HomeMy WebLinkAboutCDP 2016-0006; MFD-01; 2637 JEFFERSON STREET RESIDENTIAL DEVELOPMENT NOISE ASSESSMENT; 2017-09-14Ldn Consulting, rnc.
42428 Chisolm Trail, Murrieta CA 92562
www.ldnconsulting.net
September 14, 2017
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
phone 760-473-J253
fax 760-689-4943
Subject: 2637 Jefferson Street Residential Development Noise
Assessment -Carlsbad CA
The firm of Ldn Consulting, Inc. is pleased to submit the following noise analysis for
the proposed 2637 Jefferson Street residential development in the City of Carlsbad.
The purpose of the survey is to determine the estimated exterior noise levels at the
proposed residential uses and recommend mitigation measures for compliance with
the City of Carlsbad guidelines and requirements for noise.
PROJECT LOCATION/DESCRIPTION
The proposed site is located on 0.25 acres and includes 4 attached multifamily homes.
The project site is located 0.25 miles west of Interstate 5 along Jefferson Street in the
City of Carlsbad. The project site address is 2637 Jefferson Street, Carlsbad, CA.
The primary noise source that affects the site is vehicular traffic from adjacent Jefferson
Street and background noise from Laguna Drive located approximately 450 feet to the
south of the site. The project vicinity can be seen in Figure 1 and the project site
configuration is provided in Figure 2 below.
9/14/2017 1 1785-02 2637 Jefferson Street Noise Report
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
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9/14/2017
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Ldn eon.ult/1111, me.
42428 Chisolm Trail, Munieta CA 92562
phone 760-473-1253
Fax 760-689-4943
Figure 1: Project Site Location
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1785-02 2637 Jefferson Street Noise Report
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
9/14/2017
Ldn CoMult/1111, Int:.
42428 Chisolm Trail, Munfeta CA 92562
phone 760-473-1.253
Fax 760-689-4943
Figure 2: Proposed Project Site Plan
3 1785-02 2637 Jefferson Street Noise Report
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
ACOUSTICAL FUNDAMENTALS
Ldn eon.ult/1111, Int:.
42428 Chisolm Trail, Nunieta CA 92562
phone 760-473-.1253
Fax 760-689-4943
Noise is defined as unwanted or annoying sound which interferes with or disrupts
normal activities. Exposure to high noise levels has been demonstrated to cause
hearing loss. The individual human response to environmental noise is based on the
sensitivity of that individual, the type of noise that occurs and when the noise occurs.
Sound is measured on a logarithmic scale consisting of sound pressure levels known
as a decibel (dB). The sounds heard by humans typically do not consist of a single
frequency but of a broadband of frequencies having different sound pressure levels.
The method for evaluating all the frequencies of the sound is to apply an A-weighting
to reflect how the human ear responds to the different sound levels at different
frequencies. The A-weighted sound level adequately describes the instantaneous noise
whereas the equivalent sound level depicted as Leq represents a steady sound level
containing the same total acoustical energy as the actual fluctuating sound level over
a given time interval.
The Community Noise Equivalent Level (CNEL) is the 24 hour A-weighted average for
sound, with corrections for evening and nighttime hours. The corrections require an
addition of 5 decibels to sound levels in the evening hours between 7 p.m. and 10
p.m. and an addition of 10 decibels to sound levels at nighttime hours between 10
p.m. and 7 a.m. These additions are made to account for the increased sensitivity
during the evening and nighttime hours when sound appears louder. CNEL values do
not represent the actual sound level heard at any particular time, but rather
represents the total sound exposure.
Additionally, Sound Transmission Class ( or STC) is an integer rating of how well
airborne sound is attenuated by a building partition. STC is widely used to rate interior
partitions, ceilings/floors, doors, windows and exterior wall configurations (see ASTM
International Classification E413 and E90). The STC number is derived from tested
sound attenuation values found at the 1/3 octave band frequencies. These
transmission-loss (TL) values are then plotted and compared to a standard reference
contour. Acoustical engineers fit these values to the appropriate TL Curve to
9/14/2017 4 1785-02 2637 Jefferson Street Noise Report
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
Ldn eon.ult/1111, Int:.
42428 01/60/m Trail, Nunfeta CA 92562
phone 760-473-1253
Fax 760-689-4943
determine a single STC value found at 500 Hertz. STC is roughly the decibel reduction
in noise a partition can provide, abbreviated 'dB'.
