HomeMy WebLinkAboutCDP 98-48; Carlsbad Village Resort Hotel; Redevelopment Permits (RP) (3)GEOCON
INCORPORATED
GEOTECHNICAL CONSULTANTS
Project No. 06043-42-01
April 2, 1998
Heritage West Development Company
4370 La Jolla Village Drive, Suite 655
San Diego, Califomia 92122-1252
Attention: Mr. Howard Gad
Subject: CARLSBAD HOTEL SITE
CARLSBAD BOULEVARD AND BEECH STREET
CARLSBAD, CALIFORNIA
SUMMARY OF FIELD INVESTIGATION AND EXPLORATORY DRILLING
Gentlemen:
In accordance with your request, we have performed exploratory drilling for the subject project.
This letter has been prepared at your request to summarize the field activities and general soil
conditions encountered.
The field investigation was performed on February 4, 1998, and consisted of a site reconnaissance
and the excavation of 6 small-diameter borings. The borings were excavated to depths ranging from
21 feet to 41 feet below the existing ground surface using a Ingersoll Rand A-300 Drill Rig equipped
with 8-inch-diameter hollow stem augers. Relatively undisturbed samples were obtained by driving
a 3-inch, O.D., split tube sampler into the "undisturbed" soil mass with blows from a 140-pound
hammer falling 30 inches. The sampler was equipped with 1-inch by 2 3/8-inch brass sampler rings
to facilitate removal and testing. Bulk samples were also obtained.
The soil conditions encountered in the borings were visually examined, classified and logged in
general accordance with American Society for Testing and Materials (ASTM) practice for
Description and Identification of Soils (Visual-Manual Procedure D2844). Logs of the borings are
presented on Figures A-l through A-6. The logs depict the soil and geologic conditions encountered
and the depth at which the samples were obtained.
The site is underlain by minor amounts of undocumented fill and native Terrace Deposits.
Approximately 6 feet of fill was encountered within the northeastem portion of the property.
Several small stockpiles of undocumented fill were also encountered within this area. The remains
of an old building foundation exist at this location. The undocumented fill is loose and should be
removed and/or recompacted during site development.
The remaining portion of the site is underlain by Terrace Deposits. The Terrace Deposits consisted
of medium dense to dense, reddish brown, silty, fine to medium sand within the upper 3 to 8 feet of
the soil profile, becoming a yellowish brown, fine to medium grained sand with a trace of silt at
depth. The Terrace Deposits are suitable, from a geotechnical engineering standpoint, for support of
the planned development. However, laboratory testing should be performed on selected soil samples
6960 Flanders Drive • San Diego, California 92121-2974 • Telephone (619) 558-6900 • Fax (619) 558-6159
to evaluate in situ density, shear strength, consolidation, compaction and expansion characteristics of
the prevailing soil conditions.
No soil or geologic condition was encountered that would preclude the development of the site as
presently proposed. It is the recommendation of Geocon Incorporated that laboratory testing be
performed on the samples obtained during the field investigation. It has been our experience that
samples collected from the field investigation will dry out and/or have a grater possibility of being
disturbed such that the tme engineering properties of the soils can not be determined if the samples
remain untested for a period of time.
Upon your request, and after completion of the laboratory testing, Geocon Incorporated will prepare
a written report presenting our findings and our conclusions and recommendations regarding the
geotechnical aspects of developing the property as presently proposed. The report will include
recommended grading specifications, slope stability analysis, foundation design criteria, preliminary
pavement sections, excavation characteristics and remedial grading measures (if required).
If you have questions regarding this review, or if we may be of further service, please contact the
undersigned at your convenience.
Very tmly yours,
GEOCON INCORPORATED
'James L. Brown Rodney C^^ikesell
GE2I76 RCE 55080
RCM:JLB:dmc
(4) Addressee
Project No. 06043-42-01 - 2 - April 2, 1998
PROJECT NO. 06043-42-01
DEPTH
IN
FEET
SAMPLE
NO.
SOIL
CLASS
(USCS)
BORING B 1
ELEV. (MSL.)
