HomeMy WebLinkAbout5-82 RESOLUTIONRESOLUTION NO.
A RESOLUTION AUTHORIZING THE MAYOR AND CITY CLERK TO
EXECUTE AN AMENDMENT TO THE CITY' S GRANT AGREEMENT
WITH THE FEDERAL AVIATION ADMINISTRATION FOR AN AIRPORT
MASTER PLAN TO INCLUDE A NOISE IMPACT AND MITIGATION
ANALYSIS OF AIRCRAFT RUN-UP OPERATIONS AT DRAKE FIELD.
BE IT RESOLVED BY THE BOARD OF DIRECTORS OF THE CITY OF
FAYETTEVILLE, ARKANSAS:
That the Mayor and City Clerk are hereby authorized and
directed to execute an amendment to the City's grant agreement
with the Federal Aviation Administration for an airport master
plan study to include a noise impact and mitigation analysis
of aircraft run-up operations at Drake Field. A copy of the
grant amendment authorized for execution hereby is attached
hereto, marked Exhibit "A", and made a part hereof.
PASSED AND APPROVED this 5 -1 -PA -day of}vyy (,
1982.
APPROVED:
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gat, J G�L% illice/
MAYOR
AMENDMENT TO
AGREEMENT FOR ENGINEERING SERVICES
This Agreement entered into as of this 6
day of January.,
1982, amends the Agreement for Engineering Services, executed
August 8, 1980, between the City of Fayetteville, Arkansas and
McClelland Consulting Engineers, Inc.
Purpose. The purpose of this Amendment is to expand the Engineering
Services to include a noise impact and mitigation analysis of air-
craft run-up operations at Drake Field. All provisions of the
original Agreement shall remain unchanged except as specifically
provided for herein.
Scope of Services. The scope of the services to be performed by.
the Engineer is hereby expanded to also include the services
specifically indicated in Appendix A - Scope of Services, attached
hereto and incorporated by reference herein.
Compensation for Engineering Services. It is agreed that the com-
pensation to be paid to the Engineer shall be increased by the
amount 9f fifteen thousand dollars ($15,000), as a result of the
additional services included in this Amendment. The amended total
compensation, excluding that for any Additional Engineering Services
as provided for in the Contract, is therefore sixty-nine thousand,
three hundred eighty-eight dollars ($69,388).
IN WITNESS WHEREOF, the parties hereto have executed, or caused
to be executed by their duly authorized officials, this Agreement
in duplicate on the date heretofore stated.
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' (SEAL) •
ATTEST: /j
By...,•,{,a- 76/
OWNER:
CITY 0FAYET�TEEVV'ILLLE
By l% /cc t / Dti ZG
Typed Name Sherry Rowe Typed Name Paul Noland
Title City Clerk Title Mayor
(SEAL)
ENGINEER:
ATTEST: McCLELLAND CQNSULTING ENGINEERS, INC.
Typed Name Charles McLaughlin /Tyd Name J. E. McClelland
Title Acting Secretary -Treasurer `Title President
APPENDIX A
SCOPE OF SERVICES
NOISE IMPACT ANALYSIS AND NOISE MITIGATION ANALYSIS
FOR RUN-UP OPERATIONS AT DRAKE FIELD
Fayetteville, Arkansas
INTRODUCTION
The purpose of this Scope of Services is to present the technical
approach and description of work to be accomplished by the team
of BRAUN BINION BARNARD, Inc. and VINCENT MESTRE ASSOCIATES. This
work scope has been specifically designed to meet the needs and
requirements of the City of Fayetteville relative to noise problems
associated with the maintenance run -ups of turbdprop aircraft at
Drake Field. This study has been designed to serve the immediate
or short-term need to determine the need for and implementation of
noise control activities at Drake Field.
In order to better understand the Scope of Services presented here,
a discussion of the airport noise problem and our approach to this
problem is warranted. First of all, the basic approach is to first
define the noise environment, i.e., quantitatively describe the
actual noise levels in the community in terms of human response to.
noise. This must be done for both the run -ups and normal operations
at Drake Field. This information is used to determine the magnitude
of the noise problem and properly put the run-up noise in perspective
relative to other operations at Drake Field. Once the magnitude of
the run-up problem has been properly assessed, a design goal will
be established relative to accepted standards for community noise.
