash component of the
Project to the building on the adjoining property and the noise and vibrations that will
8 impact the sensitive uses on that property, (b) that Respondents previously adopted an MND and
9 MMRP requiring mitigation measures to address significant environmental impacts for the project
10 and have abandoned the MND and MMRP as part of the approval of the Revised Project, (e) the
11 existence of cultural resources and tribal cultural resources on the property, and (d) the additional
12 traffic generated by the Revised Project which will increase the collision rate at the intersection of
13 411 Street and N. Tustin Avenue, which is already significantly exceeds the expected rate for this
14 type of intersection.
15 105. In the alternative, a categorical exemption is also not available because of the
16 cumulative impacts of the implemented portions of the Original Project, including the amendment
17 of the general plan, and zone change and demolition of the restaurant building coupled with the
18 additional elements of the Revised Project will have a significant impact on the environment as
19 evidenced by the previously adopted MND and MMRP.
20 106. Respondents were required to, and failed to, evaluate the environmental impacts of
21 the unmodified portions of the Original Project, as well as the environmental impacts of the work
22 already completed such as the demolition of the restaurant at 301 North Tustin Avenue, along with
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environmental impacts of the changes made in the Revised Project. The existence of the MND
and MMRP, which required mitigation measures for demolition and during construction of the
entire original project, including the parts that have not been changed in the Revised Project,
demonstrates that Respondents failed to consider and properly address these cumulative impacts in
approving the Revised Project as categorically exempt.
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FIRST CAUSE OF ACTION
[Violation of CEQA Against All Respondents]
107. Petitioners reallege and incorporate each of the prior allegations as set forth in full.
108. A court shall issue a writ of mandate ordering a public agency to perform a
mandatory duty under CEQA if the court finds the agency committed a prejudicial abuse of
discretion. (Pub. Res. Code § 21168.5; Code Civ. Proc. § 1085(a).) In the context of CEQA, an
abuse of discretion "means the agency failed to proceed as required by law or there was no
substantial evidence to support its decision." (Pub. Res. Code § 21168.5.)
109. Respondents have abused their discretion and failed to act in a manner required by
CEQA because they:
a. Failed to adequately address, analyze, or otherwise consider the adverse
environmental impacts, necessary or foreseeable mitigation measures, or a
reasonable range of alternatives to the Revised Project, in an environmental
document as required by CEQA.
b. Failed to provide adequate notice to Petitioners and the public to allow them to
meaningfully prepare and participate in the hearing on the Revised Project as
required by the right to due process under the US Constitution and the California
Constitution;
c. Engaged in prohibited piecemeal environmental review by ignoring the Original
Project and abandoning the adopted MND and MMRP;
d. Failed to conduct subsequent environmental review after substantial changes were
made to the Original Project;
e. Found the Revised Project categorically exempt as an in -fill development without
meeting the statutory requirements, including consistency with the General Plan
and zoning, and no significant impacts relating to traffic, noise, air quality and
water quality.
f. Found the Revised Project categorically exempt even though (a) the Revised
Project will have a significant effect on the environment due to unusual
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circumstances, (b) the cumulative impact of successive projects over time is
significant, and (c) the Revised Project will cause a substantial adverse change in
the significance of historical resources, so that the exception provided by Guideline
section 15300.2 applied to the Revised Project;
g. Failed to provide an appeal to the City Council of the Planning Commission's
determination on the Revised Project as required by CEQA and the City of Santa
Ana's local CEQA guidelines.
110. In addition, Respondents determinations in approving the Revised Project and the
categorical exemption were not supported by substantial evidence.
111. Further, the lack of sufficient notice to Petitioners and the public deprived
Petitioners and the public of the ability to meaningfully prepare for and participate in the public
hearing regarding the Revised Project. Petitioners were denied sufficient time to hire experts,
conduct necessary tests and studies related to the Revised Project, including a traffic study, noise
study and vibration study, and to prepare and submit the public comments and materials submitted
for the City Council meeting on October 15, 2019.
112. Accordingly, the Court should determine the Revised Project is not categorically
exempt from CEQA as an infill development project, and in turn require necessary environmental
PRAYER FOR RELIEF
WHEREFORE, Petitioners pray forjudgment against all Respondents as follows:
For a peremptory writ of mandate directing Respondents to:
a. Rescind, vacate, invalidate, set aside, void or otherwise annul the approval of the
categorical exemption, the notice of exemption, the conditional use permits,
variance amendment, and all other approvals granted for the Revised Project;
b. Reinstate the MND and MMRP previously adopted and perform subsequent CEQA
review for the substantial revisions to the project contained in the Revised Project,
including the preparation of a subsequent EIR or subsequent MND if required;
c. To include in the Revised Project the portions of the Original Project that have
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already been implemented, including the general plan amendment, zone change,
demolition of the structures on 301 N. Tustin Avenue, and variance;
d. To otherwise comply with CEQA in any and all actions in connection with
approvals for the Revised Project.
e. To stay all actions under the conditional use permit and other City approvals
regarding the Revised Project pending final resolution of this action;
2. To provide public notice of all CEQA determinations, all public hearings or
meetings discussing a CEQA determination in connection with the Revised Project with adequate
time for the public to meaningfully participate and to provide notice to businesses and residents
within a sufficient radius of the Revised Project so that interested parties may meaningfully
prepare and appear to protect their interests, and Respondents may receive important input from
the public, including those affected by the Revised Project.
13 3. To provide public notice of all CEQA determinations, all public hearings or
14 meetings discussing a CEQA determination in connection with the Revised. Project to California
15 Native American tribes who have requested notice, including but not limited to, the Gabrieleno
16 Band of Mission Indians — Kizh Nation, with adequate time to meaningfully participate, prepare
17 and appear to protect their interests in their tribal cultural resources.
18 4. For preliminary and permanent injunctive relief prohibiting Respondents from
19 taking any further action in connection with the Revised Project pending resolution of this action
20 and until Respondents have fully complied with CEQA;
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5. For an award of costs and attorneys' fees, including but not limited to fees
authorized under Code of Civil Procedure section 1021.5; and
6. For such other equitable relief that the Court finds just and proper.
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(DATED: October 13, 2019
Respectfully submitted,
KARA GRANT LAW
By:
Kara E. Gra
Attorneys for inners
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PETITION FOR WRIT OF MANDATE
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VERIFICATION
STATE OF CALIFORNIA, COUNTY OF ORANGE
I have read the following VERIFIED PETITION FOR WRIT OF MANDATE FOR
VIOLATION OF THE CALIFORNIA ENVIRONMENTAL QUALITY ACT ("CEQA") AND
COMPLAINT FOR INJUNCTIVE RELIEF and know its contents.
I am a party to this action. The matters stated in the foregoing document are true of my
own personal knowledge, except as to matters that are stated on information or belief, and as to
those matters, I believe them to be true.
I declare under penalty of perjury under the laws of the State of California that the
foregoing is true and correct, and this Verification was executed on October 13, 2019.
William Conklin
PETITION FOR WRIT OF
AanlffWA
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PROOF OF SERVICE
STATE OF CALIFORNIA, COUNTY OF ORANGE
I am employed in the County of Orange, State of California. I am over the age of 18 and
not a party to the within action. My business address is 17595 Harvard, Suite C-202, Irvine,
California 92614.
On October 13, 2019, I served the foregoing document described as:
NOTICE OF INTENT TO FILE VERIFIED PETITION FOR WRIT OF MANDATE FOR
VIOLATION OF THE CALIFORNIA ENVIRONMENTAL QUALITY ACT ("CEQA") AND
COMPLAINT FOR INJUNCTIVE RELIEF
on the interested parties in this action by placing [XX] the original [ ]a true copy thereof enclosed
in sealed envelopes addressed as follows:
City of Santa Ana
Cleric of the Council, M-30
20 Civic Center Plaza
Santa Ana. CA 92701
[XX] BY MAIL
I caused such envelope to be deposited in the mail at Irvine, California. The
envelope was mailed with postage thereon fully prepaid. I am "readily
familiar" with this firm's practice of collection and processing correspondence
for mailing. It is deposited with U.S. postal service on that same day in the
ordinary course of business. I am aware that on motion of party served,
service is presumed invalid if postal cancellation date or postage meter date is
more than 1 day after date deposit for mailing in affidavit.
[ ] BY PERSONAL
I caused to be delivered by hand to the above -listed addressees or to the
SERVICE
addressees on the list attached hereto. A proof of service executed by the
delivery person will be mailed under separate cover.
[ ] BY OVERNIGHT
To expedite the delivery of the above -named document, said document was
MAIL/COURIER
sent via overnight courier for next day delivery to the above -listed party.
[ ] BY FACSIMILE
In addition to the manner of proof of service indicated above, a copy was sent
("FAX")
by FAX to the above -listed party.
I declare under penalty of perjury under the laws of the State of California that the
foregoing is true and correct.
Executed on October 13, 2019, at Irvine, California.
KARA E. G
PROOF OF
4.8 Noise
4.8 NOISE
This FIR section evaluates the potential effects of noise and groundborne vibration associated with
construction and operational activities that could occur as a result of implementation of the proposed
Transit Zoning Code (SD 84A and SD 8413) area. The Initial Study (Appendix A) identified the potential
for impacts to occur associated with a substantial temporary and/or permanent increase in ambient noise
levels within or around the Transit Zoning Code (SD 84A and SD 8413) area. Additionally, the Initial
Study identified the potential for people to be exposed to excessive noise levels, groundborne vibration,
or groundborne noise levels in excess of standards established in the local General Plan or noise
ordinance. Potential direct and indirect impacts resulting from construction and operation of the
proposed projects are identified, and potential mitigation measures that could avoid or reduce these
impacts are recommended, where feasible.
Issues scoped out include proximity to, or association with, an airport land use plan or airstrip. While the
proposed project area is located outside of the 20,000-foot notification area as required by the Orange
County Airport Land Use Commission (ALUC), the project must still comply with the Airport Environs
Element that was adopted by the City of Santa Ana in 2008, in order to comply with the Airport
Environs Land Use Plan (AELUP) for Orange County. Refer to Chapter 4.5 (Hazards and Hazardous
Materials) for analysis of this issue. Data used to prepare this report were taken from the Traffic Impact
Analysis Report prepared by KOA Corporation for the proposed project, and information obtained by
measuring and modeling existing and future noise levels at the Transit Zoning Code (SD 84A and
SD 84B) area and in the surrounding area.
Three comment letters associated with noise were received in response to the Notice of Preparation
circulated for the proposed project. The comment letters can be found in Appendix A.
4.8.1 Existing Conditions
The project is located in the central urban core of Santa Ana and comprises approximately 100 blocks
and 450 acres of land. The proposed project is generally bounded by First Street, Flower Street, Civic
Center Drive, Grand Avenue, and Interstate 5 (I-5). More specifically, the proposed project is located in
the area west of I-5, north of First Street, and between Grand Avenue and Flower Street and south of
Civic Center Drive in the City of Santa Ana in Orange County, California.
Several roadways provide access to properties within the Transit Zoning Code (SD 84A and SD 8413)
area, including Civic Center Drive, Fourth Street, First Street, and Santa Ana Boulevard, which run east -
west through the area, and Flower Street, Main Street and Grand Avenue, which run north -south
through the area.
The Transit Zoning Code (SD 84A and SD 8413) area includes the Government Center, downtown area,
the Logan and Lacy neighborhoods, and the industrial parks surrounding the Santa Ana Regional
Transportation Center (SARTC). The surrounding land uses include residential, professional,
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.8-1
Chapter Environmental Setting, Impacts, and Mitigation Measures
commercial, industrial, and civic uses and their environs. Specific adjacent (off -site) uses include the
following:
■ North: Single-family residential, office, and commercial uses, as well as I-5
■ East: Commercial and residential uses. I-5 is located immediately adjacent to portions of the
Transit Zoning Code (SD 84A and SD 84B) area
■ South: Institutional (including educational), commercial, industrial, and residential uses
■ West: Residential and commercial uses with open space located further to the west
Fundamentals of Sound and Environmental Noise
Sound is technically described in terms of amplitude (loudness) and frequency (pitch). The standard unit
of sound amplitude measurement is the decibel (dB). The decibel scale is a logarithmic scale that
describes the physical intensity of the pressure vibrations that make up any sound. The pitch of the
sound is related to the frequency of the pressure vibration. Because the human ear is not equally sensitive
to a given sound level at all frequencies, a special frequency -dependent rating scale has been devised to
relate noise to human sensitivity. The A -weighted decibel scale (dBA) provides this compensation by
discriminating against frequencies in a manner approximating the sensitivity of the human ear.
Noise, on the other hand, is typically defined as unwanted sound. A typical noise environment consists
of a base of steady "background" noise that is the sum of many distant and indistinguishable noise
sources. Superimposed on this background noise is the sound from individual local sources. These can
vary from an occasional aircraft or train passing by to virtually continuous noise from, for example,
traffic on a major highway. Table 4.8-1 (Representative Environmental Noise Levels) lists representative
noise levels for the environment.
Several rating scales have been developed to analyze the adverse effect of community noise on people.
Because environmental noise fluctuates over time, these scales consider that the effect of noise upon
people is largely dependent upon the total acoustical energy content of the noise, as well as the time of
day when the noise occurs. The L, is a measure of ambient noise, while the Ld„ and CNEL are measures
of community noise. Each is applicable to this analysis and defined as follows:
■ L,g, the equivalent energy noise level, is the average acoustic energy content of noise for a stated
period of time. Thus, the L,9 of a time -varying noise and that of a steady noise are the same if they
deliver the same acoustic energy to the ear during exposure. For evaluating community impacts,
this rating scale does not vary, regardless of whether the noise occurs during the day or the night.
■ L , , the Day -Night Average Level, is a 24-hour average Le7 with a 10 dBA "weighting" added to
noise during the hours of 10:00 P.M. to 7:00 A.M. to account for noise sensitivity in the nighttime.
The logarithmic effect of these additions is that a 60 dBA 24 hour L, would result in a
measurement of 66.4 dBA Ld,,.
■ CNEL, the Community Noise Equivalent Level, is a 24-hour average L,q with a 5 dBA
"weighting" during the hours of 7:00 P.M. to 10:00 P.M. and a 10 dBA "weighting" added to noise
during the hours of 10:00 P.M. to 7:00 A.M. to account for noise sensitivity in the evening and
4.8-2 City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR
4.8 Noise
nighttime, respectively. The logarithmic effect of these additions is that a 60 dBA 24 hour Leg
would result in a measurement of 66.7 dBA CNEL.
■ L,,, the minimum instantaneous noise level experienced during a given period of time.
■ L„ „ the maximum instantaneous noise level experienced during a given period of time.