EQUIPMENT
DATE COMPLETED
m A-300
2/4/98
;UJ' O, H
H UJ
UJ^CQ
QC
UJ
- 0
MATERIAL DESCRIPTION
- 26
Bl-1
- 2 -
- 4
TERRACE DEPOSITS
Medium dense to dense, moist, reddish brown, Silty,
fine to medium SAND
SM
Bl-2
Medium dense, moist, Reddish brown to yellowish
brown, fme to medium SAND with trace silt 34
h 8 H
10
12
- 14 -
- 16 -
- 18
20 -
- 22 -
- 24 -
Bl-3
Bl-4
Bl-5
20
SP 27
Bl-6 -Increasing silt at 20 feet 44
Bl-7 48
BORING TERMINATED AT 26 FEET
Figure A-l Log of Boring B 1, page 1 of 1 CAH
o*x,T^TT^ f.w»,T,^T n ... SAMPLING UNSUCCESSFUL C ... STANDARD PENETRATION TEST
SAMPLE SYMBOLS
^ ... DISTURBED OR BAG SAMPLE EJ ... CHUNK SAMPLE
1... DRIVE SAMPLE (UNDISTURBED)
3E ... WATER TABLE OR SEEPAGE
NOTE: THE LOG OF SUBSURFACE CONDITIONS SHOWN HEREON APPLIES ONLY AT THE SPECIFIC BORING OR TRENCH LOCATION AND AT THE
DATE INDICATED. IT IS NOT WARRANTED TO BE REPRESENTATIVE OF SUBSURFACE CONDITIONS AT OTHER LOCATIONS AND TIMES.
PROJECT NO. 06043-42-01
DEPTH
IN
FEET
SAMPLE
NO.
> CD O _J O X
I-H _J
SOIL
CLASS
(USCS)
BORING B 2
ELEV. (MSL.)
EQUIPMENT
DATE COMPLETED
IR A-300
2/4/98
lUI'
o, o
H H-^U-
CD o
- 0
MATERIAL DESCRIPTION
- 26
2 -
- 4 -
- 6 -
8
10
- 12 -
- 14 -
- 16
- 18 H
- 20
- 22
24 H
B2-1 I
B2-2 I
B2-3 I
B2-4 I
B2-5 I
TERRACE DEPOSITS
Dense, moist, reddish brown, fine to medium SAND
with some silt, weakly cemented
SP-SM
43
Medium dense to dense, moist, reddish brown to
yellowish brown, fine to medium SAND, weakly
cemented
29
SP
32
47
44
BORING TERMINATED AT 26 FEET
Figure A-2 Log of Boring B 2, page 1 of 1 CAH
SAMPLE SYMBOLS • .. . SAMPLING UNSUCCESSFUL c. . STANDARD PENETRATION TEST 1. . DRIVE SAMPLE (UNDISTURBED) SAMPLE SYMBOLS . SAMPLING UNSUCCESSFUL
E..
. DRIVE SAMPLE (UNDISTURBED)
^ .. . DISTURBED OR BAG SAMPLE E.. . CHUNK SAMPLE I . . WATER TABLE OR SEEPAGE
NOTE: THE LOG OF SUBSURFACE CONDITIONS SHOWN HEREON APPLIES ONLY AT THE SPECIFIC BORING OR TRENCH LOCATION AND AT THE
DATE INDICATED. IT IS NOT WARRANTED TO BE REPRESENTATIVE OF SUBSURFACE CONDITIONS AT OTHER LOCATIONS AND TIMES.
PROJECT NO. 06043-42-01
DEPTH
IN
FEET
SAMPLE
NO.
> CD O _l O X
I-
H -J
SOIL
CLASS
(USCS)
BORING B 3
ELEV. (MSL.)
EQUIPMENT
DATE COMPLETED
IR A-300
2/4/98
H'
a o
- 0
MATERIAL DESCRIPTION
- 26
- 2 -
- 4 -
- 6 -
- 8 -
- 10 -
12 -
14
16
- 18 -
- 20 -
- 22 -
- 24 -
B3-1 I
B3-2
B3-3
B3-4
I
B3-5 I
B3-6
SM
TERRACE DEPOSITS
Dense, moist, reddish brown, Silty, fine to medium
SAND
Medium dense to dense, moist, reddish brown to light
yellowish brown, fine to medium SAND
33
26
SP
33
44
-Abundant black grained sand at 25 feet 49
BORING TERMINATED AT 26 FEET
Figure A-3 Log of Boring B 3, page 1 of 1 CAH
SAMPLE SYMBOLS . SAMPLING UNSUCCESSFUL C. . STANDARD PENETRATION TEST • .. . DRIVE SAMPLE (UNDISTURBED) SAMPLE SYMBOLS SAMPLE (UNDISTURBED)
. DISTURBED OR BAG SAMPLE B.. . CHUNK SAMPLE ¥ •• . WATER TABLE OR SEEPAGE
NOTE: THE LOG OF SUBSURFACE CONDITIONS SHOWN HEREON APPLIES ONLY AT THE SPECIFIC BORING OR TRENCH LOCATION AND AT THE
DATE INDICATED. IT IS NOT WARRANTED TO BE REPRESENTATIVE OF SUBSURFACE CONDITIONS AT OTHER LOCATIONS AND TIMES.
PROJECT NO. 06043-42-01
DEPTH
IN
FEET
SAMPLE
NO.
> CD O _1 O X
SOIL
CLASS
(USCS)
BORING B 4
ELEV. (MSL.)
