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| Break-out noise transmitted through a duct wall,
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On
Noise Generation and Abatement
in Gas
Turbine Installations
Jeff
Lotton and Rainer Kurz
CONTENTS
1.0
INTRODUCTION TO TURBOMACHINERY COMPONENTS AND TERMINOLOGY
2.0
FUNDAMENTAL SOURCES OF TURBOMACHINERY NOISE
2.1
AXIAL COMPRESSOR
2.2
COMBUSTOR
2.3
EXHAUST COLLECTION / DIFFUSION
2.4
CASING
2.5
SUPPORTING EQUIPMENT
3.0
TYPICAL NOISE CONSTRAINTS ON TURBOMACHINERY INSTALLATIONS
4.0
STEPS TO ACHIEVE NOISE CONTROL LIMITS
5.0
VERIFICATION MEASUREMENTS
6.0
PRACTICAL LIMITATIONS OF VERIFICATION MEASUREMENTS
7.0
REFERENCES
8.0
APPENDIX
8.1
SAMPLE CALCULATION METHODS FOR DETERMINATION OF SITE SOUND
LEVELS
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2 |
2
On
Noise Generation and Abatement
in Gas
Turbine Installations
1.0
INTRODUCTION
TO TURBOMACHINERY COMPONENTS AND TERMINOLOGY
The typical
arrangement of a gas turbine
engine (Figure 1) involves several discrete steps to achieve
useable
output power. The air is compressed, fuel is mixed in, and the mixture is
combusted, forced
through a turbine,
and then is exhausted to atmosphere.
Figure
1. Cross-Sectional Schematic of Typical Industrial Gas Turbine
Each of
these steps involves large changes in gas
enthalpy, which usually is the source of large pressure
changes.
Pressure fluctuations are the basis of sound and its subjective counterpart,
noise.
Although
within the practice of noise control engineering, one must be very careful about
the distinction
between the
terms “noise” and “sound.” It is hoped that some informality taken
within the context of this
paper will
make the task of absorbing the subject matter easier.
2.0
FUNDAMENTAL
SOURCES OF TURBOMACHINERY NOISE
2.1
AXIAL
COMPRESSOR
The axial
compressor uses stages of rotating airfoils usually with stationary sections of
positioning airfoils
in between
the rotating stages. Often, these airfoils are simply called blades. For a
stationary observer
upstream of
the inlet to the compressor, each time a blade passes the observer, there will
be a large
fluctuation
of pressure associated with the blade pressure field passing by (Figure 2).
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3 |
3
Primary
Noise Generation Mode of
Axial
Compressor with Cascaded Blades
The
pressure fluctuation superimposed over the entire inlet face of the compressor
is the basic noise
generating
mechanism from the axial compressor. Since the pressure fluctuations occur each
time a
blade
passes a fixed position and since the blades are mounted to the rotating shaft,
the inlet noise levels
exhibit
significant amplitude at a specific frequency. This is referred to as a
“tone” or "blade passing
frequency”
(BPF) and is a characteristic element of turbomachinery noise signatures.
The first
stage of the axial compressor in the industrial gas turbine
is the primary contributor to the
compressor
noise. If the BPF and shaft speed are known, it is relatively simple to
determine this
experimentally
by measuring the BPF and dividing by the shaft rotating speed. The result should
be the
number of
blades on the first rotating stage.
The primary
contributions of the axial compressor are the two “haystacks” on the right
side of the inlet
sound
pressure levels shown in Figure 3.
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4
Axial
Compressor Sound Level Frequency Spectrum
Further
practical complications arise when active guide vane controls are considered.
The total sound
pressure
level of all of the axial compressor effects is not always highest at the
highest speed or output
power,
(Tyler and Sofrin, 1961).
2.2
COMBUSTOR
The process
of combustion generates pressure fluctuations, which are the primary source of
noise; the
pressure
fluctuations then excite the natural frequencies of the working fluid volume
itself. The resulting
pressure
fluctuations are carried with the working fluid and are often transmitted to any
surface that
contains
the working fluid. Finally, when the working fluid is exhausted to atmosphere,
the pressure
fluctuations
are transmitted to the atmosphere. These pressure fluctuations are the source of
acoustic
noise.