If an 85 dB sound on one side of a wall is reduced to 50 dB on the other side, that
partition is said to have an STC of 35. This number does not apply across the range of
frequencies because the STC value is derived from a curve-fit from the tested 1/3
octave band frequencies. Any partition will have less TL at lower frequencies. For
example, a wall with an STC of 35 may provide over 40 dB of attenuation at 3000 Hz
but only 15 dB of attenuation at 125 Hz.
NOISE STANDARDS
The City of Carlsbad's Noise Guidelines Manual (1995) requires that all exterior
sensitive areas shall limit noise exposure. For noise sensitive residential land uses, the
City has adopted a policy which has established a "normally acceptable" exterior noise
level goal of 60 dBA CNEL for the outdoor areas and an interior noise level of less than
45 dBA CNEL. For residential properties identified as requiring a noise study, a study
shall be prepared by an acoustical professional. This study shall document the
projected maximum exterior noise level and mitigate the projected exterior noise level
to a maximum allowable noise level as identified in Noise Guideline Manual.
Interior noise levels should be mitigated to a maximum of 45 dBA CNEL in all habitual
rooms when the exterior of the residence are exposed to levels of 60 dBA CNEL or
more. If windows and doors are required to be closed to meet the interior noise
standard, then mechanical ventilation shall be provided per City requirements.
ANALYSIS PROCEDURES
Exterior Noise Levels
The primary source of noise impacts to the project site will be vehicular noise from
adjacent Jefferson Street and background noise from Laguna Drive located
approximately 450 feet south of the project site. The projected roadway noise levels
from vehicular traffic were calculated using the methods in the Highway Noise Model
9/14/2017 s 1785-02 2637 Jefferson Street Noise Report
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
Ltln Conlllllt/1111, Int:.
42428 Chisolm Trail, Hunieta CA 92562
phone 760-473-1253
Fax 760-6/l!J-4943
published by the Federal Highway Administration (FHWA Highway Traffic Noise
Prediction Model, FHWA-RD-77-108, December, 1978). The FHWA Model uses the traffic
volume, vehicle mix, speed, and roadway geometry to compute the equivalent noise
level. A spreadsheet calculation was used which computes equivalent noise levels for
each of the time periods used in the calculation of CNEL. Weighting these equivalent
noise levels and summing them gives the CNEL for the traffic projections.
Mobile noise levels radiant in an almost oblique fashion from the source and drop off
at a rate of 3 dBA for each doubling of distance under hard site conditions and at a
rate of 4.5 dBA for soft site conditions. Hard site conditions consist of concrete,
asphalt and hard pack dirt while soft site conditions exist in areas having slight grade
changes, landscaped areas and vegetation.
The future traffic noise model also utilizes the vehicle mix referenced in the City's Noise
Guideline Manual of 97.9% Autos, 1.8% Medium Trucks and 0.3% Heavy Trucks for all
roadways. The vehicle mix provides the hourly distribution percentages of automobile,
medium trucks and heavy trucks for input into the FHWA Model.
Future year 2035 traffic along Jefferson Street and Laguna Drive is expected to have
13,500 average daily trips (ADT) and 6,900 ADT, respectively, according to the SANDAG
Series 13 Traffic Prediction Model for the year 2035. The speed limit along Jefferson
Street is 35 MPH and 30 MPH on Laguna Drive. Based on the exterior noise model, the
worst-case cumulative noise level from all the roadways was found to be 66. 7 dBA CNEL
at the site. The modeling results are provided in Figure 4 on the following page. No
noise barriers, existing structures or topography that may affect noise levels were
incorporated in the calculations.
9/14/2017 6 1785-02 2637 Jefferson Street Noise Report
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
Ldn CoMu/111111, me.
42428 Chisolm Trail, Munieta CA 92562
phone 760-473-~253
Fax 760-689-4943
Figure 4: Future Cumulative Noise Levels
Project Name:
Project Number:
Mix Ratio by Percent
Propagation Rule
Roadway
Jefferson Street
Laguna Drive
Jefferson Street
Laguna Drive
Cumulative Noise Level
9/14/2017
37 Jefferson Street
17-85
Date:
Location:
Traffic Volumes, Mix and Speeds
Autos Med. Trucks Heavy Trucks
97.9 1.8 0.3
Hard
14-Sep-17
carlsbad
ADT
13,500
6,900
Speed MPH CNEL O SO Feet 60 CNEL {Feet)
35 66.6 231
30 62.2 83
Noise Reduction due to Distance
Distance
50
450
Reduction
0.00
-14.31
7
Resultant Level
66.6
47.9
66.7 dBACNEL
1785-02 2637 Jefferson Street Noise Report
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
Interior Noise Levels
Ldn eon.ult/1111, Int:.