EQUIPMENT
DATE COMPLETED
IR A-300
2/4/98
MATERIAL DESCRIPTION
- 2 -
B4-1
- 6 -
- 8 -
- 10 -
12 -
- 14 -
- 16 -
18 -
20
22 -
- 24 -
- 26 -
- 28 -
I
TERRACE DEPOSITS
Very dense, moist, reddish brown, Silty, fine to
medium SAND
SM
-Decreasing Silt at 5 feet 68
B4-2
B4-3
B4-4
I
Medium dense to dense, moist, light yellowish brown
to light reddish brown, fine to medium SAND with
trace silt, weakly cemented and cohesionless
19
I 21
SP
B4-5 1 -Increasing silt at 20 feet 44
B4-6 I 42
Figure A-4 Log of Boring B 4, page 1 of 2 CAH
SAMPLE SYMBOLS . SAMPLING UNSUCCESSFUL c . STANDARD PENETRATION TEST • .. . DRIVE SAMPLE (UNDISTURBED) SAMPLE SYMBOLS B..
SAMPLE (UNDISTURBED)
. DISTURBED OR BAG SAMPLE B.. . CHUNK SAMPLE I • . WATER TABLE OR SEEPAGE
NOTE: THE LOG OF SUBSURFACE CONDITIONS SHOWN HEREON APPLIES ONLY AT THE SPECIFIC BORING OR TRENCH LOCATION AND AT THE
DATE INDICATED. IT IS NOT WARRANTED TO BE REPRESENTATIVE OF SUBSURFACE CONDITIONS AT OTHER LOCATIONS AND TIMES.
PROJECT NO. 06043-42-01
DEPTH
IN
FEET
SAMPLE
NO.
>-CD O _J O X h-M -I
SOIL
CLASS
(USCS)
BORING B 4
ELEV. (MSL.)
EQUIPMENT
DATE COMPLETED
IR A-300
2/4/98
•UJ'
a. H
UJHO
go
Q
MATERIAL DESCRIPTION
- 30 B4-7 1 -Becomes very dense, black grained at 30 feet 61
32 -
34 -
36
38
h 40 H
B4-8 I SP -Becomes yellowish brown, fine to coarse grained at
35 feet 66
B4-9 I -Becomes wet at 40 feet 55
BORING TERMINATED AT 41 FEET
Figure A-5 Log of Boring B 4, page 2 of 2 CAH
SAMPLE SYMBOLS • .. . SAMPLING UNSUCCESSFUL c. . STANDARD PENETRATION TEST • . .. DRIVE SAMPLE (UNDISTURBED) SAMPLE SYMBOLS . SAMPLING UNSUCCESSFUL
B..
. STANDARD PENETRATION TEST SAMPLE (UNDISTURBED)
^ .. . DISTURBED OR BAG SAMPLE B.. . CHUNK SAMPLE I . .. WATER TABLE OR SEEPAGE
NOTE: THE LOG OF SUBSURFACE CONDITIONS SHOWN HEREON APPLIES ONLY AT THE SPECIFIC BORING OR TRENCH LOCATION AND AT THE
DATE INDICATED. IT IS NOT WARRANTED TO BE REPRESENTATIVE OF SUBSURFACE CONDITIONS AT OTHER LOCATIONS AND TIMES.
PROJECT NO. 06043-42-01
DEPTH
IN
FEET
SAMPLE
NO.
> CD O _1 O X
SOIL
CLASS
(USCS)
BORING B 5
ELEV. (MSL.)
EQUIPMENT
DATE COMPLETED
m A-300
2/4/98
CQ
- 0
MATERIAL DESCRIPTION
- 2 -
- 4 -
- 6 -
- 8 -
- 10 -
- 12
- 14
16
18
h 20
B5-1
B5-2
B5-3
I I
TERRACE DEPOSITS
Medium dense, very moist, reddish brown, Silty, fine
to medium SAND
SM
-Becomes moist at 5 feet 28
I
Medium dense, moist, yellowish brown to light
reddish brown, fine to medium SAND with trace silt,
weakly cemented, cohesionless
23
B5-4 I SP -Becomes dense at 15 feet 33
B5-5 I -Becomes black grained at 20 feet 39
BORING TERMINATED AT 21 FEET
Figure A-6 Log of Boring B 5, page 1 of 1 CAH
SAMPLE SYMBOLS • ... SAMPLING UNSUCCESSFUL c. . STANDARD PENETRATION TEST • .. . DRIVE SAMPLE (UNDISTURBED) SAMPLE SYMBOLS B..