The
combustor housing (Figure 4) and exhaust collector or ducting can have the
acoustic noise
transmitted
to them by the working fluid and then reradiate the noise to the surroundings.
Ultimately, the
noise is
fluid borne and transmitted to the surroundings by the flow conduits and the
structures that
support
them.
Because
there is a large amount of low frequency acoustic energy in the working fluid
during and after
combustion,
transmission to any surface that comes into contact with the working fluid is a
common mode
of noise
generation in the combustion section of the industrial gas
turbine. Generally low frequency
energy
transmits through mechanical connections better than high frequency energy and,
as a result, flow
conduits,
connecting structures and equipment foundations can become significant sources
of
combustion-generated
noise.
Although
there is some debate on the ability of the combustion-generated noise to travel
through near
sonic flow
nozzles, the contribution of combustion-generated noise in the exhaust flow has
been
conclusively
demonstrated.
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5
2.3
EXHAUST
COLLECTION / DIFFUSION AND EXIT TO ATMOSPHERE
The bulk
mass flow of the working fluid through the various turns and cross-sectional
changes
encountered
while the working fluid is exhausted to atmosphere can cause flow-generated
pressure
fluctuations.
These pressure fluctuations can be from flow vortices around edges, flow
separations from
transitions
and bends, or flow interaction with stationary bodies. Flow-generated pressure
fluctuations
can be
significantly stronger than the pre-existing pressure fluctuations from the
combustor, although the
frequency
of flow-generated noise in exhaust systems is normally very low. A theoretically
perfect
diffusion
of the exhaust gasses to atmosphere can eliminate this source of noise.
The nature
of the combustion process and the exhaust diffusion to atmosphere (Figure 5) in
a practical
installation
invariably causes significant turbulence and pressure fluctuations. These
pressure
fluctuations
are an additional source of acoustic noise over the existing combustion noise.
Figure
5. Typical Exhaust Diffuser / Collector, (J. Liu and C. Twardochleb, 2001)
COMBUSTOR
HOUSING
INJECTOR
FLANGES
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6
Jet noise
occurs because the boundary of stationary and moving flow generates vortices and
corresponding
pressure fluctuations. The relative difference in speeds of the two gasses is
the significant
factor. In
most instances, there should be very little contribution of jet noise for Mach
numbers in the
range of
values typically seen in the exhausts of industrial gas turbine
installations. Jet noise can be a
contributor
when a high-pressure reservoir is bled to atmosphere, such as during blow down
or bleed
valve
actuation.
Flow-generated
noise can become significant at typical exhaust velocities when extensive
silencing is
employed
and the residual silenced noise levels are low. Noise is “regenerated” by
the flow as it passes
through the
silencers, if the residual noise levels after silencing are low enough there may
be some flow
generated
contribution to the net noise levels at the exhaust to atmosphere.
As stated
previously, the exit to atmosphere introduces the existing exhaust noise into a
reacting medium
and noise
is transmitted to atmosphere. This is often the primary mode of noise
transmission from the
exhaust.
2.4
CASING
The engine
"casing" is usually referred to as a significant source of noise and
included in noise source
disclosures
by equipment manufacturers.
In general,
the casings contain the working fluid and fuels of the gas
turbine and, as a result, are in
direct
contact
with the pressure fluctuations that are generated in the working fluid and fuels
by the means
described
previously. The casings are then a means of noise transmission through their own
structural
responses.
The casings often serve as bearing housings (or load paths) and can transmit
noise
generated
in the bearings.