Finally, using specific data collected at Drake Field, noise
mitigation alternatives will be evaluated. It is essential that
an evaluation of mitigation alternatives be done using the specific
frequency characteristics of the noise generated by run-up operations
at Drake Field. The sound measurements employed here will be done
both in terms of the commonly used A -weighted decibel (for assess-
ment of noise. impacts on people) and octave band sound pressure
levels (for determining frequency components of the sound to
evaluate mitigation performance).
The format of this Scope of Services is based on three major
elements, including:
Element One/DATA COLLECTION AND MEASUREMENTS
Element Two/EXISTING NOISE DESCRIPTION AT DRAKE FIELD
Element Three/EVALUATE MITIGATION ALTERNATIVES
These elements are divided into various tasks, each of which are
described in detail in the following section.
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Element One/DATA COLLECTION AND MEASUREMENTS
Element One is divided into three tasks, the purpose of which is
to provide the data base through which the noise assessment and
mitigation evaluation will be carried out. Operational information,
community liaison, and interface with the City of Fayetteville will
be done through the firm of BRAUN BINION BARNARD, Inc. The field
noise measurements will be designed by and implemented by the firm
of VINCENT MESTRE ASSOCIATES.
Task A Collect Operational Data. This task will focus on an
operational data base for the run-up operations and airport opera-
tions, identifying theaircraft mix and flight utilization and
including an analysis of flight procedures and aircraft profiles
specific to Drake Field. Sources of information include aircraft
schedules, airport management, air traffic control personnel, air-
line personnel (chief pilot and performance engineer), and ground
observations during the measurement survey. Data needed to
generate existing noise contours include number of current opera-
tions of aircraft, aircraft fleet mix, flight tracks, flight
profiles and typical operational procedures. These data will be
used to develop an .existing Day Night Noise Level (Ldn) noise
contour for Drake Field.
Run-up operations data that needs to be collected includes number
and times of run -ups, including run-up duration and engine power
settings. Information concerning orientation of the aircraft
during run-up, propeller feathering, and number of engines run-up
at one time is also required.
During this task of the program, noise complaint data will also be
collected for analysis relative to the noise measurements. It is
always important in any community noise problem to correlate noise
complaints with the noise sources in order to fully understand the
extent of the problem and to ensure proper evaluation of noise
mitigation alternatives.
Task B. Conduct Initial Public Information Meeting. To commence
the study effort, a public information meeting will be held to
solicit the cooperation of airport neighbors during the noise
study. At this time, specific problem areas in need of measurement
will be identified. The Consultant will be responsible for
conducting the meeting, reviewing the scope of the project, and
responding to any technical and professional questions and concerns.
In addition, the airport and City of Fayetteville personnel will'play
prominent roles in this meeting, to assure coordination and that
mutual interests and efforts are clarified.
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Task C. Measure A -Weighted Noise Levels. The purpose of the
A -weighted noise levels is to determine the noise levels in the
community and at the source in terms that can be directly related
to community noise standards. The A -weighted decibel is a noise
metric which accounts for the frequency response of the human ear
and corresponds well with peoples perception of relative loudness.
Community noise standards published by the Department of Transpor-
tation, Environmental Protection Agency, and Department of Housing
and UrbanDevelopmentare in terms of noise metrics based on the
A -weighted decibel. Included in these measurements will be
measures of the maximum noise level (Lmax), Equivalent Noise Level
(Leg) and Sound Exposure Level (SEL). The latter metrics will be
used for determining the Day Night Noise Levels (Ldn).
Measurements will be made near the aircraft during run -ups
the sensitive residential area where noise complaints have
In the residential area,measurements will be made of both
and approaching and departing aircraft.
The run-up measurement sequence will include measurements
surrounding the aircraft during engine run -ups. This will be done
to determine the directionality of the noise. Measurements will be
completed on a common radius at a minimum of eight locations around
the aircraft. This will be done for a minimum of two run-up
sequences.
and in
occurred.
run -ups
The noise measurements in the residential area will include
measurements of the maximum A -weighted noise levels, Sound
Exposure Levels, and Equivalent Noise Levels for both run-up.
operations and aircraft arrivals and departures. Measurements will
be made at ten locations. At two of these receptor sites, the
specific sites to be determined in the field, an octave band
analysis will be conducted for purposes of clarity, consistency
and coordination. Indigenous noise levels will be ascertained in
this process.