SAMPLE (UNDISTURBED)
^ ... DISTURBED OR BAG SAMPLE B.. . CHUNK SAMPLE . WATER TABLE OR SEEPAGE
NOTE: THE LOG OF SUBSURFACE CONDITIONS SHOWN HEREON APPLIES ONLY AT THE SPECIFIC BORING OR TRENCH LOCATION AND AT THE
DATE INDICATED. IT IS NOT WARRANTED TO BE REPRESENTATIVE OF SUBSURFACE CONDITIONS AT OTHER LOCATIONS AND TIMES.
PROJECT NO. 06043-42-01
DEPTH
IN
FEET
SAMPLE
NO.
>-CD O _J O X
J-
SOIL
CLASS
(USCS)
BORING B 6
ELEV. (MSL.)
EQUIPMENT
DATE COMPLETED
m A-300
2/4/98
;UJ'
Si
UJ; ft Lt v>
LIJ6 QC
•o u
- 0
MATERIAL DESCRIPTION
- 2 -
- 4 -
- 6 -
8 -
- 10 -
- 12 -
- 14
- 16
- 18
- 20 -
B6-1 I
UNDOCUMENTED FILL
Loose to medium dense, very moist, reddish brown,
Silty, fine to medium SAND
SM
-Wood debris at 5 feet 20
B6-2 I
TERRACE DEPOSITS
Dense, moist, reddish brown to yellowish brown, fine
to medium SAND with trace silt
48
SP
B6-3 I
B6-4 I
46
33
BORING TERMINATED AT 21 FEET
Figure A-7 Log of Boring B 6, page 1 of 1 CAH
SAMPLE SYMBOLS • .. . SAMPLING UNSUCCESSFUL c. . STANDARD PENETRATION TEST • .. . DRIVE SAMPLE (UNDISTURBED) SAMPLE SYMBOLS . SAMPLING UNSUCCESSFUL
B..
. STANDARD PENETRATION TEST SAMPLE (UNDISTURBED)
^ .. . DISTURBED OR BAG SAMPLE B.. . CHUNK SAMPLE ¥ •• . WATER TABLE OR SEEPAGE
NOTE: THE LOG OF SUBSURFACE CONDITIONS SHOWN HEREON APPLIES ONLY AT THE SPECIFIC BORING OR TRENCH LOCATION AND AT THE
DATE INDICATED. IT IS NOT WARRANTED TO BE REPRESENTATIVE OF SUBSURFACE CONDITIONS AT OTHER LOCATIONS AND TIMES.
Feb-03-98 04:23P ^
0
p. 02
DUDEK
&ASSOCIATES
A California Corjjoration
Engineering, Planning,
Environmental Sciences and
Management Services
Corporate Office:
605 Third Street
Encinitas, California 92024
760.942.5147
Fax 760.632.0164
May 11, 1998 1645-11
Mr. Howard Gad
Heritage West Development Company
4370 La Jolla Village Drive, Suite 655
San Diego, CA 92122-1252
PROJECT: Cartsbad ViUage Resort
RE: Exterior Noise Assessment
Dear Mr. Gad:
This report contains our assessment of the noise environment at the proposed Carlsbad ViUage Resort
project located in the City of Carlsbad. In summary, the primary noise source at the site is traffic
noise from Carlsbad Boulevard. The future exterior noise level at the hotel's proposed recreation area
and patio area at the northwestern portion of the site facing Carlsbad Boulevard would exceed the
City's exterior noise criteria. To mitigate the noise impact will require the construction of a
minimum five-foot high noise barrier along the western portion of the site. In addition, an interior
noise study will be required for the hotel prior to issuance of building permits. The interior noise
study will determine the interior noise level and type of sound insulation required to mitigate the
noise impact. To meet the City's interior noise requirement, it is anticipated that air-conditioning
and/or mechanical ventilation will be required, as well as sound-rated windows in certain rooms.
1.0 BACKGROUND
Project Setting
The Carlsbad Village Resort project site is located at the southeast corner of Carlsbad Boulevard and
Beech Avenue {Figure 1). The project would develop the site with a 145-room hotel. This analysis
is based on the Site Plan dated May 5, 1998.
The primary noise source at the site is vehicular traffic along Carlsbad Boulevard. Carlsbad Boulevard
is currently constructed as a four-lane road adjacent to the site. The existing traffic volume along
Carlsbad Boulevard is approximately 18,000 average daily traffic (ADT) (Urban Systems 1998).