Practically,
there is less significance to the casing contributions of noise in industrial gas
turbines
because,
while the basic mechanisms of noise generation are present, the overall
contribution to the net
noise
levels is usually small. The primary reason that the casing contribution is
small is that the relatively
heavy-walled
casings have significant transmission losses, while the openings at the inlet
and the
exhaust
have little or no transmission loss. The result is that the contribution of the
openings of the inlet
and exhaust
are large in comparison. Also, it is common in industrial gas
turbines to have a thin gauge
sheet metal
housing on the inlet and exhaust. This thin sheet transmits noise more
effectively than the
heavy
castings of the casing.
True casing
noise levels in industrial gas turbines are
very difficult to obtain and the overall noise levels
around the
entire package (less the direct contribution of inlet and exhaust openings) are
considered as
the casing
contribution.
2.5
SUPPORTING
EQUIPMENT
Industrial gas
turbines use supporting equipment that can itself be the source of noise. The
top
contributors
are oil coolers, pneumatic starters, driven equipment, and lube oil pumps.
In
addition, the equipment associated with the gas
compression process (piping, coolers and valves) are
also
significant contributors of noise.
Coolers,
whether they cool oil or gas, usually have
fans, which are generally the primary source of noise.
The coolers
can also radiate noise from their structures, which is generated by the fluid
that is within the
heat
exchanger. Most often, the net contribution of noise is by both sources. The
fans and their drives
are the
primary source of noise in most cases.
Pneumatic
starters can be significant noise sources, but are transient in nature. Lube oil
pumps generate
noise by
causing significant fluid-borne pressure fluctuations, which radiate through
piping and supports.
The
pressure fluctuations are caused by the basic working mechanisms (gear meshes,
for example) of
the pumps
and are the source of fluid-borne noise. Pumps can also cause cavitation,
although this is
usually not
the most significant source of noise generation.
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7
Piping that
carries the process gas transmits noise
generated by the compression process. The gas
carries
with it the pressure fluctuations and transmits the fluctuations to any surface
it comes into contact
with.
Piping mounts can transmit the vibrations to the foundations or mounting
supports causing the entire
foundation
to be a source of noise.
Process
valves generate noise associated with their operation. The noise is typically
generated within the
body of the
valve, transmitted to the casing and then into the surroundings. The valve
generated pressure
fluctuations
can be carried with the fluid itself and in the same fashion as the process gas
in the above
paragraph,
can become a significant noise source in addition to the valve body itself.
Driven
equipment such as centrifugal gas compressors
or gearboxes can be significant sources of noise.
Gas compressors generate noise in the diffusion of the gas
(particularly if the diffusers are vaned). The
noise from
centrifugal gas compressors is mostly tonal
and fluid borne, the cases are usually heavy
enough so
that they are less significant contributors. Exceptions do exist however.
Gearboxes
can be the source of noise primarily resulting from the bearings and the gears
themselves.
These types
of machinery elements involve unsteady forces induced in part by the practical
limits of their
machining
tolerances. These unsteady forces get transmitted to whatever load paths exist.
When the
forces are
exposed to a reacting medium (such as air), the result is pressure fluctuations,
which are the
source of
airborne noise.
3.0
TYPICAL
NOISE CONSTRAINTS ON TURBOMACHINERY INSTALLATIONS
The Federal
Energy Regulatory Commission or FERC regulates any domestic interstate pipeline.
FERC
regulates
compression installations to a sound pressure level of 55 dBA, Ldn. The term
"Ldn" refers to a
day and
night weighted average that, when continuous sources are considered, equates to
a sound
pressure
level of 48 dBA. This criterion is typically applied to the property boundary or
the nearest noise
sensitive
area (NSA) or both. If the facility is not part of an interstate network, it can
be regulated on local
or state
levels and these criteria are normally applied to the property boundary.
International
criteria are similar in concept, but vary widely in the required sound levels.
The basic
underlying
principle in all cases is to avoid disturbing the surroundings beyond some
"acceptable" limit.
