HomeMy WebLinkAboutSP202100004 Study 2021-08-164;1;<<• A C E N T E C H
August 11, 2021
Charles D'Angelo
Clifton Management LLC
4 Warwick Road
Summit NJ 07901
cdangelo(weStmountcapltalgroup. com
Subject Review of Sound Propagation from Proposed Event Site
Special Event Venue, Collina Farm, Charlottesville, VA
Acentech Project No. 634629, Revision 2
Dear Mr. D'Angelo:
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2150 Wise Street #5852♦♦♦-'
Charlottesville, VA 22905
434 218 0759
acentech.com
Thank you for taking the time to discuss your project and getting me in touch with your engineering team and
the staff onsite at The Clifton. This review outlines our understanding of your project, our assumptions
regarding sound source levels and placement, and details the associated modeling and prediction of sound
levels throughout the site. A brief glossary is included at the end of this letter.
EXECUTIVE SUMMARY
Sound level predictions due to events at the new Collina Farm venue were made using measured sound levels
at the current Clifton event venue as reference. The Collina Farm venue is expected to include an event
structure with three walls comprised of roll -up style doors. Inside this structure the loudspeakers were placed
facing West-southwest with the western and southern doors rolled up (quasi -outdoor configuration). No review
has been made of amplified sound with all wall in place (indoor configuration), as the sound levels would be
much lower and the county's preliminary review only asked the applicant to study outdoor amplified sound.
Based on the results from this study, we expect that if the Collina Farm site is configured to meet all of our
assumptions outlined in this report, the predicted sound levels will meet the county's daytime noise limits and be
below 60 dBA at all property lines. However, in order to meet the nighttime noise limits at all locations the
volume of amplified sound would need to be reduced by roughly 5 dBA relative to typical events at the current
outdoor venue at The Clifton. Further details and analysis follow.
ALBEMARLE COUNTY NOISE ORDINANCE
We understand that your team has had discussions with Albemarle County staff, and you have been given
direction to conduct a noise study of outdoor amplified sound at the Collina Farm event venue for inclusion with
your application. As is typical for these types of projects, Albemarle County expects the noise study will
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The Clifton
August 11, 2021
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compare predicted sound levels due to these outdoor events with the maximum allowable sound levels 1. All of
the parcels adjacent to Collina Farm are zoned rural or residential and must meet the strictest of these limits.
For this type of zoning, the maximum allowable sound levels are defined as an equivalent continuous sound
pressure level (LAeq — essentially an average) of 60 dBA during the daytime and 55 dBA during the nighttime Z.
The Albemarle County Code includes additional details outlining the necessary equipment and measurement
procedure (for existing projects), applicable definitions, and source exemptions. Relevant exemptions include
transportation and a person's voice. Note that while amplified music is listed as exempt, we understand that
exemption does not apply to this use.
BACKGROUND
In the preliminary special use permit application your team has outlined where the event structure, campsites,
cabins, and bathhouse will go. Figure A shows this Collina Farm concept plan as outlined in the preliminary
SUP application.
Figure A: Collina Farm Concept Plan, Preliminary SUP appl
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We understand that the event structure will be enclosed, but that three of those walls may be comprised of roll -
up style doors to allow the outside in, with only the north wall being fixed. Since the event venue can essentially
transform into an outdoor venue, you have asked us to review the venue for compliance with the county's noise
'Albemarle County Code, Chapter 18, section 4.18.04, Noise.
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2 The county defines daytime as 7AM to 1OPM and nighttime as 1OPM to 7AM.
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ordinance limits. The major sources of sound due to events are expected to be voices from the gathered crowd
and amplified speech/music.
Sound Levels Measurements at The Clifton
While your upcoming special use permit is looking to add the event venue at Collina Farm, we undersand that
you are already operating events at The Clifton venue under a separate special use permit. This provided us
with an opportunity to measure source sound levels during some of these events for use in this review of Collina
Farm events.
We continuously measured sound levels at The Clifton's event venue from May 25 through May 31, 2021,
including two events with live bands and one with a DJ. These measurements were made approximately 90
feet from the edge of the stage using a class 1 certified sound level meter that was field calibrated at the time of
install. All three events had similar A -weighted, equivalent -continuous sound levels (LAeq) with around 85 dBA at
90 feet. However, as shown in Figure B below, the DJ generated significantly more low frequency sound (bass)
than the live bands did.