CITY OF OCEANSIDE
HIGHWAY^L^^
CITY OF VISTA
CITY OF
SAN MARCOS
PACIFIC
OCEAN
CITY OF ENCINITAS
Carlsbad Village Resort - Acoustical Assessment Report
Regional Map
FIGURE
Carlsbad Viltage Resort • Exterior Noise Assessment
City Noise Criteria
The City of Carlsbad has estabhshed noise guidelines in the City's adopted General Plan Noise
Element and Noise Guidehnes Manual. These guidelines identify compatible exterior noise levels for
various land use types. The City has developed a Land Use CompatibiHty for Community Noise
Environments Matrix to determine compatibiHty between noise and land uses. Four categories are
defined in this matrix and are as follows: normaUy acceptable, conditionaUy acceptable, normaUy
unacceptable and land use discouraged. The maximum normaUy acceptable exterior noise level for
hotels is a Conmiunity Noise Equivalent Level (CNEL) of 65 dB. This criteria would apply to the
proposed outdoor recreation area and patio areas at the hotel site. Noise levels of up to 75 dB are
considered conditionaUy acceptable if needed building noise insulation features are included in the
design. Interior noise levels are not to exceed a CNEL of 45 dB. Attachment 1 contains definitions
of acoustical terms used in this report. AU sound levels discussed in this report are A-weighted.
Metliodology
The noise analysis methodology in this study is based on the City's noise assessment methodology
documented in the City's Noise Guidelines Manual (City of Carlsbad, 1995). The future noise level
along Carlsbad Boulevard was determined based on an ambient noise measurement and using
Caltrans' SOUND82 Highway Traffic Noise Prediction Model (Caltrans, 1983) with CaHfornia noise
emission factors (Caltrans, 1987). The noise model is based on the Federal Highway Administration's
traffic noise prediction model (FHWA, 1978). Input used in the noise model included the buildout
traffic volume with vehicle speeds of 80 mph (i.e., the posted speed limit). The truck mix used for
the roads was 3.52 percent medium trucks and 1.24 percent heavy trucks. The traffic mix is based
on vehicle mix surveys conducted by the City (City of Carlsbad 1995). A hard site noise propagation
factor was used for the future conditions.
2.0 EXISTING CONDITIONS
Ambient Noise Monitoring
A noise measurement was conducted at the site to determine the existing noise level. The
measurement was made using a caUbrated Larson-Davis Laboratories Model 700 (S.N. 2132)
integrating sound level meter equipped with a Bruel &: Kjaer Type 4176 y2-inch pre-polarized
condenser microphone with pre-ampUfier. When equipped with this microphone, the sound level
meter meets the current American National Standards Institute standard for a Type 1 precision
sound level meter. The sound level meter was positioned at a height of approximately five feet above
the ground.
DUDEK
&ASSOCIATES 1645-11
A c.ii/.r.i-c.„.,..(.. May 11,1998
Cartsbad Village Resort • Exterior Noise Assessment
The noise measurement location is depicted as Site 1 on.Figure 2. Site 1 is approximately 55 feet from
the center Hne of Carlsbad Boulevard. Concurrent traffic counts were conducted during the noise
measurement.
The measured average noise level was 65 dB at Site 1. Tahle 1 shows the measured noise levels and
the concurrent traffic volumes.
TABLE 1
MEASURED NOISE LEVELS AND TRAFFIC VOLUMES
Site Description llllll ;|ih^i|i;;y^ •, |:Gaj;s;|| |::ivfili
1 55 feet from Center Line to Carlsbad Boulevard 4/2/98
2:10 pm to 2:30 pm
65 dB 323 11 3
Notes: ' Equivalent Continuous Sound Level (Time-Average Sound Level)
^ Medium Trucks
3 Heavy Trucks
General Notes: Temperature 65 degrees, light westerly wind.
Traffic Noise Modeling
The existing CNEL was calculated for the traffic noise measurement location based on the current
traffic volume along Carlsbad Boulevard using Caltrans' SOUND32 noise model. To verify the input
used in the noise model, the same traffic volume and vehicle composition ratios counted during the
noise measurement were used. The modeled value was within one dB of the measured noise level
which confirms the assumptions used in the noise model.
The CNEL at the measurement sites was calculated by adjusting the traffic volume and truck
percentage to a set of normaHzed conditions (i.e., the City traffic mix and existing ADT). The
existing traffic noise level at Site 1 is calculated to be 67 dB CNEL.
DUDEK
^ASSOCIATES 1645-11
.« C.tti,r,i, C.rp.r.ll.. May 11, 1998
.•• UJ . ••• > ' <
/ O
/' Hi
CO
! i i., ^
BASE TOPO/GRADING
1- >
8
r >.•) 1; 4 / ft
•vtOTiCniiKM •a
IB]
SOURCE: Dudek & Associates, Inc.. May 1998 Scale fn Feet
Carlsbad Village Resort - Acoustical Assessment Report
Noise IVIeasurement Location
FIGURE
Carlsbad Village Resort • Exterior Noise Assessment
3.0 FUTURE CONDITIONS
Carlsbad Boulevard would be the primary traffic noise source in the future. To determine the
maximum noise level that could be experienced on-site, buildout traffic volumes were used. The
buildout traffic volume along Carlsbad Boulevard adjacent to the project site would be approximately
26,000 ADT (Urban Systems 1998).