TableRepresentative
Common Outdoor Activities
Nofse Level (dBA)
Environmental Noise Levels
Common Indoor Activities
Power Saw
—110—
Rock Band
Jet Fly -over at 100 feet
Crying Baby
Subway
—100—
Gas Lawnmower at 3 feet
Tractor
—g0—
Food Blender at 3 feet
Diesel Truck going 50 mph at 50 feet
—80—
Garbage Disposal at 3 feet
Noisy Urban Area during Daytime
Gas Lawnmower at 100 feet
—70—
Vacuum Cleaner at 10 feet
Commercial Area
Normal Speech at 3 feet
Heavy Traffic at 300 feet
—60—
Sewing Machine
Air Conditioner
Large Business Office
Quiet Urban Area during Daytime
—50—
Dishwasher in Next Room
Refrigerator
Quiet Urban Area during Nighttime
—40—
Theater, Large Conference Room (background)
Quiet Suburban Area during Nighttime
—30—
Library
Quiet Rural Area during Nighttime
Bedroom at Night, Concert Hall (background)
—20—
BroadcasNRecording Studio
—10—
Lowest Threshold of Human Hearing
—0—
Lowest Threshold of Human Hearing
SOURCE: League of the Hard of Hearing 2006
Noise environments and consequences of human activities are usually well represented by median noise
levels during the day or night, or over a 24-hour period. Environmental noise levels are generally
considered low when the CNEL is below 60 dBA, moderate in the 60 to 70 dBA range, and high above
70 dBA. Examples of low daytime levels are isolated, natural settings that can provide noise levels as low
as 20 dBA and quiet, suburban, residential streets that can provide noise levels around 40 dBA. Noise
levels above 45 dBA at night can disrupt sleep. Examples of moderate -level noise environments are
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.8-3
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
urban residential or semi -commercial areas (typically 55 to 60 dBA) and commercial locations (typically
60 dBA). People may consider louder environments adverse, but most will accept the higher levels
associated with more noisy urban residential or residential -commercial areas (60 to 75 dBA) or dense
urban or industrial areas (65 to 80 dBA). According to the City's Noise Control Ordinance, the exterior
noise level standard is 55 dBA from 7:00 A.M. to 10:00 P.M., and 50 dBA from 10:00 P.M. to 7:00 A.M.
The interior noise level standard is 55 dBA from 7:00 A.M. to 10:00 P.M., and 45 dBA from 10:00 P.M. to
7:00 A.M. Standards for impact noise, simple tone noise, speech, music, and any other combination are
5 dBA lower than the above standards, and noise levels exceeding these standards are limited to relatively
shorter periods of time.
When evaluating changes in 24-hour community noise levels, a difference of 3 dBA is a barely
perceptible increase to most people. A 5 dBA increase is readily noticeable, while a difference of 10 dBA
would be perceived as a doubling of loudness.
Noise levels from a particular source decline as distance to the receptor increases. Other factors, such as
the weather and reflecting or shielding, also intensify or reduce the noise level at a location. A common
method for estimating roadway noise is that for every doubling of distance from the source, the noise
level is reduced by about 3 dBA at acoustically "hard" locations (i.e., the area between the noise source
and the receptor is nearly complete asphalt, concrete, hard -packed soil, or other solid materials) and
4.5 dBA at acoustically "soft" locations (i.e., the area between the source and receptor is normal earth or
has vegetation, such as grass). Noise from stationary or point sources is reduced by about 6 to 7.5 dBA
for every doubling of distance at acoustically hard and soft locations, respectively. Noise levels may also
be reduced by intervening structures; generally, a single row of buildings between the receptor and the
noise source reduces the noise level by about 5 dBA, while a solid wall or berm reduces noise levels by 5
to 10 dBA. The manner in which older homes in California were constructed generally provides a
reduction of exterior -to -interior noise levels of about 20 to 25 dBA with closed windows. The exterior -
to -interior reduction of newer residential units is generally 30 dBA or more.
Fundamentals of Environmental Groundborne Vibration
Vibration is sound radiated through the ground. Groundborne noise is the rumbling sound caused by the
vibration of room surfaces. The ground motion caused by vibration is measured as particle velocity in
inches per second; in the U.S., this is referenced as vibration decibels (VdB).
The background vibration velocity level in residential and educational areas is usually around 50 VdB.
The vibration velocity level threshold of perception for humans is approximately 65 VdB. A vibration
velocity level of 75 VdB is the approximate dividing line between barely perceptible and distinctly
perceptible levels for many people. Most perceptible indoor vibration is caused by sources within
buildings, such as operation of mechanical equipment, movement of people, or the slamming of doors.
Typical outdoor sources of perceptible groundborne vibration are construction equipment, steel -wheeled
trains, and traffic on rough roads. If a roadway is smooth, the groundborne vibration from traffic is
rarely perceptible. The range of interest is from approximately 50 VdB, which is the typical background
vibration velocity level, to 100 VdB, which is the general threshold where minor damage can occur in
4.8-4 City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR
4.8 Noise
fragile buildings. Table 4.8-2 (Human Response to Different Levels of Groundborne Vibration)
describes the general human response to different levels of groundborne vibration velocity levels.
Vibration Velocity
Level
Human Reaction
65 VdB I Approximate threshold of perception for many people.
75 VdB Approximate dividing line between barely perceptible and distinctly perceptible. Many people find that
transportation -related vibration at this level is unacceptable.
85 VdB I Vibration acceptable only if there are an infrequent number of events per day.
SOURCE; HMMH, 2006
Existing Ambient Daytime Noise Levels
According to the Noise Element of the City of Santa Ana General Plan, the primary source of noise
within the City is traffic noise from major roadways and freeways within the area from mobile sources
such as automobiles, buses, trucks, and vehicles associated with construction equipment transport.
Secondary noise sources in the City include aircraft operations, railroad operations, and construction
activities. Also, stationary sources such as industrial activities, public gatherings, activities in open areas,
and the use of equipment in unenclosed spaces, produce a significant amount of noise.
Existing daytime noise levels were monitored at twelve locations around the project area, which are
depicted in Figure 4.8-1 (Noise Monitoring Locations), in order to identify representative noise levels at
various areas. The noise levels were measured using a Larson -Davis Model 814 precision sound level
meter, which satisfies the American National Standards Institute (ANSI) for general environmental noise
measurement instrumentation. The average noise levels and sources of noise measured at each location
are identified in Table 4.8-3 (Existing Noise Levels around the Proposed Transit Zoning Code [SD 84A
and SD 84B] Area). As shown, the daytime noise levels range from a high of 77.0 dBA to a low of
52.9 dBA and are characteristic of a typical urban area.
IM Existing Local Noise Environment
The Atchison, Topeka, and Santa Fe Railroad (AT&SF) tracks, which are used by Amtrak and Metrolink
for commuter train services during most of the day, run along the eastern edge of Santa Ana and through
the eastern portion of the Transit Zoning Code (SD 84A and SD 84B) area. Rail transit traveling at grade
typically produces a noise level of 80 dBA at a distance of 50 feet from the tracks while rail transit
stopped at a station typically produces a noise level of 65 dBA at a distance of 50 feet (HMMH 2O06). In
addition, the sounding of train horns, which is required when approaching at -grade crossings with streets
and highways for safety reasons, represents the highest noise levels associated with train services. The
sounding of a train horn can generate noise levels in excess of 110 dBA at a distance of 100 feet.
City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4,8-5
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
Table s Noise Levelsaround a ♦ • - • Transit Zoning
and So 848) Area
Location Primary Noise Sources
Code
Noise Level Statistics
Lp
(dBA)
L;;,,
(dBA)
L.
(dBA)
1 Santa Ana Blvd, east of Ross St.
Road Traffic
65.3
47.3
78.8
2 Main St. and Third St.
Road Traffic
71.9
54.8
90.2
3 Spurgeon St., between Santa Ana Blvd. and Civic Center Dr.
Road Traffic
59.0
49.2
70.9
4 1200 Block French St.
Road Traffic
57.5
39.9
77.6
5 700 Block 2nd St.
Road Traffic
54.2
44.2
71.7
6 Lacy St. and 5w St.
Road Traffic/Music
56.2
44.8
66.1
7 6'^ St. and Santiago St,
Road Traffic/Truck Yard
68.5
55.3
85.4
8 Rail Station Platform
Road Traffic/Trains
77.0
49.3
98.3
9 700 Block Eastwood Ave.
Road Traffic
52.9
46.1
63.7
10 2d St., between Grand Ave, and Hathaway St.
Road Traffic
58.8
48.4
77.3
11 Logan St, south of 1-5 Freeway
Freeway Traffic
74.0
71.0
77.6
12 1400 Block Hathaway St.
Freeway Traffic
60.8
58.3
65.9
SOURCE: PBS&J, January 5, 2010.
John Wayne Airport is located to the south of the City of Santa Ana and is served by several commercial
air carriers and commuter airlines. A small portion of Santa Ana located along the southeast border of
the City and not within the Transit Zoning Code (SD 84A and SD 8413) boundaries is located within the
airport's 60 CNEL noise contour.
Existing Roadway Noise Levels Off -Site
Existing roadway noise levels were calculated for the roadway segments in the project site vicinity that
have noise -sensitive uses facing the roadways. This task was accomplished using the Federal Highway
Administration Highway Noise Prediction Model (FHWA-RD-77-108) and traffic volumes from the
project traffic analysis. The model calculates the average noise level at specific locations based on traffic
volumes, average speeds, roadway geometry, and site environmental conditions. The average vehicle
noise rates (energy rates) utilized in the FHWA Model have been modified to reflect average vehicle
noise rates identified for California by Caitrans. The Caltrans data show that California automobile noise
is 0.8 to 1.0 dBA higher than national levels and that medium and heavy truck noise is 0.3 to 3.0 dBA
lower than national levels. The average daily noise levels along these roadway segments are presented in
Table 4.8-4 (Existing Roadway Noise Levels). As indicated, average daily noise levels along roadways
within the Transit Zoning Code (SD 84A and SD 8413) area range from a high of 74.4 dBA CNEL to a
low of 56.5 dBA CNEL.
4.8-6 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Noise
Table...
Roadway Segment
Reference 24-hour dBA CNEL Noise Level at 50 Feet=
Flower Street -Santa Ana Blvd to Civic Center Dr
67.6
Flower Street-17th St to Civic Center Dr
67.5
Civic Center Dr -West of Flower St
67.6
Civic Center Dr -Flower St to Ross St
67.3
Flower Street -Santa Ana Blvd to 1st St
67.6
Santa Ana Blvd -West of flower St
63.8
Santa Ana Blvd -Flower St to Parton St
64.7
Santa Ana Blvd -Parton St to Ross St
64.7
Civic Center Dr -Ross St to Broadway
66.8
Santa Ana Blvd -Ross St to Broadway
64.4
Broadway -Civic Center Dr to Santa Ana Blvd
67.7
Broadway -Civic Center Dr to Washington Ave
68.8
Civic Center Dr -Broadway to Sycamore St
66.7
Broadway -Santa Ana Blvd to 5th St
67.1
Santa Ana Blvd -Broadway to Sycamore St
63.6
Broadway-5th St to 4th St
67.0
5th St -Broadway to Ross St
61.0
5th St -Broadway to Main St
61.0
Broadway-3rd St to 4th St
67.0
Broadway-3rd St to 1 st St
67.0
Broadway -South of 1st St
65.5
1st St -Broadway to Ross St
73.8
1 st St -Main St to Broadway
73.6
Civic Center Dr -Sycamore St to Main St
66.7
Santa Ana Blvd -Sycamore St to Main St
63.6
5th St -Sycamore St to Broadway
61.0
5th St -Sycamore St to Main St
61.0
Main St -Civic Center Dr to Santa Ana Blvd
68.7
Main St -Civic Center Dr to Washington Ave
68.8
Civic Center Dr -Main St to Bush St
65.6
Main St -Santa Ana Blvd to 5th St
68.7
Santa Ana Blvd -Main St to Bush St
63.6
Main St-5th St to 4th St
68.7
5th St -Main St to Bush St
59.5
City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4.8-9
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
TableRoadway
Roadway Segment
Reference 24-hour d8A CNEL Noise Level at 50 Feet
Main St-3rd St to 4th St
68.2
Main St-1 at St to 3rd St
68.2
Santa Ana Blvd -Bush St to Spurgeon St
63.6
5th St -Bush St to French St
59.4
1 st St -Spurgeon St to Main St
73.7
Santa Ana Blvd -Lacy St to Standard Ave
65.3
Civic Center Dr -French St to Lacy St
65.6
Santa Ana Blvd -Lacy St to French St
65.0
4th St -Lacy St to French St
62.5
1st St -Lacy St to Spurgeon St
73.7
1stSt-Lacy St to Standard Ave
73.7
Santiago St -Washington Ave to Civic Center Dr
64.7
Santiago St -Washington Ave to 17th St
64.6
Santiago St -Santa Ana Blvd to Civic Center Dr
64.3
Civic Center Dr -Santiago St to Lacy St
65.5
Civic Center Dr -Lincoln Ave to Santiago St
56.5
Santiago St -Santa Ana Blvd to Brown St
63.1
Santa Ana Blvd -Santiago St to Lacy St
65.3
Santa Ana Blvd -Santiago St to U-24
68.0
4th St -Santiago St to Lacy St
64.5
Grand Ave-4th St to Santa Ana Blvd
72.1
Grand Ave -Santa Ana Blvd to 17th St
71.4
Santa Ana Blvd -East of Grand Ave
62.8
Grand Ave --1st St to 4th St
71.5
4th St -Grand Ave to Santiago St
64.5
4th St -East of Grand Ave
65.0
Grand Ave -South of 1st St
72.4
1 st St -Standard Ave to Grand Ave
73.8
1st St -East of Grand Ave
73.5
Penn Way -South of 1-5 SB Ramps
63.8
Penn Way -North of 1-5 SB Ramps
66.5
Santa Ana Blvd -West of 1-5 SB Ramps
69.7
Santa Ana Blvd -East of 1-5 SB Ramps
67.7
17th St -West of I-5 NB Ramps
74.4
17th St -East of 1-5 NB Ramps
73.4
4.8-10 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Noise
Grand Ave —South of 1-5 NIB Ramps 1 73.0
Grand Ave —North of 1-5 NB Ramos 1 797
SOURCE: PBS&J, 2010 (cc culafion data and results are provided in Appendix F).
a. Distances are in feet from roadway centerline. The identified noise level at 50 feet from the roadway centerline is for reference
purposes only. It does not reflect an actual building location or potential impact location.
Existing Groundborne Vibration Levels
The greatest regular source of ground -borne vibration in the Transit Zoning Code (SD 84A and SD 84B)
area and in the immediate vicinity is roadway traffic, bus traffic, and rail traffic. Trucks and buses
typically generate noticeable ground -borne vibration velocity levels at the edge of the road and typically
produce a vibration level of 65 VdB at a distance of 50 feet from the roadway. Trains typically generate
noticeable ground -borne vibration velocity levels at the edge of the right-of-way and typically produce a
vibration level of 75 VdB at a distance of 50 feet from the tracks (HMMH 2O06).