Figure B: Measured Sound Level Spectra During Events at The Clifton
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During the week preceding the events at The Clifton we were able to make ambient sound level measurements
at two locations on the property. The first was close the edge of the Collina Farm property near the top of Hurtts
Pond and the second close to the southeastern corner of The Clifton near the bottom of Hurtts Pond, as shown
in Figure C. These ambient sound level measurements should help to put the sound level predictions into
perspective — limiting project sound levels relative to ambient means a lower impact to the community.
Table 1 shows the measured sound levels at each location for four consecutive nights, when events might
typically take place. We understand that no events were taking place on these night and the ambient sound
level was consistently around 47 dBA for each night at both measurment locations. The historic weather report
shows that the temperatures were relatively mild, with little wind, and no precipitation. We expect the these
ambient sound levels are controlled by the general hum of traffic from nearby Interstate-64 and some insect
activity.
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Figure C: Ambient Sound Level Measurement Locations
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Location A • 11
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Table 1. Ambient Sound Level Measurement Results
Day and Time
Measured Sound Levels, LAey
Location A
Location B
Friday May 21, 7PM —11PM
49 dBA
48 dBA
Saturday May 22, 713M —11PM
46 dBA
49 dBA
Sunday May 23, 7PM —11PM
47 dBA
48 dBA
Monday May 24, 713M — 1113M
49 dBA
44 dBA
Energy Average of the Above Periods
48 dBA
47 dBA
Given the consistency in the ambient sound levels between these two locations, which are roughly 1h mile apart,
we expect these sound levels are characteristic of the ambient noise in the area surrounding the Collina Farm
and Clifton properties. We also expect that ambient sound levels will be higher at properties closer to the
interstate.
Amplified Sound at Collina Farm
In our experience amplified music and amplified speech are the loudest sources of noise at most events. We
generally see that typical sound pressure levels on the edge of a dance floor are often near 85 dBA and
increase to above 100 dBA as you move closer to the loudspeakers. For reference, 85 dBA is about the level of
a loud film in a movie theater, while 100 dBA would be similar to a dance club or louder fitness class, but quieter
than a rock concert. Note that these levels could fall in a wider range based on the performer/presenter's tastes
and their client's wishes.
In an effort to best represent the sound level from the types of events you will have at Collina Farm, we are able
to use the sound level measurements from The Clifton events as reference. The measured 85 dBA sound
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pressure levels at 90 feet from the loudspeakers equates to around 90 dBA at 50 feet 3, which is closer to the
dance floor, and will be better proxy location for monitoring of sound level compliance.
For our analysis, we have assumed a two -loudspeaker configuration using the measured sound level from The
Clifton events. The specific music played during a given event will dictate the frequency content of the
reproduced sound. For example, some music is bass heavy, while other music is not. While we cannot predict
the exact music that will be played, we have assumed an energy -averaged frequency distribution measured
from the two live bands.
Crowd Noise at Collina Farm
While a person's voice is exempt from the county's noise ordinance, it will always exist during an event. This
means that it is not easy, or practical, to remove a crowd's contribution from a measured sound pressure level,
making it difficult to show compliance with the noise ordinance of the non-exempt sources. Therefore, to be
thorough and to best reflect the constant sources of noise heard by neighbors, we have included predicted
crowd noise in our review.
Crowd noise can be very difficult to predict because there are so many independent variables. In an effort to
predict crowd noise we are relying on research 4 that characterizes the prediction of outdoor noise due to small
to medium sized crowds. Note that very little research has been completed on larger crowds and the paper we
have referenced limited their review to crowd sizes of up to only 100 people, which still makes it the best
resource we have for predicting noise from crowds of this size. Following the details outlined in this paper, the
crowd's equivalent continuous sound power level (LwAeq) has been predicted using the expected number of
people at the event. The prediction shows that the sound level will decrease by 4.5 dBA for each halving of
crowd size 5.