42428 Chisolm Trail, /llunieta CA 92562
phone 760-473-1253
Fax 760-689-4943
The methodology used to determine the resultant interior noise levels is based upon
the exterior noise level minus the sound transmission loss as identified in the American
Society of Testing and Materials (ASTM) guidelines: E413 &E90. Standard building
construction will provide a noise reduction of approximately 12-15 dBA with a windows
open condition and a minimum 20 dBA noise reduction with the windows closed. The
exterior noise levels at the proposed structures calculated in terms of dBA are
converted to the six octave band sound pressure levels between: 125 -4000 Hertz.
Acoustical modeling of the proposed project dwelling units was performed in
accordance with the above guidelines and included combining the transmission loss for
each of the building components that will reduce the interior noise levels. Building
components typically include the windows, exterior doors, and exterior walls. The total
noise reduction is dependent upon the transmission loss of each building component,
their subsequent surface area, quality of the building/construction materials, a building
fac;ade and angle correction.
The interior noise level is also dependent on the acoustical energy absorbed within the
room based upon the Noise Reduction Coefficients (NRC). NRC is a scalar
representation of the amount of sound energy absorbed upon striking a particular
surface and the arithmetic value average of sound absorption coefficients indicating a
material's ability to absorb sound. The absorption coefficients for individual surface
areas such as carpet, drywall and furnishings are used to calculate the interior room
effects. The calculated building noise reduction includes both the room absorption
characteristics and the transmission loss from the exterior wall assembly.
The interior noise reduction calculations were performed using Ldn's interior noise
model. The model converts the exterior sound level to octave band frequencies and
accounts for the transmission loss, correction factors and room absorption. The floor
plans used for this analysis were provided by ohms Architects dated December 2016.
The following construction details were utilized for each of the building assemblies to
determine the noise reduction characteristics:
9/14/2017 8 1785-02 2637 Jefferson Street Noise Report
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
Ldn Conllult/1111, Int:.
42428 Chisolm Trail, Nunieta CA 92562
phone 760-473-:1253
Fax 760-68!J-4943
Exterior walls must have a Sound Transmission Class (STC) rating of 36 or better.
Exterior walls with this rating consist of 2"x4" studs or larger, spaced 16" o.c. with R-13
insulation minimum and an exterior surface of 1/4" lap siding or 7 /8" cement plaster
(stucco). Interior wall and ceiling surfaces shall be at least 1/2" thick gypsum or
plaster. Roof assemblies should have a minimum of 1/2" sheathing, R-19 insulation
and sealed to prevent noise leaks.
Exterior entry doors should be of solid core construction and glass assemblies should
be dual-glazed and acoustical sealant applied around the exterior edges. The window
and door assemblies are generally the weakest noise reducing component but are the
most convenient and cost effective elements to change if additional attenuation is
needed. The STC ratings for the glass assemblies and exterior entry doors were
calculated in the interior noise model and provided in the findings below.
Bathrooms, kitchens, closets and corridors are not required to meet the 45 dBA CNEL
standard and therefore were not modeled. All living areas, this includes bedrooms, living
rooms and dining rooms were modeled to determine the interior noise reductions. If the
modeled interior noise levels were found to be higher than 45 dBA CNEL in the living
areas with the minimum assembly requirements described above additional modeling
was performed to determine the minimum STC rating for the glass assemblies to further
reduce interior noise levels below the acceptable interior threshold of 45 dBA CNEL.
FINDINGS
The exterior noise levels were determined to be as high as 67.7 dBA CNEL for the
buildings located adjacent to Jefferson Street. Basic calculations show that a windows
open condition will typically reduce the interior noise levels roughly 15 dBA CNEL and not
provide adequate interior noise mitigation. To meet the 45 dBA CNEL interior noise
standard, an overall minimum interior noise level reduction of 22.7 dBA CNEL is needed
for the proposed project. Therefore, a closed window condition is required to reduce
interior noise levels to comply with CCR Title 24 and City requirements. The windows
closed condition requires that mechanical ventilation is installed to move air within the
structure and control temperatures. The mechanical ventilation must meet the
jurisdictional requirements for these dwelling units.