4.8.2 Regulatory Framework
Federal
The U.S. Department of IIousing and Urban Development (HUD) has set a goal of 45 dBA Ldn as a
desirable maximum interior standard for residential units developed under HUD funding. While HUD
does not specify acceptable exterior noise levels, residential dwellings constructed under Title 24 of the
California Code of Regulations typically provide 20 dBA of acoustical attenuation with the windows
closed and 10 dBA with the windows open. Based on this assumption, the exterior Ld or CNEL should
not exceed 65 dBA under normal conditions.
State
The California Department of Health Services (DHS) Office of Noise Control has previously studied the
correlation of noise levels and their effects on various land uses (DHS no longer exists). The most
current guidelines prepared by the State noise officer were issued in 1987. They are contained in the
"General Plan Guidelines" issued by the Governor's Office of Planning and Research in 1998. Noise -
compatible land use planning depends on the ability to locate noise -sensitive land uses in an acceptable
environment. Exterior noise environments are "normally acceptable" for schools and residences if they
are below 60 dBA Ldn (or CNEL) and "conditionally acceptable" below 70 dBA Ldn (or CNEL). A
"conditionally acceptable" designation implies that new construction or development should be
undertaken only after a detailed analysis of the noise reduction requirements and after necessary noise
insulation features are incorporated into the design of the new land use. By comparison, a "normally
acceptable" designation indicates that standard construction can occur without special noise reduction
requirements.
City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4.8-11
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
The types of land uses addressed by the State standards and the acceptable noise categories for each are
presented in Table 4.8-5 (Land Use Compatibility for Community Noise Sources). There is some overlap
between the categories, indicating the importance of judgment required when determining the
applicability of the numbers in certain situations.
Table;..
Land Use Category
- Sources
Noise Exposure (dBA CNEO
55 60 65 70 75 80
Residential —Low -Density Single Family, Duplex, Mobile Homes
Residential —Multiple Family
Transient Lodging —Motels, Hotels
School, Libraries, Churches, Hospitals, Nursing Homes
—
Auditoriums, Concert Halls, Amphitheaters
Sports Areas, Outdoor Spectator Sports
Playgrounds, Neighborhood Parks
Golf Course, Riding Stables, Water Recreation, Cemeteries
4.8-12 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Nolse
Nolse Exposure (dBA, CNEL)
Land Use Cafeaory 55 60 65 70 75 80
Office Buildings, Business, Commercial and Professional
Industrial, Manufacturing, Utilities, Agriculture
Normally Acceptable: Specified land use is satisfactory, based upon the assumption that any buildings involved
are of normal conventional construction without any special noise insulation requirements.
Conditionally Acceptable: New construction or development should be undertaken only after a detailed analysis
of the noise reduction requirements is made and needed noise insulation features included in the design.
Conventional construction, but closed windows and fresh air supply or air conditioning will normally suffice.
Normally Unacceptable: New construction or development should generally be discouraged. If new construction
or development does proceed, a detailed analysis of the noise reduction requirements must be made and needed
noise insulation features included in the design.
Clearly Unacceptable: New construction or development should generally not be undertaken.
SOURCE: Office of Noise Control, California Department of Healfh Services.
Title 24 of the California Code of Regulations requires performing acoustical studies before constructing
dwelling units in areas that exceed 60 dBA L,,. In addition, the California Noise Insulation Standards
identify an interior noise standard of 45 dBA CNEL for new multi -family residential units.
Local
City of Santa Ana General Plan
Noise Element
The Noise Element of the General Plan identifies sources of noise in the City and provides objectives
and policies that ensure that noise from various sources would not create an unacceptable noise
environment. It is a tool that City planners use to achieve and maintain land uses with compatible
environmental noise levels. As shown in Table 4.8-6 (City of Santa Ana Standards and Guidelines for
Noise Levels by Land Use), the City has established the following standards and guidelines for noise
levels for land use.
City of Santa Ana Transit Zoning Code (SD Wand SD 84B) EIR 4.8-13
Chapter 4 Environmental Setting; Impacts, and Mitigation Measures
Table 4.8;-6 City of
Land Use Category
Santa Ana Standards
Noise Levels by
and Guidelines
Land Use
Desirable Maximum
(CNEL dBA)
Maximum Acceptable
(CNEL dBA)
Residential, Low Density
55
65
Residential, Medium Density
60
65
Residential, High Density
65
70
Schools
60
70
Commercial, Office
65
70
Industrial
70
75
SOURCE: City of Santa Ana General Plan Noise Element
Based on these standards, exterior noise levels of 55 dBA CNEL and lower are desirable for single-family
residential uses, while exterior noise levels of 65 dBA CNEL and lower are desirable for high -density
multi -family residential uses. Incompatible land uses should not be developed in areas where existing
noise levels exceed the maximum acceptable guidelines. All residential uses should be protected with
sound insulation over and above that provided by normal building construction when constructed in
areas exposed to greater than 60 dBA CNEL.
The following goals, objectives, and policies from the Noise Element are relevant to the proposed
'Transit Zoning Code (SD 84A and SD 84B):
Goal Prevent significant increases in noise levels in the community and minimize the
adverse effects of currently existing noise sources
Objective 1.1 Prevent creation of new and additional sources of noise.
Objective 1.2 Reduce current noise levels of acceptable standards.
Implementation Policies
■ Require consideration of noise generation potential and
susceptibility to noise impacts in the siting, design and
construction of new developments
m Require mitigating site and building design features, traffic
circulation alternatives, insulation and other noise prevention
measures of those new developments which generate high
noise levels.
■ Sound insulate and/or buffer sensitive land uses such as
housing from adverse noise impacts in noise -prone areas
■ Minimize noise generation in residential neighborhoods
through control or elimination of truck traffic and through -
traffic from these areas
4.8-14 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Nolse
Consistency Analysis
As described under Impact 4.8-1, construction -related noise could negatively affect nearby sensitive
receptors. However, with the implementation of mitigation measures MM4.8-1 though MM4.8-4,
construction -related noise would be reduced. Sources of noise generated by implementation of the
proposed project would include new stationary sources (such as rooftop heating, ventilation, and air
conditioning [HVAC] systems for the residential and office uses). As discussed under Impact 4.8-2, these
noise sources have the potential to impact sensitive uses located both on- and off -site. Mitigation
measures MM4.8-5 though MM4.8-7 would reduce exterior noise levels affecting nearby sensitive uses to
below the exterior noise standard of 65 dBA CNEL. The primary source of noise in the vicinity of the
proposed project is traffic noise. As discussed in Impact 4.8-7, traffic generated by the proposed project
would generate noise along nearby road segments; however, the increase attributed to the proposed
project would not be substantial and would not affect nearby sensitive uses both on- and off -site.
However, portions of the Transit Zoning Code (SD 84A and SD 8413) area are located within close
proximity to the SARTC and the AT&SF rail line. As discussed in Impact 4.8-8, sensitive receptors may
be exposed to noise levels from trains in excess of the desired exterior noise standard of 65 dBA CNEL
and interior noise standard of 45 dBA CNEL. Implementation of mitigation measures outlined below
would reduce noise levels but below the standards set by the City. For the reasons listed above, the
proposed project is not consistent with Goal 1.
City of Santa Ana Municipal Code
The City of Santa Ana has also adopted a Noise Ordinance (Chapter 18, Article VI of the Santa Ana
Municipal Code), which identifies exterior noise standards, specific noise restrictions, exemptions, and
variances for sources of noise within the City. Section 18-311 of the Municipal Code designates the entire
City as Noise Zone 1 for exterior and interior noises. Section 18-312 of the Municipal Code establishes
exterior noise levels for residential land uses. The exterior noise standards established in the City's Noise
Ordinance are identified in Table 4.8-7 (City of Santa Ana Noise Ordinance Exterior Noise Standards). If
the ambient noise level is greater than the identified noise standards, the noise standard becomes the
ambient noise level without the offending noise.
TableOrdinance
Noise Level That May Not Be
Exceeded for More Than
Exterior
7:00 A.M.-10.*00 P.M.
N 6ise Stanclardi
10:00 P.M: 7.00 A.M.
30 minutes in any hour
55 dBA
50 dBA
15 minutes in any hour
60 dBA
55 dBA
5 minutes in any hour
65 dBA
60 dBA
1 minute in any hour
70 dBA
65 dBA
Any time
75 dBA
70 dBA
SOURCE: City of Santa Ana Municipal Code Section 18-312
In the event that the alleged offensive noise consists entirely of Impact noise, simple tone noise, speech, music or cry combination
thereof, the specified noise limits are reduced by 5 dB(A)
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.815
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
Section 18-313 of the Municipal Code establishes interior noise standards that apply to all residential
properties within the designation Noise Zone 1. Interior noise levels must not exceed 55 dBA between
the hours of 7:00 A.M. and 10:00 P.M. or 45 dBA between the hours of 10:00 P.M. and 7:00 A.M., as shown
in Table 4.8-8 (City of Santa Ana Noise Ordinance Interior Noise Standards). As with Section 18-312 of
the Municipal Code, if the ambient noise level is greater than the identified noise standards, the noise
standard becomes the ambient noise level without the offending noise.
Noise Level That May Not Be
Exceeded for More Than
7:00 A.M._10:00 P.M.
10:00 P.m,7.,00 A.M.
5 minutes in any hour
55 dBA
45 dBA
1 minute in any hour
60 dBA
50 dBA
Any time
65 dBA
55 dBA
SOURCE: City of Santa Ana Municipal Code Section 18-312
Interior noise measurements shall be made within the affected dwelling unit. The measurement shall be made at a point of least
four (4) feet from the wall, ceiling, or floor nearest the alleged offensive noise source and may be made with the windows of the
affected unit open. In the event the alleged offensive noise consists entirely of impact noise, simple tone noise, speech, music, or
any combination thereof, each of the above noise levels shall be reduced by five (5) dB(A).
Section 18-314 of the Noise Ordinance provides special provisions which exempt certain activities from
the standards established in the Noise Ordinance. As such, the following activities are exempt:
■ Activities conducted on the grounds of any public or private nursery, elementary, intermediate or
secondary school or college
■ Outdoor gatherings, public dances and shows, provided said events are conducted pursuant to a
license issued by the City of Santa Ana
■ Activities conducted on any park or playground, provided such park or playground is owned and
operated by a public entity
■ Any mechanical device, apparatus or equipment used, related to or connected with emergency
machinery, vehicle or work
■ Noise sources associated with construction, repair, remodeling, or grading of any real property,
provided said activities do not take place between the hours of 8:00 P.M. and 7:00 A.M. on
weekdays, including Saturday, or any time on Sunday or a federal holiday
m All mechanical devices, apparatus or equipment which are utilized for the protection or salvage of
agricultural crops during periods of potential or actual frost damage or other adverse weather
condition
■ Mobile noise sources associated with agricultural operations, provided such operations do not take
place between the hours of 8:00 P.M. and 7:00 A.M. on weekdays, including Saturday, or at any time
on Sunday or a federal holiday
■ Mobile noise sources associated with agricultural pest control through pesticide application,
provided that the application is made in accordance with restricted material permits issued by or
regulations enforced by the agricultural commissioner
4.8-16 City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR
4.8 Noise
■ Noise sources associated with the maintenance of real property, provided said activities take place
between 7:00 A.M. and 8:00 P.M. on any day except Sunday or a federal holiday, or between the
hours of 9:00 A.M. and 8:00 P.M. on Sunday or a federal holiday
■ Any activity to the extent regulation thereof has been preempted by state or federal law
Under Section 18-314(e) of the Municipal Code, construction activity noise sources are exempt from the
Noise Ordinance standards so long that the activities do not take place between the hours of 8:00 P.m.
and 7:00 A.M. on weekdays, including Saturday, or at any time on Sunday or a federal holiday.
4.8.3 Project Impacts and Mitigation
Analytic Method
Implementation of the proposed project could result in the introduction of noise levels that may exceed
permitted City noise levels. The primary sources of noise associated with the proposed project would be
construction activities within the Transit Zoning Code (SD 84A and SD 84B) area and project -related
traffic volumes associated with operation of those projects. Secondary sources of noise would include
new stationary sources (such as heating, ventilation, and air conditioning units) and increased human
activity throughout the Transit Zoning Code (SD 84A and SD 84B) area. In addition, land use allowed
under the Transit Zoning Code (SD 84A and SD 84B) could be affected by noise generated by existing
rail operations along the AT&SF tracks, which run through the eastern portion of the Transit Zoning
Code (SD 84A and SD 8413) area. The net increase in noise levels generated by these activities and other
sources have been quantitatively estimated and compared to the applicable noise standards and
thresholds of significance.
Aside from noise levels, groundborne vibration would also be generated during the construction phase of
the proposed projects within the Transit Zoning Code (SD 84A and SD 8413) area by various types of
construction equipment. In addition, land uses allowed under the Transit Zoning Code (SD 84A and
SD 8413) could be affected by groundborne vibration generated by existing rail operations along the
AT&SF tracks. Thus, the groundborne vibration levels generated by construction equipment have also
been quantitatively estimated and compared to applicable thresholds of significance.
Construction Noise Levels
Construction noise levels were estimated by data published by the U.S. Environmental Protection
Agency (U.S. EPA). Potential noise levels are identified for on- and off -site locations that are sensitive to
noise, including residences and schools.
The EPA has compiled data regarding the noise -generating characteristics of typical construction
activities. These noise levels would diminish rapidly with distance from the construction site, at a rate of
approximately 6 dBA per doubling of distance. For example, a noise level of 86 dBA measured at 50 feet
from the noise source to the receptor would reduce to 80 dBA at 100 feet from the source to the
receptor, and reduce by another 6 dBA to 74 dBA at 200 feet from the source to the receptor.
City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4.8-17
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
Roadway Noise Levels
Roadway noise levels have been calculated for various locations in and around the Transit Zoning Code
(SD 84A and SD 84B) area. The noise levels were calculated using the FHWA-RD-77-108 model and
traffic volumes from the project traffic study. The average vehicle noise rates (energy rates) utilized in the
FHWA Model have been modified to reflect average vehicle noise rates identified for California by
Caltrans. Traffic volumes used in the FHWA model are derived from the project traffic study, which is
provided in its entirety Appendix G and summarized in Section 4.11 (Transportation/Traffic) of this
document.
Railway Noise Levels
Railway noise levels resulting from railway operations occurring within the Transit Zoning Code
(SD 84A and SD 84B) area were estimated using data published by Harris Miller Miller & Hanson Inc.
(HMMH 2O06) for the Federal Transit Administration (FTA).
Vibration Levels Associated with Construction Equipment
Groundborne vibration levels resulting from construction activities occurring within the Transit Zoning
Code (SD 84A and SD 84B) area were estimated using data published by Harris Miller Miller & Hanson
Inc. (HMMH 2O06) for the FTA. Potential vibration levels are identified for on- and off -site locations
that are sensitive to vibration, including residences and schools.