Exterior Noise Level
The proposed hotel would be exposed to a future traffic noise level greater than 65 dB CNEL. At the
proposed hotel facade facing Carlsbad Boulevard, the CNEL would reach up to approximately 68 dB.
The outdoor recreation area and patio areas at the northwestern portion of the site facing Carlsbad
Boulevard would similarly be exposed to a noise level of approximately 68 dB. This noise level would
exceed the City's exterior noise criteria by three dB.
Interior Noise Level
The City requires that interior noise levels not exceed a CNEL of 45 dB. TypicaUy, with the windows
open, building sheUs provide approximately 15 dB of noise reduction. Therefore, hotel rooms exposed
to an exterior CNEL greater than 60 dB could result in an interior CNEL greater than 45 dB. The
noise level at the rooms facing Carlsbad Boulevard would exceed an exterior noise level of 60 dB due
to traffic noise along Carlsbad Boulevard.
Project Generated Noise Impacts
Vehicles within the proposed parking lot located along the southeastern property boundary of the
site would generate noise at the adjacent residences. A maximum of approximately 65 vehicle trips
would be generated during the p.m. peak hour (Urban Systems, 1998). Based on methodology
developed by the Federal Transit Administration for parking lot noise, the peak one-hour noise level
would be approximately 54 dB at the adjacent eastern property boundary (FTA 1995). The City has
not adopted a noise ordinance that would estabUsh quantitative limits for general nuisance noise
generated on private property. The appHcant proposes to construct an approximate six-foot high
masonry waU along the eastern property boundary. The proposed waU would reduce the peak hour
parking lot noise to less than 50 dB. This noise level would result in a less than significant noise
impact.
4.0 MITIGATION
Exterior Noise
Mitigation of the noise impacts at the outdoor recreation and patio areas would require the
construction of a minimum five-foot high noise barrier along the western portion of the site. The
location of the proposed five-foot high noise barrier is shown in Figure 3.
DUDEK
&ASSOCIATES 1645-11
A c.iii.niii c.ri>.r.ii» May 11,1998
>
<„
. • o
LU
LU Dp
ii /
i
••\^A* .":•>«.: / --y^—L-iy —
BASE TOPO/(»ADING{ SCXJRCE: Dudek ft Associates. Inc.. May 1998 Scale In Feet
Carlsbad Village Resort - Acoustical Assessment Report
Noise Barrier Locations and Heights
FIGURE
Cartsbad Village Resort • Exterior Noise Assessment
The noise barrier may be constructed as a waU, berm, or combination of both. The materials used
to construct the noise barrier are required to have a minimum surface density of 3.5 pounds per
square foot. Such materials may consist of masonry, 5/8-inch Plexiglas, 8/8-inch tempered glass, or
a combination of these materials. The barrier must be designed and constructed so that there are no
openings or cracks.
Interior Noise
To comply with the City's interior noise standard, an interior noise analysis wiU be required for the
project. The interior acoustical analysis wiU be required for the hotel prior to issuance of building
permits to ensure that interior noise levels would not exceed a CNEL of 45 dB within the hotel
rooms. To mitigate the interior noise impact, the hotel rooms would require air-conditioning and/or
mechanical ventilation, and could require sound-rated windows in certain rooms.
This concludes our noise assessment. If you have any questions, please caU me.
Very truly yours,
DUDEK &ASSOCL\TES, INC.
Mike Komula
Acoustician
REFERENCES
California Department ofTransportation (Caltrans), June 1983, User's Instructions for SOUND52 (FHWA/CA-83/06).
California Department of Transportation (Caltrans), 1987, CaUfornia Vehicle Noise Emission Levels, (FHWA/CA/TL-87/03).
Carlsbad, City of, September 1995, City of Carlsbad Noise Guidelines Manual.
Federal Highway Administration (FHWA), 1978. FHWA Highway Traffic Noise Prediction Modet (FHWA-RD-77-^08).
Federal Transit Administration (FTA), April 1995. Transit Noise and Vibration Impact Assessment.
Urban Systems Associates, Inc., April 27, 1998. Carlsbad Boulevard Hotel.
DUDEK
&ASSOCIATES 1645-11
A c.Hi.r.i. cp.r.H.. May 11,1998
Carlsbad Village Resort • Exterior Noise Assessment
ATTACHMENT 1
DEFINITIONS
Term Definition
Ambient Noise Level
A-Weighted Sound Level
The composite of noise from all sources near and far.
The normal or existing level of environmental noise at
a given location.
The sound pressure level in decibels as measured on a
sound level meter using the A-weighted filter
network. The A-weighting filter de-emphasizes the
very low and very high frequency components of the
sound in a manner similar to the frequency response
of the human ear and correlates weU with subjective
reactions to noise.