The meaStrements described above will be used to determine the
extent of the noise problem, i.e., whether there is exceedance of
accepted noise standards, and if there is exceedance, the extent
to which the standards are exceeded. The difference between noise
levels measured at the aircraft and that measured in the field is
the existing "field insertion loss". The goal of the mitigation
anaylsis will be to improve the field insertion loss.
Meteorological data will be gathered from the Flight Service
Station and on-site observation. This data will be recorded and
documented and included in the final report noting the findings
and recommendations of this study.
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Task D. Measure the Freauency Characteristics of the Run-up Noise.
The frequency components of the run-up noise will be determined at
the same measurement sequence as the noise measurements described
in Task B. These frequency measurements will be made by measuring
the octave band sound pressure level in each of the ten octave bands
centered from 31.5 Hertz to 16,000 Hertz.
The frequency data is essential for the proper evaluation of
mitigation alternatives relative to the run-up noise. Without
knowing the frequency content of the sound, the performance of a
given mitigation alternative cannot be reliably estimated. For
example, a noise barrier such as a block wall reduces high frequency
noise much better than itdoes very low frequency noise. In order to
predict how well a noise barrier will reduce noise from a given
source, the frequency of the noise source' must be known. The
A -weighted decibel, while good for predicting peoples response to
noise, combines all frequencies into a single number rating of
loudness weighted for human hearing and does not provide any
insight into the frequency of the measured sound. For this reason,
octave band frequency measurements are proposed here in addition
to the A -weighted noise level measurements.
Element Two/EXISTING NOISE DESCRIPTION AT DRAKE FIELD
Element Two is divided into three tasks, which are designed to
produce noise contours for Drake Field. Run-up noise contours will
be produced and an existing noise contour for all aircraft operations
at Drake Field will be produced. These contours, when compared to
the surrounding land uses, will provide the assessment of Drake Field
operations impact on the surrounding area. This assessment will be
done separately for the run-up operations and other airfield
operations.
Task A. Develop Ldn and Lmax Noise Contours for Run-up Operations.
Utilizing the noise measurement data collected in Element One,
noise contdurs for the run-up operations will be constructed. These
contours will include directional characteristics of run-up noise
propagation, topographic barrier effects, building shielding effects,
and any other relevant physical factors observed during the test
sequence. Noise contours will be drawn for both the maximum noise
levels observed and the Day Night Noise Level computed from the
measurement data.
Task B. Develop Ldn Noise Contours For Existing Operations at
Drake Field. Utilizing the Federal Aviation Administration's
Integrated Noise Model (INm) Version 2.7, existing aircraft operations
at Drake Field will be modeled. The noise contours that will be
Plotted include the 60, 65, and 70 Ldn noise contours. The INM is
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a large computer program written in FORTRAN for which VINCENT MESTRE
ASSOCIATES has developed a preprocessor program which operates on
in-house computing systems. This INM file generator develops and
checks for coding errors in the INM data file prior to sending and
launching the INM. The INM model is remotely run on the United
Computing Systems Cyber 6600 computing network. Plots of the noise
contours are generated automatically on a CalComp Digital Plotter.
Task C. Determine Relative Impacts of Run-up Noise on Sensitive
Land Uses. Using the noise contours developed in Tasks A and B
above, the land uses impacted by Drake Field operations and in
particular those impacted by run-up operations will be identified.
Land use information necessary for the impact anaylsis will be
developed. The result of this anaylsis will be the quantified
measure of land use areas that are impacted and the extent to
which they are impacted, and the relative impacts of run -ups
versus other airport operations.
Existing land use in the vicinity of the airport will be inventoried
and mapped. The types of land uses to be mapped include residential,
commerical, industrial, public and agricultural uses. Noise
sensitive uses/areas will be specifically identified. In addition,
natural characteristics which will impact development and planning
in and off airport property will be identified, including
such elements as flood plains, natural areas, topographic
characteristics and other unique features. Key transportation
routes and public utilities or right-of-way will be identified.
Element Three/EVALUATE MITIGATION ALTERNATIVES
The purpose here is to evaluate alternative methods of mitigating
noise impacts identified with the run-up operations. Each
alternative will be examined in terms of noise reduction
performance (improved field insertion loss), feasibility, and
implemel>tation. Those measures which may have great potential
for noise reduction which might prove to be uneconomical will be
discussed in terms of economic impact as well as noise reduction
potential.