Vibration Levels Associated with Railway Operations
Groundborne vibration levels resulting from railway operations occurring within the Transit Zoning
Code (SD 84A and SD 8413) area and were estimated using data published by Harris Miller M ller &
Hanson Inc. (HMMH 2O06) for the FTA. Potential vibration levels are identified for on -site locations
that are sensitive to vibration, including residences and schools.
FA Thresholds of Significance
The following thresholds are based on Appendix G of the CEQA Guidelines, as amended. For purposes
of this EIR, implementation of the proposed project may have a significant adverse impact on noise if it
would result in any of the following:
■ Expose persons to or generate noise levels in excess of standards established in the local general
plan or noise ordinance, or applicable standards of other agencies
■ Expose persons to or generate excessive groundborne vibration or groundborne noise levels
■ Cause a substantial permanent increase in ambient noise levels in the project vicinity above levels
existing without the project
■ Cause a substantial temporary or periodic increase in ambient noise levels in the project vicinity
above levels existing without the project
4.8-18 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Nolse
■ Expose people residing or working in the project site to excessive noise levels from a project
located within an airport land use plan or, where such a plan has not been adopted, within 2 miles
of a public airport or public use airport
■ Expose people residing or working in the project site to excessive noise levels from a project
located within the vicinity of a private airstrip
The CEQA Guidelines do not define the levels at which temporary and permanent increases in ambient
noise are considered "substantial." As discussed previously in this section, a noise level increase of 3 dBA
is barely perceptible to most people, a 5 dBA increase is readily noticeable, and a difference of 10 dBA
would be perceived as a doubling of loudness. Based on this information, the following thresholds would
apply to the operational characteristics of the proposed project:
■ Less than 3 dBA: not discernable, not significant
■ Greater than 3 dBA but less than 5 dBA: noticeable, but not significant, if noise levels remain
below 65 dBA CNEL noise level standard at sensitive land uses including residential uses
■ Five dBA or greater: potentially significant, if the noise increase would meet or exceed 65 dBA
CNEL noise level standard at sensitive land uses including residential uses
■ Five dBA or greater: potentially significant
- The CEQA Guidelines also do not define the levels at which groundbome vibration or groundborne
noise is considered "excessive." For the purpose of this analysis, groundborne vibration impacts
associated with human annoyance would be significant if the proposed project exceeds 85 VdB, which is
the vibration level that is considered by FTA to be acceptable only if there are an infrequent number of
events per day (as described in Table 4.8-2 [fIuman Response to Different Levels of Gooundbotne
Vibration]). In terms of groundborne vibration impacts on structures, this analysis will use FTA's
vibration damage threshold of approximately 100 VdB for fragile buildings and approximately 95 VdB
for extremely fragile historic buildings (HMMH 2O06).
Effects Found to Have No Impact
Threshold If the project is located within an airport land use plan or, where such a plan has
not been adopted, within 2 miles of a public airport or public use airstrip, would it
expose people residing or working in the project site to excessive noise levels?
As discussed in Section 4.6 (Hazards and Hazardous Materials), the proposed project is not located
within an airport land use plan or within 2 miles of a public airport or public use airport. The nearest
public airport to the project is the John Wayne Airport, which is located approximately 5.0 miles south of
the proposed project. Further, the proposed project is located over 5,000 feet from the 60 CNEL noise
contour for John Wayne Airport. Thus, no impact related to the exposure of people residing or working
in the project area to excessive airport related noise levels is anticipated, and no further analysis is
required in this FIR.
City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4.8-19
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
Threshold If the project is located within the vicinity of a private airstrip, would it expose
people residing or working in the project site to excessive noise levels?
The Transit Zoning Code (SD 84A and SD 8413) area is not located within the vicinity of a private
airstrip. Thus, no impact related to the exposure of people residing or working in the project site to
excessive airstrip -related noise levels is anticipated, and no further analysis is required in this EIR.
Effects Found to Be Less Than Significant
Threshold Would the project result in the exposure of persons to or generation of noise levels
in excess of standards established in the local general plan or noise ordinance, or
applicable standards of other agencies?
Impact 4.8-1 Construction activities associated with the proposed project would
generate noise levels that exceed the noise standards established by the
City of Santa Ana Municipal Code. This is considered a potentially
significant impact. Implementation of mitigation measures MM4.8-1
through MM4.8-4 would reduce this impact, but noise levels could still be
substantial. However, the project's construction noise impacts would be
temporary and would be consistent with the exemption for construction
noise that exists in the Municipal Code. Therefore, this impact would be
considered less than significant.
The proposed project has the potential to result in events that may exceed permitted noise levels. The
primary sources of noise associated with the proposed project would be construction activities and
project -related traffic volumes. Secondary sources include increased human activity throughout the sites.
Noise limits for sensitive uses established in Section 18-311 and 18-312 of the Santa Ana Municipal Code
are shown in Table 4.8-7 and Table 4.8-8.
Development of projects under the Transit Zoning Code (SD 84A and SD 8413) would require the use of
heavy equipment for demolition, site excavation, installation of utilities, site grading, paving, and building
fabrication. Construction activities would also involve the use of smaller power tools, generators, and
other sources of noise. During each stage of construction there would be a different mix of equipment
operating, and noise levels would vary based on the amount of equipment in operation and the location
of the activity.
The EPA has compiled data regarding the noise generating characteristics of specific types of
construction equipment and typical construction activities. These data are presented in Table 4.8-9
(Noise Ranges of Typical Construction Equipment) and Table 4.8-10 (Typical Outdoor Construction
Noise Levels). These noise levels would diminish rapidly with distance from the construction site at a
rate of approximately 6 dBA per doubling of distance. For example, a noise level of 86 dBA measured at
50 feet from the noise source to the receptor would reduce to 80 dBA at 100 feet from the source to the
receptor, and reduce by another 6 dBA to 74 dBA at 200 feet from the source to the receptor.
4.8-20 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Noise
TableRanges: 4.8-9 Noise
Equfpmenf
Equipment
Noise Levels in dBA L, of 50 Feet
Front Loader
73 to 86
Trucks
82 to 95
Cranes (moveable)
75 to 88
Cranes (derrick)
86 to 89
Vibrator
68 to 82
Saws
72 to 82
Pneumatic Impact Equipment
83 to 88
Jackhammers
81 to 98
Pumps
68 to 72
Generators
71 to 83
Compressors
75 to 87
Concrete Mixers
75 to 88
Concrete Pumps
81 to 85
Back Hoe
73 to 95
Pile Driving (peaks)
95 to 107
Tractor
77 to 98
Scraper/Grader
80 to 93
Paver
85 to 88
SOURCE: U.S. EPA 1971
a. Machinery equipped with noise control devices or other noise -reducing design features does not
generate the same level of noise emissions as that shown in this table.
Noise that would be experienced by sensitive uses due to development associated with implementation
of the proposed project is determined at their property lines. While the nearest sensitive uses vary at
different locations in and around the Transit Zoning Code (SD 84A and SD 8413) area and as specific
development plans have not yet been determined at individual sites, for the purpose of this analysis it is
assumed that sensitive receptors could be as close as 50 feet from where construction would take place.
Sensitive receptors in the project vicinity could experience noise levels up to 86 dBA Leg as a result of
construction activities, or as high as 107 dBA L.9 in the event that pile drivers are used. The City of Santa
Ana Municipal Code, Section 18-314(e) allows for noise resulting from construction activities to be
exempt from noise limits established in the Code. In accordance with the Noise Ordinance, construction
activities would also be limited to the hours of 7:00 A.M. and 8:00 P.M. Monday through Saturday, and is
prohibited on Sundays and federal holidays. As construction would not occur except during the times
permitted in the Noise Ordinance, and as the Municipal Code, Section 18-314(e) of the Municipal Code
allows construction noise in excess of standards to occur between these hours, the proposed project
would not violate established standards.
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.8-21
Chapter 4 Environmental Setting, Impaots, and Mitigation Measures
TableOutdoor
Construction Phase
Noise Levels at 50 Feet(dBA L. J
Noise Levels at 50 Feet with Mufflers (dBA L«J
Ground Clearing
84
82
Excavation, Grading
89
86
Foundations
78
77
Structural
85
83
Finishing
89
86
SOURCE: U.S. EPA 1971
The following mitigation measures shall be implemented as part of the proposed project:
MM4.8-1 All construction activity within the City shall be conducted in accordance with Section 18-314(e) of
the City of Santa Ana Municipal Code.
MM4.8-2 Each project applicant shall require by contract .rpecications that the following construction best
managementpractices (BMPs) be implemented by contractors to reduce construction noise levels:
■ Two weeks prior to the commencement of construction, notification must be provided to property
owners within 300 feet of a project site disclosing the construction schedule, including the various
types of activities that would be occurring throughout the duration of the construction period
■ Ensure that construction equipment is properly muffled according to industry standards and be in
good working condition
■ Place noise -generating construction equipment and locate construction staging areas away from
sensitive uses, where feasible
■ Schedule high noise producing activities between the hours of 8:00 A.M. and 5:00 P.M. to
minimitie disruption on sensitive uses
■ Implement noise attenuation measures, which may includz, but are not limited to, temporay noire
barriers or noise blankets around stationary construction noise sources
■ Use electric air compressors and similar power tools rather than diesel equipment, where feasible
■ Construction -related equipment, including heavy-duty equipment, motor vehicles, and portable
equipment, shall be turned off when not in use for more than 30 minutes
■ Construction hours, allowable workdays, and the phone number of the job super ntendent shall be
clearly posted at all construction entrances to allow for surrounding owners and residents to contact
the job superintendent. If the City or the job superintendent receives a complaint, the
superintendent shall investigate, take appropriate corrective action, and report the action taken to
the reportingpardy.
Contract specifications shall be included in the proposed project construction documents, which shall be
reviewed by the City prior to issuance of a grading permit.
MM4.8-3 Each pr ject applicant shall require by contract spec -cations that construction staging areas along
with the operation of earthmoving equipment within the project area would be located as far away from
vibration and noise sensitive sites as possible. Contract specifications shall be included in the proposed
4.8-22 City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR
4.8 Noise
project construction documents, which shall be reviewed by the City prior to issuance of a grading
permit.
MM4.8-4 Each project applicant shall require by contract specifications that heavily loaded trucks used during
construction would be routed away from residential streets. Contract specfications shall be included in
the proposed project construction documents, which shall be reviewed by the City prior to issuance of a
grading permit.
Implementation of mitigation measures MM4.8-1 through MM4.8-4 would ensure that impacts
associated with construction -related noise would be minimized. Therefore, this impact would be less
than significant
Impact 4.8-2 Operation of the proposed project could expose noise -sensitive land uses
to noise levels that exceed the standards established by the City of Santa
Ana General Plan. This is considered a potentially significant impact.
Implementation of mitigation measures MM4.8-5 through MM4.8-7 would
reduce this impact to a less-than-signiitcantlevel.
Sources of noise generated by implementation of the proposed project would include new stationary
sources (such as rooftop heating, ventilation, and air conditioning [HVAC] systems for the residential
and office uses). The proposed project would also introduce new activity and noise to the area as part of
the development of a new mix of uses under the proposed project. As shown in Table 4.8-3 (Existing
Noise Levels Within and Around the Transit Zoning Code (SD 84A and SD 84B) Area), noise
monitoring in the project area indicates that existing noise levels on site currently exceed the 65 dBA
"desirable maximum" noise standard for high density residential uses. Development of new residences in
areas where existing noise levels are over 65 dBA could constitute a significant impact. As the noise
levels monitored on -site exceed the 65 dBA thresholds, the project site would not meet acceptable noise
levels for a residential use. It should be noted that some monitoring locations such as Santa Ana Street,
east of Ross St., and the intersection of Main Street and Third Street, are located in institutional and
commercial areas, respectively, and contain uses that typically do not qualify as sensitive receptors.
Further, impacts related to substantial permanent increases in ambient noise levels that could potentially
result with implementation of the proposed project are discussed below under Impact 4.8-8.
The City of Santa Ana General Plan states that all residential uses should be protected with sound
insulation over and above that provided by normal building construction when constructed in areas
exposed to greater than 60 dBA CNEL. As such the following rrtigation measures shall be implemented
to all residential development within the Transit Zoning Code (SD 84A and SD 8413) area where the
existing noise levels exceed the 60 dBA CNEL standard established in the General Plan.
MM4.8-5 lFhen residential uses would be located in areas with noise levels in excess of 60 dBA CNEL (either
through conversion of uselstructure or new construction), the pr ject applicant shall provide noire
barriers around private open space areas, includa'ng patios and balconies, as necessary. The height and
density of the barriers shall be sufficient to reduce the exterior noise levels within private open space
areas to a CNEL of 65 dBA or less.
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.8-23
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
A&14.8-6 Prior to issuance of building permits, building plans shall sped the STC rating of windows and
doors far all residential land uses. Vindow and door ratings shall be sufficient to reduce the interior
noise level to a CNEL of 45 dBA or less, and shall be determined by a quaked acoustical
consultant as part of the f nal engineering design oj'the project.
As previously discussed, implementation of the proposed project would lead to the development of high -
density residential uses in areas that exceed the 65 dBA CNEL "Desirable Maximum," and this would be
considered a significant impact. However, implementation of mitigation measure MM4.8-5 would ensure
that exterior living spaces, such as porches and patios, are constructed in a manner that noise levels do
not exceed the 65 dBA CNEL. Further implementation of mitigation measure MM4.8-6 would ensure
that interior living spaces of the residential units do not exceed 45 dBA CNEL. Therefore, this impact
would be reduced to a level of less than significant.
In addition, the HVAC systems that would be installed for the new residential development associated
with the proposed project can result in noise levels that average between 50 and 65 dBA Lq at 50 feet
from the equipment. As 24-hour CNEL noise levels are about 6.7 dBA greater than 24-hour Leg
measurements, this means that the HVAC equipment associated with the retail -commercial buildings
could generate community noise levels that average between 57 to 72 dBA CNEL at 50 feet when the
equipment is operating constantly over 24 hours. These HVAC units would be mounted on the rooftops
of the proposed buildings and would be screened from view by building features. However, the
installation of shielding around these HVAC systems would be required as part of the proposed project,
as stated in mitigation measure MM4.8-7 below.
MM4.8-7 Each project applicant shall provide proper shielding for all new HVAC systems used by the
proposed residential and mixed use buildings to achieve an attenuation of 13 dBA at 50 feet from the
equipment.
The shielding installed around these systems would typically reduce noise levels by approximately
15 dBA, which could reduce HVAC system noise to approximately 50 dBA Lrq at 50 feet from the
equipment, which would be approximately 56.7 dBA CNEL. Implementation of mitigation measure
MM4.8-7 would ensure that impacts related to the HVAC systems would remain below the 65 dBA
CNEL "Desirable Maximum" exterior noise level guideline established in the City's General Plan for
high density residential uses. As such impacts to residents of the proposed project relating to HVAC
systems would be less than significant.