In addition
to property boundary or NSA type criteria, there may be the need to control the
noise levels at
specific
locations within the installation. Almost invariably, the basic 85 dBA sound
pressure level at one
meter
distance criterion is the basis used to establish equipment noise limits. The 85
dBA criterion stems
from a
health and safety aspect. It is based on an acceptable dosage concept and
applies only to
workplace
sound levels. It is mistakenly used as an equipment noise criterion in the hopes
of achieving
compliance
in the workplace, (Johnson, 2000).
These two
methods of establishing criteria are the common recurring themes in the practice
of noise
control of
industrial equipment.
The two
previously mentioned methods of establishing criteria are sometimes taken in
conjunction and
the
requirement is simply stated to meet the lowest of all criteria for any
particular location in the
installation.
The importance of establishing the correct criteria for each particular
installation cannot be
overemphasized.
Problems often arise when all aspects of increasing the site noise levels are
not
considered.
4.0
STEPS TO
ACHIEVE NOISE CONTROL GOALS
The steps
used to control the various sources of noise are all based on the fundamental
relationships
between
each source and its path to the receiver. In addition, a criterion or noise
limit (for all sources) at
the
receiver needs to be identified.
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8
The
source-path-receiver concept of noise control is applied to each of the
contributing sources in a
method
consistent with the characteristics of each source and its path to the receiver.
The primary
path in property boundary criteria is usually airborne noise that emanates from
the gas
turbine intake and exhaust, oil cooler, process gas
piping and valves and process gas coolers.
The gas
turbine casing is enclosed in either a building or a close-fitting
acoustic enclosure. Driven equipment is
often
enclosed in a similar manner.
Variations
on the theme revolve around additional treatment methods. Close-fitting acoustic
enclosures
may
themselves be placed within acoustically treated buildings. Walls or vegetation
barriers may be
used.
Occasionally, the driven equipment is unenclosed for maintenance reasons.
Table 1
lists typical sources encountered in an industrial gas turbine
installation and the most common
treatments
associated with each.
Table
1. Typical Sources and Treatments for Industrial Gas Turbine
Noise
Source
Description
Typical
Treatment
Axial
Compressor
·
Package Enclosure
·
In-Duct
Dissipative Silencer
·
External Lagging
Combustor
Housing
·
Package Enclosure
·
External Lagging
·
Mechanical
Isolation
Exhaust to
Atmosphere
·
In-Duct
Dissipative Silencer
·
Direct Stack Exit
Away from Receiver
·
External Lagging
·
In-Duct Reactive
Silencer
·
Mechanical
Isolation
Gas Turbine
Casing
·
Package Enclosure
·
Offskid Building
·
Both of the Above
Lube Oil or
Process Coolers
·
Reduce Fan Tip
Speed
·
Enclosure
Process
Piping
·
Bury
·
External Lagging
·
In-Line
Dissipative Silencer
·
Mechanical
Isolation
Gearboxes
·
Package Enclosure
·
External Lagging
The most
significant elements of noise control are proper source identification and
source noise level
evaluations.
Source noise levels need to be established prior to implementing abatement
measures. The
“unsilenced”
(data taken without the presence of a silencer) noise data must be of high
quality to achieve
reliable
results.
The most
useful and reliable source noise data are those obtained under the strict
adherence to
recognized
standards.
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9
5.0
VERIFICATION
MEASUREMENTS
Verification
of the steps used to control noise is generally a component of meeting the
regulatory
obligations
made to the controlling authority.
Verification
measurements should follow the agreed upon criteria at the agreed upon
locations. Typical
measurements
(Figure 6) are made with integrating sound level meters of various types.
Spectrum
analyzers
may be required in cases where the frequency content, as well as the overall
sound pressure
level, is
part of the criteria. Spectrum analyzers are also indispensable when attempting
to isolate
sources and
contributing factors.
The general
practice of taking measurements should be based on recognized standards wherever
possible.
Examples of existing standards for gas turbine
installations can be found in the references
listed in
Section 8.0 in this paper. In many cases, no real standard will exist to cover
the specific needs of
an
installation and, in these cases, the verification measurements need to be taken
in a previously agreed
upon
fashion.