9/14/2017 9 1785-02 2637 Jefferson Street Noise Report
ohms Architects
Miguel A. Reyes
536 Sears Avenue
San Diego, CA 92118
Ldn eon.ult/1111, me.
42428 Chisolm Trail, Hunieta CA 92562
phone 760-473-1253
Fax 760-689-4943
The necessary Sound Transmission Class and transmission losses for all glass
assemblies and entry doors of the residential units located adjacent to and having
direct line of sight to Jefferson Street are provided in Table 1. The modeled results
with an anticipated interior noise level of 45 dBA CNEL or less are provided as an
Attachmentto this report.
Table 1: Sound Transmission Class Ratings
STC Octave Band Transmission Loss (Hz)
Assembly Rating1
125 250 500 1000 2000 4000
Windows 30 20 21 26 34 38 29
Fixed Windows 30 20 20 26 35 39 37
Glass Doors 30 22 20 29 33 39 30
1 STC Ratings used in Model
All glass assemblies of the units having direct line of sight to Jefferson Street should
be dual-paned and acoustical sealant applied around the exterior edges having an STC
30 rating. No impacts are anticipated with the incorporation of the STC ratings provided
in Table 1. If you have any questions, please do not hesitate to contact me directly at
(760) 473-1253 or jlouden@ldnconsulting.net.
Sincerely,
Ldn Consulting, Inc.
Jeremy Louden, Principal
Attachments: Interior Noise Model Calculations
9/14/2017 10 1785-02 2637 Jefferson Street Noise Report
INTERIOR NOISE CALCULATIONS
Project Name: 2637 Jefferson
Building (s) All
Floor Level 1
Arch Plan: A&B
Room Type: Living/Dining
Exterior Noise Levels
Exterior
Assembly Source Area
Stucco NBS W-50-71 470
Windows Champion 65
Fixed Window Champion 12
Glass Doors Thermal Tru 24
Exterior Door NBS Monograph 77 0
Room Absorption (RA)
Interior
Characteristics Source
Carpet Army TM 5-805-4
Furnishings Army TM 5-805-4
Drywall Netwell
Overall Absorption Factor (Furnished Room)
Noise Reduction
Noise Reduction from Absorption based upon Floor Area
Noise Level Increase for Defects and Exposed Surface Area
STC
36
30
30
30
28
NRC
0.28
0.45
0.07
0.8
Overall Reduction from Tranmission Loss + Room Absorption -Surfa
Building Fac;ade Noise Level (dBA CNEL)
Ldn Consulting, Inc.
Date: 9/14/17
Project# 17-85
Transmission Loss (dB)
Frequency (Hz.)
125 250 500 1000 2000 4000
15 25 33 44 so 43
20 21 26 34 38 29
20 20 26 35 39 37
22 20 29 33 39 30
16 14 23 30 36 26
Absorption Coeffidents
Frequency {Hz.)
125 250 500 1000 2000 4000
0.15 0.17 0.12 0.32 0.52 0.30
0.32 0.29 0.42 0.58 0.60 0.48
0.09 0.08 0.05 0.03 0.06 0.09
0.56 0.54 0.59 0.93 1.18 0.87
125 250 500 1000 2000 4000
-24.6 -24.6 -24.6 -24.6 -24.6 -24.6
18.4 18.4 18.4 18.4 18.4 18.4
ce Exposure 22.9
67.7
Resultant Interior Noise Level (dBA CNEL) 45
* Corrections for Fa~de Level was accounted for In the modeling.
INTERIOR NOISE CALCULATIONS
Project Name:
Building (s)
Floor Level
Arch Plan:
Room Type:
2637 Jefferson
All
2
A&B
Bedroom 1
Exterior Noise Levels
Exterior
Assembly Source
Stucco NBS W-50-71
Windows Champion
Fixed Window Champion
Glass Doors Thermal Tru
Exterior Door NBS Monograph 77
Room Absorption (RA)
Interior
Characteristics Source
Carpet Army TM 5-805-4
Furnishings Army TM 5-805-4
Drywall Netwell
Overall Absorption Factor (Furnished Room)
Noise Reduction
Area
160
15
9
0
0
Noise Reduction from Absorption based upon Floor Area
Noise Level Increase for Defects and Exposed Surface Area
src
36
30
30
30
28
NRC
0.28
0.45
0.07
0.8
Overall Reduction from Tranmission Loss + Room Absorption -Surfa
Building Fa<;ade Noise Level (dBA CNEL)
125 250
15 25
20 21
20 20
22 20
16 14
125 250
0.15 0.17
0.32 0.29
0.09 0.08
0.56 0.54
125 250
-20.8 -20.8
16.4 16.4
ce Exposure
Ldn Consulting, Inc.