Threshold Would the project result in the exposure of persons to or generation of excessive
groundborne vibration or groundborne noise levels?
Impact 4.8-3 Operation of the proposed project would not generate and expose sensitive
receptors on site or off site to excessive groundborne vibration or
groundborne noise levels. This is considered a less -than -significant
impact.
During operation of the proposed project, background operational vibration levels would be expected to
average around 50 VdB, as discussed previously in this section. This is substantially less than the 85 VdB
4.8-24 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Nolse
threshold for people in the vicinity of the project site. Groundborne -vibration resulting from operation
of the proposed project would primarily be generated by trucks making periodic deliveries to the
proposed Transit Zoning Code (SD 84A and SD 84B) area. However, these types of deliveries would be
consistent with deliveries that are currently made along roadways to commercial uses in the proposed
Transit Zoning Code (SD 84A and SD 84B) area and in the proposed project vicinity and would not
increase groundborne vibration above existing levels. Because no substantial sources of groundborne
vibration would be built as part of the proposed project, no vibration impacts would occur during
operation of the proposed project. Therefore, operation of the proposed project would not expose
sensitive receptors on or off site to excessive groundborne vibration or groundborne noise levels, and
this impact would be less than significant.
Impact 4.8-4 Operation of the Southern California Regional Rail Authority's rail line
would not generate and expose sensitive receptors located within the
Transit Zoning Code (SD 84A and SD 8413) area to excessive groundborne
vibration or groundborne noise levels. This is considered a less -than -
significant impact.
Implementation of the Transit Zoning Code (SD 84A and SD 84B) would locate new sensitive land uses
within the vicinity of the existing railroad tracks. Problems for residential uses, such as disturbance due to
groundborne vibration from these sources, are usually contained to areas with n about 200 feet of the
vibration source (HMMII2006). Typically, the main effect of groundborne vibration is to cause
annoyances for occupants of nearby buildings. The proposed residential uses in the Logan
Neighborhood, Transit Village, and First Street Corridor could be located within 200 feet from the
centerline of the railroad. As discussed earlier, trains typically produce a vibration level of 75 VdB at a
distance of 50 feet from the tracks during operation and 65 dBA at a distance of 50 feet while stopped at
a train station, both of which are below the human annoyance threshold of 85 VdB. Therefore, the
occupants of the proposed residential units would not be exposed to potentially significant vibration
levels, and th s impact would be less than significant.
Threshold Would the project result in a substantial temporary or periodic increase in ambient
noise levels in the project vicinity above levels existing without the project?
Impact 4.8-5 Construction activities associated with the proposed project would result in
a substantial temporary or periodic increase in ambient noise levels.
However, the project's construction noise impacts would be temporary,
would not occur during recognized sleep hours, and would be consistent
with the exemption for construction noise that exists in the Municipal
Code. Therefore, this impact would be considered less than significant.
As discussed in Impact 4.8-1, construction activities associated with the proposed project could reach
above 86 dBA Leg within 50 feet of the proposed project site. These construction activities would
represent a substantial temporary or periodic increase in ambient noise levels. As discussed previously
under "Thresholds of Significance," this analysis assumes that an increase of 5.0 dBA or greater over
ambient noise levels is substantial and significant. As shown in Table 4.8-3, the highest existing daytime
ambient noise level monitored in the project vicinity was 77.0 dBA Leg at the Rail Station Platform. As
City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4.8-25
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
such, the noise generated by construction activities for the proposed project could result in a temporary
increase in ambient noise levels of over 5 dBA at uses adjacent to the project site. However, with
implementation of mitigation measure MM4.8-1, the construction activities would only occur during the
permitted hours designated in the City of Santa Ana Municipal Code Section 18-314(e), and thus would
not occur during recognized sleep hours for residences or on days that residents are most sensitive to
exterior noise (Sundays and federal holidays). As such, while the physical impact from an increase in
ambient noise levels could occur from the construction activities associated with the proposed project, an
adverse effect on the nearby residents would not occur. Implementation of mitigation measures
MM4.8-2 through MM4.8-4 would also help reduce this impact. Therefore, with mitigation, this impact
would be less than significant.
Impact 4.8-6 Operation of the proposed project would not result in temporary or
periodic increases in ambient noise levels. There would not be a
substantial temporary or periodic increase and, thus, this impact would be
less than significant.
Operation of the proposed project would not include special events or temporary activities which would
cause an increase in ambient noise levels. In addition, operation of the proposed project would not
require periodic use of special stationary equipment that would expose off -site sensitive receptors to an
increase in ambient noise levels above those existing without the proposed project. Therefore, there
would be no temporary or periodic noise impacts to on- or off -site receptors due to operation of the
proposed project. This impact would be less than sigtzi6cant.
Threshold Would the project result in a substantial permanent increase in ambient noise
levels in the project vicinity above levels existing without the project?
Impact 4.8-7 Operation of the proposed project would not generate increased local
traffic volumes that would cause a substantial permanent increase in
ambient noise levels in the project vicinity. This is considered a less -than -
significant impact.
The increase in traffic resulting from implementation of the proposed project would increase the ambient
noise levels at sensitive off -site locations in the project vicinity. Traffic was analyzed both for near -term
project opening year (2030) and long range (2035) General Plan buildout conditions. Traffic analyzed as
part of the 2030 traffic analysis was derived from existing traffic, an ambient growth factor of 0.5 percent
per year and the traffic that is anticipated to occur based on known development projects within the
vicinity of the study area that will contribute some (or all) of their traffic to the various study area
roadways and intersections. Traffic analyzed as part of the 2035 traffic analysis was obtained from the
OCTA Traffic Demand model. Previous analysis was conducted by using OCTAM 3.2 travel demand
forecasting model. KOA conducted screenline analysis for OCTA's later version model OCTAM 3.3.
The screenline analysis surrounding the City indicates that OCTAM 3.3 represents about 11 percent
higher traffic volumes forecasting for both the AM and PM peak hour models. KOA therefore applied
an 11 percent growth factor to the original OCTAM 3.2 traffic volume forecast. The growth in housing,
population, and employment included in the OCP-2004 demographic projections is consistent with the
4.8-26 City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR
4.8 Noise
anticipated growth that is expected in conjunction with buildout of the City of Santa Ana General Plan
land uses and circulation element.
Table 4.8-11 compares near -term (2030) conditions with the project to existing conditions to identify the
overall change in future noise levels along study area roadway segments. As discussed previously, a
difference of 3.0 dBA between 24-hour noise levels is a barely perceptible increase to most people. A
5.0 dBA increase is readily noticeable, and a difference of 10 dBA would be perceived as a doubling of
loudness. Existing traffic noise levels are identified in Table 4.8-4. Noise levels associated with traffic
generated from existing conditions within the proposed project area were calculated along study -area
roadway segments using traffic data from the traffic study (included in Appendix G). In addition,
Table 4.8-10 (Traffic Noise Impacts for Year 2030) also compares near -term (2030) with project
conditions to near -term (2030) without project conditions to determine the project's contribution to
changes in noise levels along study area roadway segments.
Noise Levels In dBA CNEL at 50 feet
Increase
with Project
Year 2030
Year 2030
over
Exceeds
Existing
Without Project
With Project
Existing
Project
Significance
Significance
Roadway Segment
Conditions _.._7raific
Volumes
-TraRc Volumes
Conditions
Conidbution
Threshold= -
Threshold?
Flower Street -Santa
Ana Blvd to Civic
67.6
68.2
68.2
0.6
0.0
3.0
No
Center Dr
Flower Street-17th
St to Civic Center Dr
67.5
67.9
68.0
0.5
0.1
3.0
No
Civic Center Dr-
West of Flower St
67.6
68.1
68.3
0.7
0.2
3.0
No
Civic Center Dr -
67.3
67.8
68.1
0.8
0.3
3.0
No
Flower St to Ross St
Flower Street -Santa
67.6
68.2
68.3
0.7
0.1
3.0
No
Ana Blvd to 1st St
Santa Ana Blvd-
63.8
64.2
64.6
0.8
0.4
5.0
No
West of Flower St
Santa Ana Blvd-
64.7
65.1
65.6
0.9
0.5
5.0
No
Flower St to Parton St
Santa Ana Blvd-
64.7
65.1
65.6
0.9
0.5
5.0
No
Parton St to Ross St
Civic Center Dr -
66.8
67.4
67.8
1.0
0.4
3.0
No
Ross St to Broadway
Santa Ana Blvd -
64.4
64.9
65.4
1.0
0.5
5.0
No
Ross St to Broadway
Broadway -Civic
Center Dr to Santa
67.7
68.3
68.3
0.6
0.0
3.0
No
Ana Blvd
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.8-27
Chapter 4 Environmental Setting Impacts, and Mitigation Measures
Noise Levels in dBA CNEL at 50 feet
Increase
with Project
Year203O
Year 2030
over
Exceeds
Existing
Without Project
With Project
Existing
Project
Significance
Significance
Roodway Segment
Conditions
TraRlc Volumes
Traffic Volumes
Conditions
Contribution
Threshold-
Threshold?
Broadway -Civic
Center Dr to
68.8
69.4
69.5
0.7
0.1
3.0
No
Washington Ave
Civic Center Dr -
Broadway to
66.7
67.3
67.7
1.0
0.4
3.0
No
Sycamore St
Broadway -Santa
67.1
67.6
67.7
0.6
0.1
3.0
No
Ana Blvd to 5th St
Santa Ana Blvd -
Broadway to
63.6
64.3
64.5
0.9
0.2
5.0
No
Sycamore St
Broadway-5th St to
67.0
67.6
67.7
0.7
0.1
3.0
No
4th St
5th St -Broadway to
61.0
61.4
61.8
0.8
0.4
5.0
No
Ross St
5th St -Broadway to
61.0
61.4
61.7
0.7
0.3
5.0
No
Main St
Broadway-3rdSt to
67.0
67.5
67.7
0.7
0.2
3.0
No
4th St
Broadway-3rdSt to
67.0
67.5
67.8
0.8
0.3
3.0
No
1st St
Broadway -South of
65.5
66.4
66.5
1.0
0.1
3.0
No
1st St
1 st St -Broadway to
73.8
74.4
74.5
0.7
0.1
3.0
No
Ross St
1st St -Main St to
73.6
74.5
74.6
1.0
0.1
3.0
No
Broadway
Civic Center Dr -
Sycamore St to Main
66.7
67.1
67.5
0.8
0.4
3.0
No
St
Santa Ana Blvd -
Sycamore St to Main
63.6
64.1
64.4
0.8
0.3
5.0
No
St
5th St -Sycamore St
61.0
61.4
61.7
0.7
0.3
5.0
No
to Broadway
5th St -Sycamore St
61.0
61.5
61.8
0.8
0.3
5.0
No
to Main St
Main St -Civic Center
68.7
69.2
69.4
0.7
0.2
3.0
No
Dr to Santa Ana Blvd
Main St -Civic Center
68.8
69.4
69.5
0.7
0.1
3.0
No
Dr to Washington Ave
4.8-28 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Noise
Noise Levels in dBA CNEL at 50 feet
Increase
with Project
Year203O
Yecr203O
over
Exceeds
Existing
Wdhout Project
Wdh Project
Existing
Project
Significance
Significance
Roadway Segment
Conditions
Traffic Volumes
Traffic Volumes
Conditions
Contribution
Threshold-
Threshold?
Civic Center Dr -Main
65.6
66.1
66.5
0.9
0.4
3.0
No
St to Bush St
Main St -Santa Ana
68.7
69.4
69.6
0.9
0.2
3.0
No
Blvd to 5th St
Santa Ana Blvd-
63.6
64.1
64.4
0.8
0.3
5.0
No
Main St to Bush St
Main St-5th St to 4th
68.7
69.4
69.6
0.9
0.2
3.0
No
St
5th St -Main St to
59.5
60.1
60.5
1.0
0.4
5.0
No
Bush St
Main St-3rd St to 4th
68.2
68.9
69.2
1.0
0.3
3.0
No
St
Main St -1st St to 3rd
68.2
68.9
69.2
1.0
0.3
3.0
No
St
Santa Ana Blvd -
Bush St to Spurgeon
63.6
64.1
64.3
0.7
0.2
5.0
No
St
5th St -Bush St to
59.4
59.9
60.3
0.9
0.4
5.0
No
French St
1st St -Spurgeon St
73.7
74.2
74.4
0.7
0.2
3.0
No
to Main St
Santa Ana Blvd -
Lacy St to Standard
65.3
65.8
65.8
0.3
0.0
3.0
No
Ave
Civic Center Dr -
65.6
66.5
66.8
12
0.3
3.0
No
French St to Lacy St
Santa Ana Blvd -
65.0
65.6
66.1
1.1
0.5
3.0
No
Lacy St to French St
4th St -Lacy St to
62.5
62.9
63.0
0.5
0.1
5.0
No
French St
1stSt-Lacy St to
73.7
74.2
74.4
0.7
0.2
3.0
No
Spurgeon St
1 st St -Lacy St to
73.7
74.2
74.4
0.7
0.2
3.0
No
Standard Ave
Santiago St -
Washington Ave to
64.7
65.4
65.9
1.2
0.5
5A
No
Civic Center Dr
Santiago St -
Washington Ave to
64.6
65.2
65.6
1.0
0.4
5.0
No
17th St
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.8-29
Chapter 4 Environmental Setting Impacts, and Mitigation Measures
Noise Levels in dBA CNEL at 50 feet
Increase
with Project
Year2030
Year2030
over
Exceeds
Existing
Without Project
With Project
Existing
Project
Significance
Significance
Roadway Segment
Conditions
Traffic Volumes
Traffic Volumes
Conditions
Contribution
Threshold^
Threshold?