Task A Evaluate Alternative Methods of Mitigating Run-up
Operation Noise Impacts. The mitigation alternative will be
evaluated in detail relative to their noise reduction performance.
Where applicable and appropriate, conceptual design parameters
or characteristics, including height, length, location, and material
of construction, will be noted. The following list of mitigation
alternatives has been prepared to demonstrate the analysis technique
that will be used .to evaluate the various mitigation methods.
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1. Noise Barriers. Noise barriers can act as effective mechanisms
for noise control. A noise barrier can consist of_solid walls,
earthen berms, or building structures. The key characteristics of
a noise barrier'are that the noise barrier be solid with no holes or
cracks, sufficient density to prevent sound transmission through
the barrier, and most important that the barrier be high enough to
block "line of sight" between the source and the receiver.
The noise reduction characteristics of a noise barrier are dependent,
on the frequency characteristics of the sound. Low frequency sound
is not attenuated by barriers nearly as well as high frequency sounds.
For aircraft noise this means that barriers are good at reducing
the high pitched noise assiciated with turbo machinery and fan inlet
noise while being considerably less effective with the low frequency
combustion and exhaust noise.
Because of the dependence of barrier noise reduction on frequency
characteristics of the sound, this work scope has been carefully
designed to include measurements of the frequency characteristics
of the run-up noise at Drake Field. VINCENT MESTRE ASSOCIATES has
developed computer programs which compute noise reduction of
barriers based on the frequency characteristics of the source. This
involves computing the Fresnel Number for each frequency and com-
puting the noise reduction in that frequency band. Once the noise
reduction for each frequency is known, the total A -weighted noise
level can be computed and compared to the A -weighted noise level
without the barrier. This difference, or improvement in Field
Insertion Loss, forms the basis for determining if the noise barriers
can significantly improve the noise environment at Drake Field.
Noise barriers of three types will be considered in this work effort.
These are barriers located adjacent to the run-up area, barriers at
the border of the residential area, and the use of buildings and
structures as noise barriers. All three types have been used at
various airports to solve ground operation noise problems.
.2. Noise Enclosures. Sometimes called hush houses, noise enclosures
have been effectively used to reduce ground run-up noise levels.
These facilities are quite complex to design properly to ensure
operator safety, noise reduction, and long life. While hush houses
represent the most effective means of noise control, the cost may
be prohibitive. Therefore, included in the analysis of noise
enclosures will be estimates of relative cost for such devices.
Noise enclosures have been built for use with business jet aircraft.
The military has developed noise enclosures for propeller driven
aircraft as well as jet aircraft. The major advantage of a hush
house is the ability to reduce inlet noise, prop noise, and exhaust
noise simultaneously. The major disadvantage is cost.
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3. Noise Suppressors. Noise suppressors have a very high potential
for reducing run-up noise at Drake Field. Noise suppressors are
devices that are located aft of the engine and reduce noise associated
with the exhaust gases. Such devices can be nothing more than simple
flow separators which take a narrow high speed flow of exhaust gas
and divide the flow into several larger area slower moving air
streams. This reduction in flow velocity can result in radical noise
reductions. Noise suppressors can also include sound absorptive and
tuned resonator characteristics which can act as exhaust "mufflers".'
Noise suppressors can only be used on the exhaust stream of propeller
driven aircraft and therefore, cannot reduce inlet noise or propeller
noise. For this reason it is of critical importance that the noise
measurements include frequency measurements so that the noise
problem can be identified in terms of exhaust noise, propeller noise,
inlet noise, or turbo machinery noise. Certainly, noise suppressors
cannot be used to reduce propeller noise.
4. Modified Testing Schedules. Noise control through midification
of test schedules can be considered as a last resort method of
relieving community noise problems. This can mean that tests are
delayed or confined to certain operating periods. While this
amounts to a severe restriction on the operator, it serves as a
basis for comparing noise reduction achieved through schedule
restrictions versus other mechanisms described herein.
5. Aircraft Reorientation During Run -ups. During the run-up
operations, the noise as a function of direction from the aircraft
varies There exists the potential to utilize this fact, perhaps
with another control mechanism, to achieve substantial noise
reduction. During the measurement phase of the scope of services,
measurements at several locations located on a redius around the
aircraft are proposed. These data will be used to determine if
aircraft orientation can be used to reduce noise due to run-up
operatiors.