Date: 9/14/17
Project# 17-85
Transmission Loss (dB}
Frequency {Hz.}
500 1000 2000 4000
33 44 50 43
26 34 38 29
26 35 39 37
29 33 39 30
23 30 36 26
Absorption Coefficients
Frequency {Hz.}
500 1000 2000 4000
0.12 0.32 0.52 0.30
0.42 0.58 0.60 0.48
0.05 0.03 0.06 0.09
0.59 0.93 1.18 0.87
500 1000 2000 4000
-20.8 -20.8 -20.8 -20.8
16.4 16.4 16.4 16.4
27.7
67.7
Resultant Interior Noise Level (dBA CNEL) 40
* Corrections for Fai;ade Level was accounted for in the modeling.
INTERIOR NOISE CALCULATIONS
Project Name: 2637 Jefferson
Building (s) All
Floor Level 2
Arch Plan: A&B
Room Type: Bedroom 2
Exterior Noise Levels
Exterior
Assembly Source Area
Stucco NBS W-50-71 260
Windows Champion 30
Fixed Window Champion 15
Glass Doors Thermal Tru 0
Exterior Door NBS Monograph 77 0
Room Absorption (RA)
Interior .
Characteristics Source
Carpet Army TM 5-805-4
Furnishings Army TM 5-805-4
Drywall Netwell
Overall Absorption Factor (Furnished Room)
Noise Reduction
Noise Reduction from Absorption based upon Floor Area
Noise Level Increase for Defects and Exposed Surface Area
src
36
30
30
30
28
NRC
0.28
0.45
0.07
0.8
Overall Reduction from Tranmission Loss + Room Absorption -Surfa
Building Fac;ade Noise Level (dBA CNEL)
125 250
15 25
20 21
20 20
22 20
16 14
125 250
0.15 0.17
0.32 0.29
0.09 0.08
0.56 0.54
125 250
-21.8 -21.8
17.0 17.0
ce Exposure
Ldn Consulting, Inc.
Date: 9/14/17
Project# 17-85
Transmission Loss {dB}
Frequency {Hz.}
500 1000 2000 4000
33 44 so 43
26 34 38 29
26 35 39 37
29 33 39 30
23 30 36 26
Absorption Coeffidents
Frequency {Hz.}
500 1000 2000 4000
0.12 0.32 0.52 0.30
0.42 0.58 0.60 0.48
0.05 0.03 0.06 0.09
0.59 0.93 1.18 0.87
500 1000 2000 4000
-21.8 -21.8 -21.8 -21.8
17.0 17.0 17.0 17.0
26.3
67.7
Resultant Interior Noise Level (dBA CNEL) 41
* Corrections for Fa~de Level was accounted for in the modeling.
INTERIOR NOISE CALCULATIONS
Project Name:
Building (s)
Floor Level
Arch Plan:
Room Type:
2637 Jefferson
All
1
C&D
Bedroom 1
Exterior Noise Levels
Exterior
Assembly
Stucco
Windows
Fixed Window
Glass Doors
Exterior Door
Source
NBS W-50-71
Champion
Champion
Thermal Tru
NBS Monograph 77
Room Absorption {RA)
Interior
Characteristics Source
Carpet Army TM 5-805-4
Furnishings Army TM 5-805-4
Drywall Netwell
Overall Absorption Factor (Furnished Room)
Noise Reduction
AIN
130
15
0
0
0
Noise Reduction from Absorption based upon Floor Area
Noise Level Increase for Defects and Exposed Surface Area
STC
36
30
30
30
28
NRC
0.28
0.45
0.07
0.8
overall Reduction from Tranmission Loss + Room Absorption -Surfa
Building Fac;ade Noise Level (dBA CNEL)
125 250
15 25
20 21
20 20
22 20
16 14
125 250
0.15 0.17
0.32 0.29
0.09 0.08
0.56 0.54
125 250
-21.4 -21.4
15.2 15.2
ce Exposure
Ldn Consulting, Inc.