Santiago St -Santa
Ana Blvd to Civic
64.3
65.2
65.9
1.6
0.7
5.0
No
Center Dr
Civic Center Dr -
65.5
66.0
66.2
0.7
0.2
3.0
No
Santiago St to Lacy St
Civic Center Dr -
Lincoln Ave to
65.4
66.0
66.0
0.6
0.0
5.0
No
Santiago St
Santiago St -Santa
63.1
63.5
64.7
1.6
0.2
5.0
No
Ana Blvd to Brown St
Santa Ana Blvd-
65.3
65.9
66.6
1.3
0.7
3.0
No
Santiago St to Lacy St
Santa Ana Blvd -
68.0
68.7
69.0
1.0
0.3
3.0
No
Santiago St to U-24
4th St -Santiago St to
64.5
64.9
65.0
0.5
0.1
5.0
No
Lacy St
Grand Ave-4th St to
721
72.7
72.8
0.7
0.1
3.0
No
Santa Ana Blvd
Grand Ave -Santa
71.4
72.1
72.5
1.1
0.4
3.0
No
Ana Blvd to 17th St
Santa Ana Blvd -East
62.8
63.5
63.5
0.7
0.0
5.0
No
of Grand Ave
Grand Ave-1 st St to
71.5
72.0
72.2
0.7
0.2
3.0
No
4th St
4th St -Grand Ave to
64.5
65.0
65.5
1.0
0.5
5.0
No
Santiago St
4th St -East of Grand
65.0
65.6
65.8
0.8
0.2
3.0
No
Ave
Grand Ave -South of
72.4
73.1
73.3
0.9
0.2
3.0
No
1 st St
1 st St -Standard Ave
73.8
74.4
74.6
0.8
0.2
3.0
No
to Grand Ave
1 st St -East of Grand
73.5
73.9
74.1
0.6
0.2
3.0
No
Ave
Penn Way -South of
63.8
64.5
65.0
1.2
0.5
5.0
No
1-5 SB Ramps
Penn Way -North of
66.5
66.9
67.2
0.7
0.3
3.0
No
1-5 SB Ramps
Santa Ana Blvd -
69.7
70.1
70.8
1.1
0.73.0
No
West of 1-5 SB Ramps
4.8-30 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Noise
Noise Levels in dBA CNEL at 50 feet
Increase
with Project
Yeor2030
Year203O
over
Exceeds
Existing
Without Project
With Project
Existing
Project
Significance
Significance
Roadway Segment
Conditions
Traffic Volumes
Traffic Volumes
Conditions
Contribution
Threshold-
Threshold?
Santa Ana Blvd -East
of 1-5 SB Ramps
67.7
68.2
68.9
1.2
0.7
3.0
No
17th St -West of 1-5
NB Ramps
74.4
74.8
74.8
0.4
0.0
3.0
No
17th St -East of 1-5
73.4
73.8
73.8
0.4
0.0
3.0
No
INS Ramps
Grand Ave -South of
73.0
73.5
73.8
0.8
0.3
3.0
No
1-5 NB Ramps
Grand Ave-Nofth of
72.7
73.2
73.3
0.6
0.1
3.0
No
1-5 NB Ramps
SOURCE: PSS&J, 2010 (calculation data and results are provided in Appendix F).
a. Significance Thresholds are set as follows:
5.0 dBA CNEL if the noise increase is below the City of Santa Ana standard of 65 dBA CNEL
3.0 dBA CNEL if the noise Increase meets or exceeds the City of Santa Ana standard of 65 dBA CNEL
Similarly, Table 4.8-12 (Traffic Noise Impacts for Year 2035) compares long-term (2035) conditions with
the project to existing conditions to identify the overall change in future noise levels along study area
roadway segments. In addition, Table 4.8-12 also compares long-term (2035) with project conditions to
long-term (2035) without project conditions to determine the project's contribution to changes in noise
levels along study area roadway segments.
Noise Levels in dBA CNEL at 50 feet
Increase
with Project
Year2035
Year 2035
over
Exceeds
Existing
Without Project
With Project
Existing
Project
Significance
Significance
Roadway Segment
Conditions
Traffic Volumes
Traffic Volumes
Conditions
Contribution
Threshold-
Threshold?
Flower Street -
Santa Ana Blvd to
67.6
68.8
68.8
1.2
0.0
3.0
No
Civic Center Dr
Flower Street-17th
67.5
68.5
68.6
1.1
0.1
3.0
No
St to Civic Center Dr
Civic Center Dr-
67.6
68.6
68.8
1.2
0.2
3.0
No
West of Flower St
Civic Center Dr -
67.3
68.4
68.7
1.4
0.3
3.0
No
Flower St to Ross St
Flower Street -
Santa Ana Blvd to
67.6
69.2
69.2
1.6
0.0
3.0
No
1 st St
City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4.8-31
Chapter Environmental Setting, Impacts, and Mitigation Measures
Noise Levels in dBA CNEL at 50 feet
Increase
wdh Project
Year2035
Year2035
over
Exceeds
Existing
Without Project
with Project
Existing
Project
Significance
Significance
Roadway Segment
Conditions
Traft Volumes
TraRc Volumes
Conditions
Contribution
Threshold-
threshold?
Santa Ana Blvd -
West of Flower St
63.8
64.9
65.3
1.5
0.4
5.0
No
Santa Ana Blvd -
Flower St to Parton
64.7
65.7
66.1
1.4
0.4
5.0
No
St
Santa Ana Blvd-
Parton St to Ross St
64.7
66.3
66.6
1.9
0.3
5.0
No
Civic Center Dr -
Ross St to
66.8
68.0
68.3
1.5
0.3
3.0
No
Broadway
Santa Ana Blvd -
Ross St to
64.4
65.6
66.0
1.6
0.4
5.0
No
Broadway
Broadway -Civic
Center Dr to Santa
67.7
68.8
68.8
1.1
0.0
3.0
No
Ana Blvd
Broadway -Civic
Center Dr to
68.8
69.8
69.9
1.1
0.1
3.0
No
Washington Ave
Civic Center Dr -
Broadway to
66.7
68.0
68.3
1.6
0.3
3.0
No
Sycamore St
Broadway -Santa
67.1
68.1
68.2
1.1
0.1
3.0
No
Ana Blvd to 5th St
Santa Ana Blvd -
Broadway to
63.6
65.0
65.2
1.6
0.2
5.0
No
Sycamore St
Broadway-5th St to
4th St
67.0
68.1
68.3
1.3
0.2
3.0
No
5th St -Broadway to
61.0
62.0
62.3
1.3
0.3
5.0
No
Ross St
5th St -Broadway to
Main St
61.0
63.2
63.5
2.5
0.3
5.0
No
Broadway-3rd St
to 4th St
67.0
68.1
68.3
1.3
0.2
3.0
No
Broadway-3rd St
to 1 at St
67.0
69.2
69.3
2.3
0.1
3.0
No
Broadway -South of
65.5
66.6
66.6
1.1
0.0
3.0
No
1st St
1st St -Broadway to
Ross St
73.8
74.8
74.9
1.1
0.1
3.0
No
4.8-32 City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR
4.8 Nolse
Noise Levels in dBA CNEL at 50 feet
Increase
with Project
Year2035
Year2035
over
Exceeds
Existing
Without Project
With Project
Existing
Project
Significance
Significance
Roadway Segment
Conditions
Traffic Volumes
Traffic Volumes
Conditions
Contribution
Threshold-
Threshold?
1stSt-Main Stto
Broadway
73.6
74.8
74.9
1.3
0.1
3.0
No
Civic Center Dr -
Sycamore St to
66.7
67.7
68.1
1.4
0.4
3.0
No
Main St
Santa Ana Blvd -
Sycamore St to
63.6
64.7
64.9
1.3
0.2
5.0
No
Main St
5th St -Sycamore
61.0
62.0
62.3
1.3
0.3
5.0
No
St to Broadway
5th St -Sycamore
St to Main St
61.0
62.0
62.3
1.3
0.3
5.0
No
Main St -Civic
Center Dr to Santa
68.7
69.8
70.0
1.3
0.2
3.0
No
Ana Blvd
Main St -Civic
Center Dr to
68.8
69.9
70.1
1.3
0.2
3.0
No
Washington Ave
Civic Center Dr-
65.6
66.7
67.0
1.4
0.3
3.0
No
Main St to Bush St
Main St -Santa Ana
Blvd to 5th St
68.7
70.0
70.2
1.5
0.2
3.0
No
Santa Ana Blvd -
Main St to Bush St
63.6
65.0
65.2
1.6
0.2
5.0
No
Main St-5th St to
4th St
68.7
70.0
70.2
1.5
0.2
3.0
No
5th St -Main St to
Bush St
59.5
61.7
61.9
2.4
0.2
5.0
No
Main St-3rd St to
4th St
68.2
69.4
69.8
1.6
0.4
3.0
No
Main St 1st St to
68.2
69.4
69.7
1.5
0.3
3.0
No
3rd St
Santa Ana Blvd -
Bush St to
63.6
64.7
64.9
1.3
0.2
5.0
No
Spurgeon St
5th St -Bush St to
59.4
60.5
60.9
1.5
0.4
5.0
No
French St
1 st St -Spurgeon St
73.7
74.8
75.0
1.3
0.2
3.0
Na
to Main St
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.833
Chapter Environmental Setting, Impacts, and Mitigation Measures
Noise Levels in daA CNEL at 50 feet
Increase
with Project
Year2035
Year2035
over
Exceeds
Existing
Without Project
Wth Project
Existing
Project
Signiricance
Significance
Roadway Segment
Conditions
Trafic Volumes
Traffic Volumes
Conditions
Contribution
Threshold
Threshold?
Santa Ana Blvd -
Lacy St to Standard
65.3
66.5
66.5
1.2
0.0
3.0
No
Ave
Civic Center Dr -
65.6
66.9
67.2
1.6
0.3
3.0
No
French St to Lacy St
Santa Ana Blvd -
65.0
66.2
66.7
1.7
0.5
3.0
No
Lacy St to French St
4th St -Lacy St to
62. 5
63.6
63.7
1.2
0.1
5.0
No
French St
1stSt-Lacy St to
73.7
74.9
75.0
1.3
0.1
3.0
No
Spurgeon St
1stSt-Lacy St to
73.7
74.9
75.0
1.3
0.1
3.0
No
Standard Ave
Santiago St -
Washington Ave to
64.7
67.7
68.1
3.4
0.4
5.0
No
Civic Center Dr
Santiago St -
Washington Ave to
64.6
67.1
67.4
2.8
0.3
5.0
No
17th St
Santiago St -Santa
Ana Blvd to Civic
64.3
67.9
68.3
4.0
5.0
No
Center Dr
Civic Center Dr -
FOA
Santiago St to Lacy
65.5
66.6
66.8
1.3
3.0
No
St
Civic Center Dr -
Lincoln Ave to
65.4
66.4
66.5
1.1
0.1
5.0
No
Santiago St
Santiago St -Santa
Ana Blvd to Brown
63.1
64.1
65.2
2.1
1.1
5.0
No
St
Santa Ana Blvd -
Santiago St to Lacy
65.3
67.7
68.2
2.9
0.5
3.0
No
St
Santa Ana Blvd-
68.0
69.8
70.1
2.1
0.3
3.0
No
Santiago St to U-24
4fh St -Santiago St
64.5
65.5
65.6
1.1
0.1
5.0
No
to Lacy St
Grand Ave-4th St
721
73.3
73.4
1.3
0.1
3.0
No
to Santa Ana Blvd
4.8-34 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Noise
Noise Levels in dBA CNEL at 5o feet
Increase
with Project
Year2035
Year2035
over
Exceeds
Existing
Without Project
With Project
Existing
Project
Significance
Signiticance
Roadway Segment
Conditions
TraRC Volumes
TFaitic Volumes
Conditions
Contribution
Threshold^
Threshold?
Grand Ave -Santa
71.4
73.2
73.6
2.2
0.4
3.0
No
Ana Blvd to 17th St
Santa Ana Blvd-
62.8
63.9
63.9
1.1
0.0
5.0
No
East of Grand Ave
Grand Ave -1st St
71.5
72.5
72.7
1.2
0.2
3.0
No
to 4th St
4th St -Grand Ave
64.5
65.5
66.0
1.5
0.5
5.0
No
to Santiago St
St -East of
65.0
66.1
66.2
1.2
0.1
3.0
No
Grand Ave
Grand
Grand Ave -South
724
73.7
73.9
1.5
0.2
3.0
No
of 1 at St
1 st St -Standard
73.8
75.1
75.2
1.4
0.1
3.0
No
Ave to Grand Ave
1stSt-East of
73.5
74.6
74.7
1.2
0.1
3.0
No
Grand Ave
Penn Way -South
63.8
66.7
67.0
3.2
0.3
5.0
No
of 1-5 SB Ramps
Penn Way -North of
66.5
67.6
67.8
1.3
0.2
3.0
No
1-5 SB Ramps
Santa Ana Blvd -
West of 1-5 SB
69.7
70.7
71.3
1.6
0.6
3.0
No
Ramps
Santa Ana Blvd -
East of 1-5 SB
67.7
68.8
69.5
1.8
0.7
3.0
No
Ramps
17th St -West of 1-5
74.4
75:4
75.4
1.0
0.0
3.0
No
NB Ramps
17th St -East of 1-5
73.4
74.4
74.4
1.0
0.0
3.0
No
INS Ramps
Grand Ave -South
73.0
74.3
74.6
1.6
0.3
3.0
No
of 1-5 NB Ramps
Grand Ave -North
72.7
74.1
74.2
1.5
0.1
3.0
No
of 1-5 NB Ramps
SOURCE: PBS&J, 2010 (calculation data and results are provided in Appendix F(,
a. Significance Thresholds are set as follows:
5.0 dBA CNEL if the noise increase Is below the City of Santa Ana standard of 65 dBA CNEL
3.0 dBA CNEL if the noise increase meets or exceeds the City of Santa Ana standard of 65 dBA CNEL
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.8-35
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
As stated in the Thresholds of Significance, a 3.0 dBA CNEL increase is considered substantial if the
noise increase would meet or exceed the City's 65 dBA CNEL noise level standard at high density
residential uses, and a 5.0 dBA CNEL increase is considered substantial where existing noise levels are
below the 65 dBA CNEL standard at high density residential uses. As shown in Table 4.8-11 (Traffic
Noise Impacts for Year 2030) and Table 4.8-12 (Traffic Noise Impacts for Year 2035), none of the
roadways within the Transit Zoning Code (SD 84A and SD 8413) area would result in a 3.0 dBA or
5.0 dBA CNEL increase over existing conditions with implementation of the proposed project under
both scenarios. Likewise, the contribution of the proposed project to this increase under both scenarios
would not exceed 3.0 dBA or 5.0 dBA CNEL. Therefore, this impact would be considered less than
significant.
Effects Found to Be Significant
Threshold Would the project result in the exposure of persons to or generation of noise levels
in excess of standards established in the local general plan or noise ordinance, or
applicable standards of other agencies?
Impact 4.8-8 Operation of the Southern California Regional Rail Authority's (SCRRA)
rail line would potentially expose noise -sensitive land uses located within
the Transit Zoning Code (SD 84A and SD 84B) area to noise levels that
exceed the standards established by the City of Santa Ana General Plan.
This is considered a significant and unavoidable impact.
Under the Transit Zoning Code (SD 84A and SD 8413), additional sensitive uses (primarily residential
structures) would be located in close proximity (approximately 100 feet) to the SCRRA rail line. As stated
previously, typical commuter train noise produces a noise level of 80 dBA at 50 feet from the tracks,
while a stopped commuter train would produce a noise level of 65 dBA. Per the Federal Railway
Administration, noise levels associated with trains are anticipated to attenuate/reduce at a rate of
4.5 dBA for each doubling of distance. As such, potentially noise -sensitive uses, such as residential
structures, would likely experience noise levels ranging from 60.5 to 75.5 dBA due to the physical
movement and idling of commuter trains along the SCRRA rail fine.