Figure
6. Typical Instrumentation. From left, B&K 2144, _” microphone, B&K
2230 and B&K 2260
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10
It is not
unusual for verification measurements in general to have some predefined
tolerance. For some
unknown
reason, noise criteria are typically taken as an upper limit. It is often
unacceptable to claim that
the
requirements have been met if the agreed upon limit is even slightly exceeded by
the verification
measurements.
The process of collecting noise data inherently involves tolerances. The reality
of the
conflicts
between the "upper limit" mentality and the inherent tolerances
involved in collecting the data is a
frequent
cause of concern. Inevitably, the practicing noise control engineer learns how
to cope with the
tolerances
while meeting the "upper limit" expectations, (Johnson, 2001).
6.0
PRACTICAL
LIMITATIONS OF VERIFICATION MEASUREMENTS
Unfortunately,
noise measurements can be difficult or impossible to be used verbatim to show
compliance.
There can be several reasons for this, but the biggest reason is normally that
the equipment
supplier is
only interested in verifying their own equipment and the measurements almost
always include
some
environmental influences. Obviously, verification measurements could be made in
a controlled
environment,
such as an anechoic chamber, but that is impractical and expensive.
Industrial gas
turbines are no exception to being impractical candidates for anechoic
measurements and
the
applications they find themselves in typically do not warrant the extra costs
involved, even if anechoic
measurements
are possible.
Measurements
are usually taken when the equipment is installed and all other supporting
equipment is
fully
operating. As discussed above, the sound fields become complicated as a result
of additional
sources,
reflecting surfaces, weather effects, other human activity, and wildlife.
The task of
the noise control engineer in these situations is to make as much effort as
possible to obtain
useful data
that can be used to show compliance (or to offer recommendations for
remediation)
analytically.
This is an inherently difficult proposition because the client may or may not be
inclined to
accept the
analysis when measured data are available. Carefully isolating each component of
a
contributing
source is often necessary.
Several
test standards exist for field measurements of industrial gas
turbines, [1,2,3,4,5]. It is necessary
to agree up
front upon the types of measurements to be made and the limitations that can
arise from
them. If a
manufacturer declines to use a recognized standard in its equipment noise
declarations, the
manufacturer
should at least propose an explanation of how the data were derived.
Verification should
then
proceed in the same manner as was used to generate the data.
If the
criteria were incorrectly chosen, there may be no possible way to make
verification measurements.
For
example, the criteria may be such that the sound levels to be verified were
significantly below the
ambient
sound levels. It is rare to find a place that has ambient sound levels lower
than 35 dBA at any
time of the
night or day.
Several
techniques are available to the noise control engineer when trying to make good
verification
measurements.
A few of these techniques are described in the standards. Perhaps the most
useful
technique
is to simply get closer to the source that needs to be isolated while taking
narrow band data, (at
least 1/3
octave). This can be done in several steps so that the change in frequency
spectrum, as well as
the overall
change in amplitude, can be observed as the measurements get closer to the
source.
Shielding
sources can be a valuable tool in determining the effects of the source. A
position can usually
be found
that shields one or more of the contributing sources and, by a process of
elimination using the
shielded
frequency spectrum of various positions, the relative contribution of each
source can then be
determined.
Another
promising method is the use of sound intensity evaluations. A commonly used
standard for
making
sound intensity evaluations is ISO 9614, [2]. Sound intensity evaluations
involve two
microphones
making simultaneous readings. The difference in the readings is then analyzed to
determine
the direction as well as the magnitude of the sound field. Using sound intensity
evaluations
can help
isolate individual sources. The main drawbacks to intensity evaluations are the
inherent
complexity
of the method and the need for evaluation of several data quality indicators. If
the data quality
indicators
are not monitored carefully, the usefulness of the measurements is doubtful.
Sound intensity
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11
evaluations
have not been as widely used as “normal” sound pressure level measurements
and there
does not
seem to be a great deal of momentum towards using sound intensity evaluations
over sound
pressure
level measurements.
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