Date: 9/14/17
Project# 17-85
Transmission Loss {dB}
Frequency {Hz.}
500 1000 2000 4000
33 44 so 43
26 34 38 29
26 35 39 37
29 33 39 30
23 30 36 26
Absorption Coeffidents
Frequency {Hz.}
500 1000 2000 4000
0.12 0.32 0.52 0.30
0.42 0.58 0.60 0.48
0.05 0.03 0.06 0.09
0.59 0.93 1.18 0.87
500 1000 2000 4000
-21.4 -21.4 -21.4 -21.4
15.2 15.2 15.2 15.2
29.5
67.7
Resultant Interior Noise Level (dBA CNEL) 38
* Corrections for Fa~de Level was accounted for in the modeling.
INTERIOR NOISE CALCULATIONS
Project Name: 2637 Jefferson
Building (s) All
Floor Level 2
Arch Plan: C&D
Room Type: Bedroom 2
Exterior Noise Levels
Exterior
Assembly Source Area
Stucco NBS W-50-71 130
Windows Champion 15
Fixed Window Champion 0
Glass Doors Thermal Tru 0
Exterior Door NBS Monograph 77 0
Room Absorption (RA)
Interior
Characteristics Source
Carpet Army TM 5-805-4
Furnishings Army TM 5-805-4
Drywall Netwell
Overall Absorption Factor (Furnished Room)
Noise Reduction
Noise Reduction from Absorption based upon Floor Area
Noise Level Increase for Defects and Exposed Surface Area
STC
36
30
30
30
28
NRC
0.28
0.45
0.07
0.8
Overall Reduction from Tranmission Loss + Room Absorption -Surfa
Building Fa<;ade Noise Level (dBA CNEL)
Ldn Consulting, Inc.
Date: 9/14/17
Project# 17-85
Transmission Loss {dB)
Frequency {Hz.)
125 250 500 1000 2000 4000
15 25 33 44 so 43
20 21 26 34 38 29
20 20 26 35 39 37
22 20 29 33 39 30
16 14 23 30 36 26
Absorption Coeffidents
Frequency {Hz.)
125 250 500 1000 2000 4000
0.15 0.17 0.12 0.32 0.52 0.30
0.32 0.29 0.42 0.58 0.60 0.48
0.09 0.08 0.05 0.03 0.06 0.09
0.56 0.54 0.59 0.93 1.18 0.87
125 250 500 1000 2000 4000
-21.4 -21.4 -21.4 -21.4 -21.4 -21.4
15.2 15.2 15.2 15.2 15.2 15.2
ce Exposure 29.5
67.7
Resultant Interior Noise Level (dBA CNEL) 38
* Corrections for Fai;ade Level was accounted for in the modeling.
INTERIOR NOISE CALCULATIONS
Project Name:
Building (s)
Floor Level
Arch Plan:
Room Type:
2637 Jefferson
All
3
C&D
Living/Dining
Exterior Noise Levels
Exterior
Assembly
Stucco
Windows
Fixed Window
Glass Doors
Exterior Door
Source
NBS W-50-71
Champion
Champion
Thermal Tru
NBS Monograph 77
Room Absorption (RA)
Interior
Characteristics Source
Carpet Army TM 5-805-4
Furnishings Army TM 5-805-4
Drywall Netwell
Overall Absorption Factor (Furnished Room)
Noise Reduction
Area
550
45
38
112
0
Noise Reduction from Absorption based upon Floor Area
Noise Level Increase for Defects and Exposed Surface Area
STC
36
30
30
30
28
NRC
0.28
0.45
0.07
0.8
Overall Reduction from Tranmission Loss + Room Absorption -Surfa
Building Fa<;ade Noise Level (dBA CNEL)
125 250
15 25
20 21
20 20
22 20
16 14
125 250
0.15 0.17
0.32 0.29
0.09 0.08
0.56 0.54
125 250
-25.8 -25.8
19.0 19.0
ce Exposure
Ldn Consulting, Inc.
Date: 9/14/17
Project # 17-85
Transmission Loss {dB}
Frequency {Hz.}
500 1000 2000 4000
33 44 50 43
26 34 38 29
26 35 39 37
29 33 39 30
23 30 36 26
Absorption Coefficients
Frequency {Hz.}
500 1000 2000 4000
0.12 0.32 0.52 0.30
0.42 0.58 0.60 0.48
0.05 0.03 0.06 0.09
0.59 0.93 1.18 0.87
500 1000 2000 4000
-25.8 -25.8 -25.8 -25.8
19.0 19.0 19.0 19.0
22.3
66.7
Resultant Interior Noise Level (dBA CNEL) 44
* Corrections for Fai;ade Level was accounted for in the modeling.