I Iowever, in addition to movement and idling noise levels, trains are required to use horns at any at -grade
crossing for safety reasons. Depending on the type of horn used, noise levels could reach 110 dBA at a
distance of 100 feet. Under the Transit Zoning Code (SD 84A and SD 8413), sensitive uses, both interior
and exterior, could be located within areas that may experience excessive noise levels due to train horns.
Interior uses would include predominantly residential structures, while exterior uses at new developments
adjacent to the rail station and the SCRRA rail line may include communal open spaces, such as pocket
parks or pedestrian walkways. It is expected that these uses could be located within the interior of new
developments or on the opposite side of the development from the rail station and SCRRA tracks,
thereby mitigating some of the noise generated by those transportation facilities. In terms of interior uses
and as stated previously, under new construction practices, noise levels inside structures, such as
residential buildings, can be expected to be 30 dBA less than exterior noise levels. As such, the
instantaneous interior noise levels attributable to residential units located within 100 feet of the SCRRA
4.8-36 City of Santa Ana Transit Zoning Code (SD 84A and SD 8413) EIR
4.8 Noise
tracks would be reduced to approximately 80 dBA when a train horn blows. However, this noise level
would remain in excess of City noise standards as established in Section 18-312 and 18-313 of the
Municipal Code by approximately 15 dBA for instantaneous noise. As such, this impact would be
considered potentially significant.
Implementation of the mitigation measures provided above (MM4.8-5 and MM4.8-6) will reduce
potential noise levels at sensitive receptors associated with interior and exterior communal and private
spaces but not to levels beneath the standards set in the City's Municipal Code. In addition to the
aforementioned mitigation measures, the following mitigation measure would be implemented,
MM4.8-8 The City shall provide a written statement to each applicant for projects located within 400 feet of the
SCRRA tracks that shall be provided for each residential unit and resident, noting them of
potential noise and vibration issues associated with the railroad tracks, including the following:
Notice ofDisclosure
Each owner's [or renter's] interest is subject to the fact that trains operate at different times of the day
and night on the railway tracks immediately adjacent to a prelect site; and that by accepting the
conveyance of an interest [or lease agreement] in that project, owner for renter] accepts all impacts
generated by the trains.
Posting ofNotice ofDisclosure in each residential unit
Prior to offering the first residential unit for purchase, lease, or rent, the properly owner or developer
shall post a copy of the Notice of Disclosure in every unit in a con picuous location. Also, a copy of the
Notice of Disclosure shall be included in all materials distributed for the Preject, including but not
limited to: the prospectus, informational literature, and residential lease and rental agreements.
Although the above mitigation measure would reduce impacts, it would not serve to fully mitigate the
potential impact to nearby residents of the Transit Zoning Code (SD 84A and SD 84B). However, it
should also be noted that in accordance with the Final Rule for the Use of Locomotive Horns at
Highway -Rail Grade Crossings, as established by the FRA, local jurisdictions have the ability to prevent
trains from using their horns at at -grade crossings through the establishment of Quiet Zones. The
establishment of a Quiet Zone involves the installation of additional design features that would limit
potential vehicle and pedestrian conflicts with moving trains, including four -quadrant gates, advance
warning signs, mountable curb medians with channelization devices, programmed enforcement, photo
enforcement, and public education and awareness. The City of Santa Ana is currently pursuing the
establishment of a Quiet Zone within the City; however, until such time, the use of a train horns would
be considered to have a significant and unavoidable impact on sensitive receptors developed as part of
the Transit Zoning Code (SD 84A and SD 8413).
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.8.37
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
Threshold Would the project result in the exposure of persons to or generation of excessive
groundborne vibration or groundborne noise levels?
Impact 4.8-9 Construction activities associated with the proposed project could generate
or expose persons or structures to excessive groundborne vibration. While
implementation of mitigation measures MM4.8-1 through MM4.8-4 would
minimize this impact, it would not reduce it to a less -than -significant level.
This is considered a significant and unavoidable impact.
Although construction -related vibration associated with individual development projects constructed
pursuant to the Transit Zoning Code would be temporary there are two potential impacts that could
occur. First, vibration at high enough levels can result in human annoyance. Second, groundborne
vibration can potentially damage the foundations and exteriors of historic structures. Groundbome
vibration that can cause this kind of damage is typically limited to impact equipment, especially pile
drivers. Construction activities that would occur pursuant to the Transit Zoning Code have the potential
to generate low levels of groundborne vibration. Table 4.8-13 (Vibration Source Levels for Construction
Equipment) identifies various vibration velocity levels for the types of construction equipment that
would operate within the City during construction.
Table-
Equipment
Approxmmote VdB
25 Feet
50 Feet
75 Feet
100 Feet
Large Bulldozer
87
81
77
75
Loaded Trucks
86
80
76
74
Jackhammer
79
73
69
67
Small Bulldozer
58
52
48
46
SOURCE: Federal Railroad Administration 1998
In addition to the construction equipment shown in Table 4.8-13 (Vibration Source Levels for
Construction Equipment), vibration that would be experienced from the use of impact pile drivers could
reach as high as 112 VdB at a distance of 25 feet (HMMH 2O06). Like noise, groundbome vibration will
attenuate at a rate of approximately 6 VdB per doubling of distance. The groundborne vibration
generated during construction activities would primarily impact existing sensitive uses (e.g., residences,
schools, and hospitals) that are located adjacent to, or within, the vicinity of specific projects. These
sensitive uses could sometimes be located as close as 25 feet to the construction site or as far as several
hundred feet away. Based on the information presented in Table 4.8-13, vibration levels could reach up
to 87 VdB at sensitive uses located within 25 feet of construction. For sensitive uses that are located at or
within 25 feet of potential project construction sites, sensitive receptors (e.g., residents, school children,
and hospital patients) at these locations may experience vibration levels during construction activities that
exceed the FTA's vibration impact threshold of 85 VdB for human annoyance. So long as construction
occurs more than 50 feet from sensitive receptors, the impact associated with groundborne vibration
generated by the equipment would be below 85 VdB and thus would be less than significant. However,
as specific site plans or constructions schedules for projects requiring impact pile drives are unknown at
4.838 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Nolse
this time, it may be possible that construction activities could occur as close as 25 feet from sensitive
receptors. This would result in these sensitive receptors experiencing vibration impacts above the
threshold of 85 VdB, in which case this impact would be potentially significant. Implementation of
mitigation measures MM4.8-1 through MM4.8-4 would help to reduce this impact, but not to a less -than -
significant level; therefore, this impact would remain significant and unavoidahle.
4.8.4 Cumulative Impacts
The geographic context for the analysis of cumulative noise impacts depends on the impact being
analyzed. For construction impacts, only the immediate area around the project site would be included in
the cumulative context. For operational/roadway related impacts, the context is existing and future
development in the City of Santa Ana. This cumulative impact analysis considers development of the
proposed project, in conjunction with ambient growth and other development within the vicinity of the
proposed project in the City of Santa Ana. Noise is by definition a localized phenomenon, and
significantly reduces in magnitude as distance from the source increases. The analysis accounts for all
anticipated cumulative growth within this geographic area, as represented by full implementation of the
City of Santa Ana General Plan Framework and development of the related projects provided in
'Table 3-3 in Chapter 3.0 (Project Description).
Increases in noise at sensitive uses would occur as a result of construction of individual projects pursuant
to the Transit Zoning Code the proposed project, along with other construction in the vicinity. Other
construction that may occur in the vicinity of the Transit Zoning Code area would contribute noise levels
similar to those generated by individual development projects. Where this development adjoins a
proposed project's construction, the combined construction noise levels would have a cumulative effect
on nearby sensitive uses. Noise is not strictly additive, and a doubling of noise sources would not cause a
doubling of noise levels; however, cumulative construction noise levels would be in excess of 65 dBA
CNEL at nearby sensitive receptors.
As discussed under Impact 4.8-1, Section 18-314(e) of the City Municipal Code limits construction
activities to between the hours of 7:00 A.M. and 8:00 P.M. Monday through Saturday, and also prohibits
construction activities on Sundays and public holidays. Because compliance with this construction time
limit is required by the City Municipal Code, the proposed project and all other cumulative development
would be exempt, and the cumulative impact associated with construction noise in the Santa Ana area
would be considered less than significant. Similarly, because construction -related noise generated under
the proposed project would be exempt from established noise standards, the construction of the
proposed project would not be cumulatively considerable and the cumulative impact of the project
would also be less than significant
Other development projects within the City of Santa Ana could potentially introduce residential
development into areas that currently exceed the 60 dBA CNEL standard for residential uses. However,
such residential development would have to be constructed so that noise levels within exterior living
spaces do not exceed the 65 dBA CNEL standard as set forth in the Noise Element of the General Plan.
Since any potential new residential development within the City would be required to mitigate through
site and building design, insulation and other noise preventative measures, the proposed project's impact
City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4.839
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
would not be cumulatively considerable and the cumulative impact of the project would also be less
than significant
As discussed under Impact 4.8-2, all rooftop HVAC equipment would be shielded; therefore, no source
would generate maximum noise levels of greater than 57 dBA Leg at 50 feet. Consequently, multiple units
would have to be located within 50 feet of a receptor to achieve noise levels that would exceed the City
standards. The development types associated with the proposed project and other nearby projects are not
so dense that multiple stationary units would be so closely spaced, either on -site or off -site.
Consequently, the cumulative effect of multiple HVAC units and other mechanical equipment would be
less than significant and the contribution of the project would not be cumulatively considerable. This
would be a less than signiitcantimpact.
As discussed in Impact 4.8-9, the construction of individual projects pursuant to the Transit Zoning
Code would produce temporary vibration impacts. However, as discussed in Impact 4.8-9, the
construction vibration impact would be significant and unavoidable. Cumulative development in the City
of Santa Ana is not considered likely to result in the exposure of on -site or off -site receptors to excessive
groundborne vibration due to the localized nature of vibration impacts, the fact that all construction
would not occur at the same time and at the same location, and the largely built -out nature of the City,
which would usually preclude the use of heavy equipment such as bulldozers. Other projects listed in
Table 3-3 in Chapter 3.0 (Project Description) are proposed in close enough proximity to affect the same
receptors as the proposed project. Only receptors located in close proximity to each construction site
would be potentially affected by each activity. Construction activities associated with these projects,
which are adjacent to or within, the Transit Zoning Code (SD 84A and SD 8413) area, may overlap with
construction activities for other projects for some amount of time. Sensitive uses in the immediate
vicinity of the Transit Zoning Code (SD 84A and SD 8413) area may be exposed to two sources of
groundborne vibration. However, for the combined vibration impact from the two projects to reach
cumulatively significant levels, intense construction from both projects would have to occur
simultaneously within 50 feet of any receptor. As individual development projects under the Transit
Zoning Code (SD 84A and SD 84B) area may be constructed concurrently with each other or other
related projects, it is possible that intense construction from two or more projects would simultaneously
occur at distances of 50 feet or less from existing nearby receptors. Therefore, vibration from future
development could potentially combine with construction vibration of other projects to result in a
potentially significant cumulative impact. Nlitigation measures MM4.8-1 through MM4.84 would help
reduce this impact, but not to a less than significant level. Therefore, the cumulative impact of the
proposed project would be significant and unavoidable.
Groundbome vibration could conceivably be generated by operation of projects in the vicinity of the
Transit Zoning Code (SD 84A and SD 8413) area. Since no substantial sources of groundborne vibration
would be built as part of the proposed project, no vibration impacts would occur during operation of the
proposed project. The same is expected to hold true for other projects in the vicinity of the Transit
Zoning Code (SD 84A and SD 8413) area. Consequently, there would be no cumulative operational
groundborne vibration impacts to any on -site or off -site receptor. This impact would be less than
significant.
4.8-40 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 NO/Se
The proposed project and two related projects with residential components identified in Table 3-3 in
Chapter 3.0 (Project Description) are located within close proximity to the AT&SF rail line. Problems for
residential uses, such as disturbance due to groundborne vibration from these sources, are usually
contained to areas within about 200 feet of the vibration source (HMMH 2O06). Typically, the main
effect of groundborne vibration is to cause annoyances for occupants of nearby buildings. The effect of
vibration at each related project site is site specific and is dependent on existing localized conditions.
However, as none of the related projects are located within 100 feet of the railroad right of way, impacts
associated with vibration from the tracks are expected to be less than significant. As discussed in
Impact 4.8-4, the occupants of the proposed residential units within the Transit Zoning Code (SD 84A
and SD 8413) area would not be exposed to potentially significant vibration levels. Therefore, this impact
would be less than significant.
As discussed in Impact 4.8-7, noise impacts as the result of increased traffic on local roadways was
analyzed both for near -term project plan completion (2030) and long range (2035) conditions. The near -
term (2030) analysis included both ambient growth and development of the related projects provided in
Table 3-3 in Chapter 3.0 (Project Description). The long range (2035) analysis included data obtained
from the OCTAM 3.2 travel demand forecasting model which utilizes the latest adopted demographic
forecasts for the City. As a result both the near -term (2030) analysis and the long range (2035) analysis
are cumulative in nature.
As discussed above, cumulative traffic would not result in substantial increases in noise along any
roadway segments under either near -term (2030) or long-range (2035) conditions. Roadway noise under
either scenarios with the project would not increase roadway noise levels above the 3.0 dBA CNEL
significance threshold in areas where existing noise levels meet or exceed the 65 dBA CNEL standard for
sensitive uses, or above the 5.0 dBA CNEL significance threshold in areas where existing noise levels are
below the 65 dBA CNEL standard. Likewise, the contribution of the proposed project to this increase
under both scenarios would not exceed 3.0 dBA or 5.0 dBA CNEL. As a result, the contribution of the
proposed project to future roadway noise levels would not exceed the identified thresholds of
significance and, therefore, would not be considered cumulatively considerable and the cumulative
impact would be less than significant.
The proposed project and two related projects with residential components are located within close
proximity to the AT&SF rail line. Sensitive receptors, including residential uses with exterior uses such as
communal areas consisting of pocket parks or pedestrian walkways and private balconies, may or may
not be shielded from noise generated by railroad operations. As a result, noise levels within these areas
may exceed the 65 dBA CNEL "Desirable Maximum" standard, and this would be considered a
significant and unavoidable cumulative impact. Mitigation measures MM4.8-5, MM4.8-6, and
MM4.8-8 would reduce noise levels at these receptors but not to a less -than -significant level.