Community Noise Equivalent Level, CNEL
Decibel. dB
Time-Average Sound Level
(Equivalent Continuous Sound Level) L^^
Maximum A-weighted Sound Level,
Sound Transmission Class, STC
CNELis the A-weighted equivalent continuous)sound
exposure level for a 24-hour period with a ten dB
adjustment added to sound levels occurring during
nighttime hours (10 pm to 7 am) and a five dB
adjustment added to the sound levels occurring during
the evening hours (7pm to 10 pm).
A unit for measuring sound pressure level and is equal
to 10 times the logarithm to the base 10 of the ratio of
the measured sound pressure squared to a reference
pressure, which is 20 micropascals.
The sound level corresponding to a steady state sound
level containing the same total energy as a varying
signal over a given sample period. L^^ is designed to
average all of the loud and quiet sound levels occurring
over a time period.
The greatest sound level measured on a sound level
(L^jJ meter during a designated time interval or event
using fast time-averaging and A-weighting.
A single number rating of the noise reduction of a
building element.
DUDEK
&ASSOCIATES 1645-11
A Cl*,.,.,. c.r,«.M.. May 11,1998
Cartsbad Village Resort • Exterior Noise Assessment
ATTACHMENT 2
NOISE MODELING INPUT AND TRAFFIC DATA
Parameter Fatio Area Pool Area
ADT 26,000 26,000
Speed (mph) 30 30
MT% 3.52 3.52
HT% 1.24 1.24
Number of Lanes 4 4
Angle of View (degrees) - 90/90 - 90/90
Center Line to Barrier (ft) 75 75
Barrier to Receiver (ft) 5 5
Road Elevation (ft. amsl) 57 60
Receiver Elevation (ft. amsl) 59 60
Barrier Elevation (ft. amsl) 59 60
Receiver Height (ft) 5 5
Barrier Height (ft) 5 5
CNEL (dB) 63 63
DUDEK
&ASSOCIATES 1645-11
c.iii.,.i. c.r,.r.,i.. May 11, 1998
URBAN SYSTEM^SSOCIATESy INC
PLANNINO t, TMFFIC ENGiNea^fi MARKETING «S PROJECT SUPPORT
CONSULTAffTS TO tNDUSTRY AND GOVERNMENT
TO; Howard Gad, President
COMPANY:^ Heritage West Development Co.
FROM: ^\ / Sam P. Kab, II, Senior Traffic Engineer
DATE: April 27, 1998 TIME : 11:56 AM
SUBJECT: CARLSBAD BOULEVARD HOTEL
APR 2 7 1998
plione: ^ fax: ^
(619)458-1141 (619)458-0041
TOTAL PAGES: 2 -f 10 PBgeS of
Attachments
TRANSMTTTED VIA: Messenger
As you requested, Urban Systems Associates, Inc. is providing the following
descnption of traffic characteristics related to the 145 room Carlsbad Hotel
project.
Based on our evaluation of existing, project plus existing, and buildout traffic
conditions, it can be concluded that the hotel project would result in no
significant traffic impacts and that no traffic mitigation is needed to
maintain the City ofCarlsbad Growth Management Program level of service
performance standard for the adjacent street segments and intersections.
Provided below are descriptions ofthe attachments and a discussion of our
traffic evaluation.
EXISTING CONDITIONS
Attachment 1 shows existing AM and PM peak hour volumes atthe adjacent
intersections and the average daily traffic volumes on the adjacent street
segments.
PROIECT ONLY TRIP GENERATION
Attachment 2 shows the project site plan.
Attachment 3 shows the expected vehicle trip generation from the 145 unit
hotel project and the directional distribution to the adjacent street system.
003897 C:\@fORMS\cbh/disk
4540 KEARNY VILLA ROAD, SUTTE 106 • SAN DIEGO, CA 92123-1573 • (619) 560-4911 • FAX (619) 560-9734
Howard Gad A Wlan Systems Associates, Inc.
April 27, 1998
PROIECT PLUS EXISTING CONDmONS
Attachment 4 shows the project traffic added to existing peak hour and daily
traffic volumes.
BUILDOUT TRAFFIC CONDITIONS
Attachment 5 shows buildout peak hour and daily traffic volumes, including
project traffic. These buildout volumes were derived fi^om the City of
Carlsbad traffic model, an appendix to the City ofCarlsbad 1994 Master EIR.
SUMMARY
Attachment 6 shows a tabulation of intersection and street segment levels
of service for existing conditions, project plus existing conditions, and
buildout conditions. As shown intersection and street segment levels of
service are at "D" or better, which is within the City of Carlsbad's Growth
Management Program circulation performance standards.
Attachment 7 includes intersection levels of service worksheets.