6. Run-up Relocation. Run-up relocation will be evaluated in terms
of noise reductions that can be achieved by moving run-up operations
to other locations on the airfield. Moving the run-up locations can
take advantage of increased distance to the residential area or to
take advantage of some building or structure which can act as a
noise barrier. Movement of run -ups to increase distance between
the source and the receiver is not a likely candidate for successful
noise reduction. For every doubling of distance between the source
and the receiver, a 6 dB noise reduction will occur. Since the
homes in question are already quite some distance away, this distance
doubled would locate the run -ups very far from its current location
while achieving only a 6 dB noise reduction.
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Task B. Develop Document on Noise Study. The Consultant will
develop a findings and recommendations document utilizing the output
from the tasks described above for the short-term noise study.
Findings of this evaluation will be documented, explained in easily
understandable terms. Twenty copies of this document will be
furnished the Sponsor.
Task C. Conduct Public Information Meeting. A public information
meeting will be conducted to present the various proposals and
recommendations of the Noise Study. Presentation material will be
prepared which adequately illustrates and which will be directed
toward assuring an understanding of the study findings on the part
of the public.
NOISE MEASUREMENT EQUIPMENT
In-house noise measurement instrumentation includes computer
automated 24-hour measurements. VINCENT MESTRE ASSOCIATES utilizes
its Digital. Acoustics Model 607P Version 3 Portable Noise Data
Acquisition System, and/or our BBN model 614 Portable Noise Monitor
System. These instruments calculate both single event and 24-hour
noise levels, and their automatic calculations reduce the time
required for data reduction. The Digital Acoustics instrumentation
is the latest and most sophisticated noise monitor, for ;reasuring
community noise. The Version 3 incorporates dual microprocessors
and the capability of measuring the energy content of very short
duration high noise level sounds with extremely high accuracy.
For measuring the frequency characteristics of a noise source, a
General Radio 1933 Sound Level Analyzer with built in octave band
filters will be utilized.
All the equipment identified above satisfy American National Standards
Institute (ANSI) standards for Type 1 noise measurement instrumen-
tation with calibration traceable to the National Bureau of Standards.
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United States of America
Department of Transportation
FEDERAL AVIATION ADMINISTRATION
Bethany, Oklahoma 73008
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Page 1 of 2 Pages
Contract No. DOT FA 81 SW -8350
Drake Field Airport
Fayetteville, Arkansas
AMENDPIENT NO. 1 TO GRANT AGREEMENT FOR PROJECT NO. 6-05-0020-11
IT IS AGREED that the project work description for this project is hereby
revised to read as follows:
Pave access taxiway (approximately 40'x1250'); construct air-
craft parking apron (approximately 20,600 SY); and develop a
noise study.
The following special conditions .are added to and made a part of the Grant
Agreement:
14. Sponsor agrees that the noise study be conducted as outlined
in the work scope submitted and approved by FAA on
December 21, 1981.
15. Sponsor agrees to provide the following:
a. Final Report (5 copies)
b. Draft Report (5 copies)
c. Progress Reports (monthly).
Executed this -.J ''day of L—} r, tli*;4_i, 1982.
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(SEAL)
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Attest:
i
Attest: .NCIZ-{i_(V '>/i"
Title City 'Clerk
Department of Transportation
UNITED STATES OF AMERICA
FEDERAL AVIATION ADMINISTRATION
Bob A. Smith, Chief, Oklahoma City Airports
Title District Office, FAA, Southwest Region
City of Fayetteville, Arkansas
By
Title
7-1
1 (t i . 1., :'!- ..?/(-67.V(/
Mayor
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Page 2 of 2 Pages
CERTIFICATE OF SPONSOR'S ATTORNEY, submitted pursuant to Section 16(h) of the
Airport and Airway Development Act of 1970, as amended.
I, acting as Attorney for the City of Fayetteville, Arkansas, do hereby
certify that I have examined the foregoing Amendment to Grant Agreement
and the proceedings taken by said Sponsor relating thereto, and find that
the acceptance thereof by said Sponsor has been duly authorized and that
the execution thereof is in all respects due and proper and in accordance
with the laws of the State of Arkansas and the regulations, and further
that, in my opinion, said Amendment to Grant Agreement constitutes a legal
and binding obligation of the Sponsor in accordance with the terms thereof.
Dated at Fayetteville, Arkansas this
day of``_� L, yj ;.../ ,. 1982.
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6 /L City Attorney