Periodic and temporary noise levels would be generated by construction of individual projects along with
other construction in the vicinity. As discussed in Impact 4.8-1, these projects by themselves would
expose some receptors to noise levels in excess of acceptable City standards. Construction noise impacts
are localized in nature and decrease substantially with distance. Consequently, in order to achieve a
substantial cumulative increase in construction noise levels, more than one source emitting high levels of
City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4.8-41
Chapter 4 Environmental Setting, Impacts, and Mitigation Measures
construction noise would need to be in close proximity to a sensitive receptor. As discussed previously,
related projects provided in Table 3-3 in Chapter 3.0 (Project Description) are in the vicinity of the
Transit Zoning Code area. Construction activity associated with these projects may overlap with
construction activity for the proposed project. Thus, the possibility exists that a substantial cumulative
increase in construction noise levels could result from construction associated with the projects in the
Transit Zoning Code area and related projects. The cumulative impact concerning these projects and the
related projects, concurrently emitting high levels of construction noise, would likely be significant and
unavoidable. As discussed previously, the City exempts construction noise from the provisions of the
Municipal Code as long as construction occurs within certain hours of the day. All of the projects
analyzed in the cumulative context that would construct concurrently with the individual projects within
the plan area would be required to comply with the same provisions of the Municipal Code described
above. Consequently, all projects analyzed in the cumulative context would fall under the Municipal
Code exemption, and the cumulative impact of the proposed project would be less than significant
Operation of the projects constructed in the Transit Zoning Code area would not include special events
or temporary activities which would cause an increase in ambient noise levels. Therefore, there would be
no temporary or periodic noise impacts to on- or off -site receptors due to operation of the proposed
project, and the cumulative impact of the proposed project would be less than significant.
4.8.5 References
Harris Miller Miller & Hanson Inc. 2006. Transit Noise and Vibration Impact Assessment, Final Report, May.
Hendriks, R. 1998. Technical Noise Supplement: A Technical Supplement to the Traffic Noise Analysis
Protocol. California Department of Transportation (Caltrans), Sacramento, California. October.
Katz, Okitsu & Associates. December 2006, Traffic Impact Study for the Mixed Use Specfc Plan Area in the
City of Santa Ana.
KOA Corporation. January 2010. Santa Ana Renaissance Speck Plan Traffic Study.
Redden, John P. September 2005. Is train horn noise a problem inyour toum? American Public Works
Association website (http://www,apwa.net/Publications/Reporter/ReporterOnHne/
index.asp?DISPLAY=ISSUE&ISSUE_DATE=092005&ARTICLE_NUMBER=1129). Accessed
on January 12, 2008.
Santa Ana, City of. 1982. City of Santa Ana General Plan Noise Element, 1982.
United States Department of Transportation. Federal Highway Administration, 1980a. Highway Noise
Fundamentals.
. Federal Highway Administration. 1980b. Fundamentals and Abatement of Iighway Traffic
Noises. September.
Federal Highway Administration. 1980c. Highway Noise Mitigation.
Federal Highway Administration. Traffic Noise Prediction Model (FHWA-RD-77-108).
Federal Railroad Administration. 1998. High -Speed Ground Transportation Noise and
Vibration Impact Assessment,
4.8-42 City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR
4.8 Nolse
United States Envitonmental Protection Agency. 1971. Noise from Construction Equipment and
Operations, Building Equipment and Home Appliances.
City of Santa Ana Transit Zoning Code (SD 84A and SD 84B) EIR 4.8-48
Santa Ana City Council 9/25/2019
22 Civic Center Plaza
Santa Ana CA, 92701
RE: Russell Fischer Project
325/ 301 N Tustin Ave
Santa Ana CA, 92705
Dear Kristine Ridge,
The intent of this letter is to provide all factual data regarding our pending project to assist Santa Ana City
Council in making the correct decision.
Our Santa Ana location was purchased in September of 2015. Immediately after our purchase, we began
all necessary steps to upgrade the existing location. Over four years later, we have spent hundreds of
thousands of dollars, followed all city requirements and guidelines, and have been approved unanimously
by the planning commission.
After four years of work and following all city's requirements, we have had no valid opposition. The only
opposition that has come forward is an existing competitor (purchased their business in 2017) that
aggressively attempts to hurt our company financially and stop our project from happening with the
argument that the market is "overly saturated."
There are a total of six operating express car washes in the city of Santa Ana, including our existing
location. There are over 30 coffee shops, over 20 dry cleaners, over 40 auto repair shops, over 30 oil
change centers, over 50 fast food restaurants in the city of Santa Ana. Are we to believe that once a
business is established, they are to expect no future competition? Or even worse, that an existing
business will be unable to enhance their business after following all city requirements because existing
competition doesn't support it? The aforementioned would state otherwise. This is quite the precedent to
even consider entertaining for existing or new businesses, no matter what the industry.
We understand there is no way around the appeal process set forth by the City and that the appeal
process is necessary. However, the company who filed the appeal did so at the 11th hour of the last day
of the appeal process in order to inflict the maximum amount of financial loss to our company. Not only
did they do so with malicious intent, but they also executed this exact same plan to a previously pending
car wash project, (furniture store on 17th and Maybury) which was ultimately approved. Our competitor's
egregiously selfish nature and use of government process to inflict financial harm on others without any
remorse is appalling.
Our business on 325/301 N Tustin Ave has been a fuel station and car wash since the 1970's. Through
great cost and effort we jumped through all the required hoops to clean up a dilapidated restaurant site
and to enhance an existing business to maximize what can be offered to the community of Santa Ana.
Sincerely,
Chase Russell
301/325 N Tustin Project
Summary
Russell Fischer partnership purchased both sites in September of 2015
Car Wash and Fuel station have been on location since 1973
Goal has been to enhance existing business to provide a better product for the community of
Santa Ana
- Russell Fischer is a small family business run by Chase Russell (after the death of his Father) for
his Mother, Jeanie Russell
- Immediately after purchase, Russell Fischer started the process with the city to commence
improvements on the site
- After purchase of the site, the dilapidated and crime ridden restaurant has been demolished,
crime and vagrants on the corner have been drastically reduced, and site has been cleaned to
highest potential
- January 4, 2019 zone change and general plan amendment (C2) became effective
- September 9, 2019 planning commission unanimously approved CUP, environmental review, and
to facilitate the construction of a new convenience store and new automated car wash. Project
supported by staff
September 19, 2019 Speedie Clean Car Wash (1.2 Miles away from project site) filed appeal.
Staff disagrees with appeal and continues to support car wash project
Opposition
Dental office to the South of our project has voiced concerns regarding vibration of the car wash.
With a car wash or fuel station, there is no vibration. We have it in our plans to overbuild with
concrete block construction, while also having three sound studies to meet city requirements to
ensure no increase in noise on site. We have worked with the dental office, given them an
additional 12" of our land for additional sound buffer and confirmed that our quality construction
will ensure no additional noise.
Speedie Clean Car Wash, Conklin family, (purchased in 2017 for $8,040,000) stating that the city
of Santa Ana cannot support an enhanced car wash that this will hurt them financially. They have
filed this appeal to ensure their $8,040,000 investment does not see any upgraded competition,
even though our car wash has been on site since 1973, Speedie Clean went through this same
appeal process with project at 17th and Maybury, which was ultimately approved
We are a small family business that has followed all city requirements and battled this process at a large
financial loss over a four year period to enhance our business and provide a better service for the
community. The corner will be beautified, over 20 jobs will be added, and taxable income for the city will
be over three times what it is today. A selfish competitor costing us a fortune and taking up the city's
valuable time should never be allowed to stand in the way of improving the City of Santa Ana. What
possible benefit could there be to reconsider the planning commission's decision? We urge you to not
grant this continuance and to push the project forward so we and the City of Santa Ana can move
forward, together.
Sincerely,
Chase Russell
October 15, 2019
Santa Ana City Council
20 Civic Center Plaza
Santa Ana, CA 92701
RE: Moratorium on Car Washes
Dear City Councilmembers
I would like to ask you to adopt a moratorium on new car washes in the City of Santa Ana
in order to develop standards that will limit their negative impact on our residents.
Currently, there are at least 22 existing car washes in Santa Ana. In Santa Ana's 27
square miles, that is about one car wash per 1.2 square miles. In neighboring Anaheim,
there are at least 16 existing car washes within its 50 square miles, which is about one
car wash for every 3.1 square miles.
There are more car washes in Santa Ana than the total locations for McDonald's, Taco
Bell, and Burger King in Santa Ana, and the amount of those fast food establishments in
Santa Ana feels overwhelming.
The environmental impacts of car washes, such as the harmful chemicals contained in
the soap, which becomes mixed with the dirt and grease removed from the cars, ends up
contaminating the soil underneath the car washes and our City's underground water
supply, which affects our drinking water. I want Santa Ana to continue to make the news
for winning awards for having the best -tasting water, not the most contaminated water.
Twenty-two is a significant amount of locations for a use that provides our City little
economic benefit since there are minimal sales tax revenues generated from car washes.
The locations of many of these car washes result in the loss of some of the more desirable
commercial sites throughout the City.
Multiple cities in San Diego County and the Inland Empire have recognized the impacts
of having too many car washes and have passed moratoriums to develop standards that
limit their negative impacts. I hope that Santa Ana will do the same.
Sincerely,
Phil Bacerra
Mitre -Ramirez, Norma
From: Kara Grant <
Sent: Tuesday, October 15, 2019 1:28 PM
To: eComment
Cc: Kelaher, Selena
Subject: City Council Meeting 10/15 - Comments
Attachments: RK - Noise Peer Review - 101519.pdf
Attached hereto are written comments submitted for the hearing on Appeal Application No. 2019-03 before the City
Council tonight, 10/15.
Thank you,
Kara Grant
ICARA E. GRANT
Attorney at Law
This communication, including any attachments, may contain confidential and/or proprietary information (and, in some cases
information protected by either or both doctrines of attorney -client privilege and attorney work -product), and is intended only
for the individual(s) or entity or entities to whom the communication is addressed. Any review, dissemination, or copying of
this email by anyone other than the intended recipient(s) is strictly prohibited. If you are not an intended recipient, please
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S
engineering
group, inc.
October 15, 2019
Ms. Kara E. Grant
Law Office of Kara E. Grant
17595 Harvard Suite C-202
Irvine, CA 92614
traffic engineering & design
transportation planning
parking
acoustical engineering
au quality & ghg
Subject: 301 and 325 North Tustin Avenue Noise Impact Analysis Review, City
of Santa Ana
Dear Ms. Grant:
Introduction
RK ENGINEERING GROUP, INC. (RK) is pleased to provide this review of potential
environmental noise and vibration impacts from the construction and operation of a
proposed express car wash and gas station with convenience market located at 301 and
325 North Tustin Avenue, in the City of Santa Ana (hereinafter referred to as project). This
review is based on the information provided in 301 and 325 Tustin Avenue Noise Impact
Analysis, prepared by LSA, July 2019 (hereinafter referred to as Noise Study).
The purpose of this letter is to review the Noise Study from a noise and vibration impact
standpoint and provide comments to help ensure that all potential impacts from the
project are adequately identified and the effects mitigated to the maximum extent feasible.
RK has over 50 years of combined experience in environmental acoustics and has prepared
hundreds of noise impact analyses for public agencies and developers in the State of
California, and we are fully aware of the complexity of data gathering, modeling, and the
possibility for error within these technical documents.
Comments
Based upon our review, the following comments are provided:
1. Page 19, Car Wash Operations. The noise level data utilized to predict future noise
levels from the car wash tunnel seems low. RK has collected similar noise level data
4000 westerly place, ste. 280
newport beach, ca 92660
0(949) 474-0809
0 rkengineeccont
Law Office of Kara E. Grant
RK 15591
Page 2
for express car wash sites and has recorded noise levels above 90 dBA Leq and 100
dBA Lmax at the exit of the tunnel, near the blowers. Attachment A shows the
manufacture's noise level readings for a Ryko Solutions 3-Fan SlimLine Dryer system
installed in a car wash tunnel. As can be seen in the attachment, noise levels of
approximately 90 decibels were recorded at 10 feet from the exit of the tunnel. This
is significantly louder than the referenced 81.9 dBA noise levels at 13 feet utilized in
the Noise Study. The Noise Study also utilizes noise levels of 73.7 dBA at 20 feet for
sound propagating from the tunnel exit at 90 degrees off -center. As shown in
Attachment A, noise levels at 25 feet at 90 degrees off -center are shown to be 80.5
decibels for typical equipment. This too is significantly louder than what is projected
in the Noise Study. As a result, the Noise Study may underestimate future noise level
impacts from the car wash tunnel.
2. Page 19, Car Wash Operations. The Noise Study does not discuss or analyze the
noise level impacts from the self -serve vacuums. Per RK's understanding,
approximately 20 self -serve vacuum stalls will be provided on the project site. The
Noise Study should analyze and disclose the noise level impact from all vacuum
locations, as they will be a major source of noise. For example, RK has measured
noise levels up to 90 decibels near vacuum service areas. As a result, the Noise Study
may underestimate future noise level impacts to adjacent land uses.
3. Page 19, Car Wash Operations and Table 1 Car Wash Noise Levels. The Noise Study
states, "because noise levels generated by the carwash operations would be similar
to those experienced from traffic impacts, the increase would be less than 3 dBA,
typically a threshold used to determine if the increase in noise would be
perceptible." However, upon looking at the projected car wash noise levels, shown
in Table 1, the project noise contribution would be 66.7 dBA Leq at R-6, Medical
Office. When the project noise is added to the daytime noise levels at LT-1, reported
as being 66 dBA during the 10:00 AM and 11:00 AM hours, the resulting noise
level is approximately 69.4, 3.4 decibels higher than the ambient. As stated above,
this would typically exceed the threshold of human perception and is frequently
considered a substantial permanent increase in the ambient environment; thus
triggering a significant impact under CEQA. Although the adjacent medical office
land use does contain noise sensitive exterior areas, further analysis and mitigation
should be provided to demonstrate that the project would not adversely affect the
noise sensitive interior areas of the medical office building.
®onglinnnring
group, Inc.
rkengineeccom
Law Office of Kara E. Grant
RK 15591
Page 3
4. General Comment, Construction Noise and Vibration Impacts. The Noise Study does
not address the potential temporary increase in ambient noise levels caused by
construction activity in the vicinity of the project, particularly at the noise sensitive
medical office building located immediately adjacent to the car wash tunnel.
Medical equipment, devices and procedures can be particularly susceptible to noise
and vibration, and therefore, it is important that the Noise Study identify and
disclose any potential noise a vibration impacts cause by the construction of the car
wash project.
Conclusions
Based upon this review, 301 and 325 North Tustin Avenue Noise Impact Analysis may not
adequately address all potential noise impacts from the proposed project. Additional
analysis and mitigation measures should be provided to ensure the project does not
adversely affect the surrounding noise sensitive land uses.
RK Engineering Group, Inc appreciates this opportunity to work with the Law Office of Kara
E. Grant. If you have any questions regarding our review, or need additional analysis,
please call me at (949) 474-0809.
Respectfully submitted,
RK ENGINEERING GROUP, INC.
zurtA Cu,
Bryan Estrada, AICP
Senior Associate
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Attachment A
Example of Car Wash Tunnel Sound Level Reading
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