Based on the levels of service calculated, it can be concluded that no
intersection or street improvements are needed and that no significant
traffic impacts are expected fr-om this project.
003897 2 C:\@FORMS\cbh/disk
r ATTACHMENT 1
EXISTING AM / PM PEAK HOUR
AND AVERAGE DAILY TRAFFIC (ADT)
o
V 1 V
^10/5
-^0/0
^0//
5//0-^
15//O-^ i
Oak Avenue
UEGEND
XXXy.YXY - AM/PM Peak Hour Traffio VolunM
XXX " Average Daily Traffic (ADT)
TO « o u
<
NO SCALE
Aprs. 1998
CD-C CBH-Alchwg
CA//LSBAD BOaLBVAm /¥07EL
- URBAN SYSTEMS— OOOffffS
r ATTACHMENT 2
PROJECT SITE PLAN
SOURCE
Saiemc/Uvingston Architects
Apri. 189a
CD-C CBH-A2.c(Jr/dwg
CAfiLSBAD BOULSyAflD HOTEL
- URBAN SYSTEMS— 000998
^ ATTACHMENT 3
PROJECT ONLY TRAFFIC
AND DIRECTIONAL DISTRIBUTION PERCENTAGES
AM PM
Uaa Rate 1 ADT in Out in Out
145 Rooms I0/Room|l .450 52 35
•
70 46
LEGEND
STOP SIGN
EXISTI^4G SIGNAL LOCATION
PROJECT AREA
AVERAGE DAILY TRAFFIC XXX
XX% • DIRECTIONAL DISTRIBUTION PERCENTAGES
XXXJXXX • AM/PM PEAK HOUR TRAFFIC
NO SCALE
April 1998
CD-C CBH-A3.dwg
CA/HSBAD BOULEVABD HOTEL
- URBAN SYSTEMS —
000998
r ATTACHMENT 4
PROJECT PLUS EXISTING AM / PM PEAK HOUR
AND AVERAGE DAILY TRAFFIC (ADT)
LEGEND
xxx AM/PM Peaic Hour Traffic Voiumea
Average Daily Traffic Voiumea NO SCALE
April. 1998
CD-C CBH-A4.dwg
CAHLSBAD BOULEVAHD HOTEL
- URBAN SYSTEMS — 000998
ATTACHMENT 5
BUILDOUT WITH HOTEL PROJECT AM / PM PEAK HOUR
AND AVERAGE DAILY TRAFFIC (ADT)
25.000
10//5-^
10//0—•
30/20-y
Carlsbad Village Drive
V.15/20 1D//0 ^25130 800
Beech Avenue
1.000
26.000
Grand Avenue
O 00 lO
K-20/20
-4—5/5
^25/30
10//5-^
10//0—^
30/50-y
o o
i|i
Oak Avenue
a o
be
.g
OQ
«.. o..
is-'
li!
eo.,
LEGEND
XXX/XYY - AM/PM Peaic Hour Traffic Voiumea
xxx - Average DaSy Traffte Volumes NO SCALE
v. April. 1998
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CAHLSBAD BOULEVAHD HOTEL
- URBAN SYSTEMS — 00099S
r
ATTACHMENT 6
INTERSECTION AND STREET SEGMENT
LEVELS OF SERVICE
Existing Existing ^• Project Buildout
LOCATION AM PM AM PM AM PM
INTERSECTION
Carisbad Boulevard / Christiansen Way A A A A A A
Cartsbad Boulevard / Beech Avenue A A A A A A
STREET SEGMENT
CARLSBAD BOULEVARD
Cypress Avenue - Beech Avenue A(170) A(325) A(175) A(325) A(225) A(425)
Beech Avenue - Christiansen Way A(170) A(325) A(175) A(325) A(250) A(440)
Christiansen Way - Grand Avenue A(165) A(325) A(185) A(335) A(255) A(485)
BEECH AVENUE
East of Carist)ad Boulevard A(30) A(30) A(55) A(75) A(50) A(55)
CHRISTIANSEN WAY
East of Carist)ad Boulevard A(25) A(30) A(55) A(60) A(55) A(60)
(XXX)=VPH in Peak Direction; Segment Capacity = 1,800 VPHPL
April, 1998
CD-C CBH-Ae.wb3
CAHLSBAD BO/JLEVAHD HOTEL
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r ATTACHMENT 7 Page 1 of 4
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April. 1998
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CAHLSBAD BOULEVAHD HOTEL
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r ATTACHMENT 7 Page 2 of 4
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April. 1998
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r ATTACHMENT 7 Page 3 of 4
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April, 1998
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ATTACHMENT 7 Page 4 of 4
PAQE OF
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CAHLSBAD BOULEVAHO HOTEL
- URBAN SYSTEMS— 000998