We understand that you are requesting approval for events of up to 300 people at the Collina Farm venue, so
that maximum attendance size has been used in our predictive model. The sound power level for 300 people
has been added inside the event structure for our predictions at Collina Farm. Note that this crowd noise
prediction is for the equivalent continuous level. However, crowd noise is transient and should be expected to
be higher and lower over time, such that the actual sound levels of a crowd vary.
Because the sound power level of the crowd is expected to be more than 20 dBA lower than that of the
amplified sound from the PA speakers, it will contribute very little to the highest sound levels generated during
an event on a longer -term LAeq basis.
SOUND LEVEL MODELING
We use a software package called CadnaA to build a model, predict noise levels, and present that data.
CadnaA is a widely recognized and accepted noise propagation modeling software that follows ISO 9613-2 6.
We were able to obtain public terrain data for the planned site and used Albemarle County GIS to identify
building locations and property boundaries. Using this data, we have built a noise propagation model of your
site for the purposes of sound level prediction.
Propagation Model Details
Buildings near sound source(s) were defined to provide reflection and shielding in the sound propagation path.
Elevation contours provided the necessary topographic information to predict spreading, ground and foliage
absorption, shielding, and diffraction. These physical conditions in the sound propagation path influence how
3 Resulting in a source sound Dower level (LwAQ of over 120 dBA re 1pW
4 Prediction of Noise from Small to Medium Sized Crowds. M.J. Hayne, at. al. ACOUSTICS 2011.
6 Crowd sound Dower levels are predicted to be about 101 dBA for 300 people and 96.5 dBA for 150 people.
6 International Standards Organization 9613-2, Attenuation of Sound during Propagation Outdoors.
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the sound is absorbed or reflected and ground conditions in particular can vary greatly for a given site. Collina
Farm is largely soft ground with ground absorption factors likely nearing 1. However, in an effort to be more
conservative in our predictions, we have chosen to model the general ground absorption factors as 0.5, midway
between reflective (0) and absorptive (1). Additionally, much of the project boundary includes the Rivanna River
and Hurtts Pond, which has been accounted for by including ground absorption factors of 0 (reflective) in those
areas. Foliage such as trees and bushes were included within and outside the project boundary in appropriate
regions because of the forest -like density of trees. Note that seasonal variations will occur, but the planned
outdoor uses would only take place in the warmer seasons when there is little variation.
Atmospheric attenuation of sound is somewhat influenced by temperature and relative humidity, but should not
have a large impact on our results. This is because lower frequencies and higher frequencies do not behave
the same for a given set of conditions. Because this study only reviews outdoor events at Collina Farm, we
expect they will primarily be in use during fair weather, so we have assumed a typical temperature of 80OF and a
relative humidity of 70%.
We have not accounted for the effects of temperature inversions, wind speed, and wind direction in the sound
propagation model. These variables require meteorological data specific to the site and further complicate the
predictions. Note that temperature inversions, where a layer of warm air covers cooler surface air, typically
occur near sunrise of clear and calm nights, when events will not be taking place. A review of typical weather
conditions on Weather Spark 7 shows that the warmer months, when events are expected to be held, have an
hourly mean wind speed below 4 mph (roughly 1.5 m/s), which should not be high enough to perceptibly change
the downwind sound level 8. Since the applicable wind correction factor would be small and based on actual
wind direction/speed, it has not been included in our model. This means that our model and predictions
represent the general wind conditions expected for this region.
Event Structure & Amplified Sound Sources
The event structure, in its proposed operating condition, would have three walls rolled up (west, south, and east)
and a standard fourth wall on the north side. However, because the nearest neighbors are to the east, and
sound from unamplified instruments is more omnidirectional than the main loudspeakers, we do not recommend
rolling up the east wall during the performance portion of the event.
We have modeled the event structure as reflective barrier walls to the north and east, a reflective floor and a 20'
high reflective ceiling inside the plan area of the 10,500 ft2 structure. We have assumed a pair of loudspeakers
placed 8 feet above the floor and located 10 feet from the east wall. These two sources were assigned a
standard PA loudspeaker directivity, pointed along the length of the structure (— west-southwest), and given a
frequency spectrum and sound level from the live band measurements made at The Clifton.
Noise Contour Maps
A noise contour map is a way of graphically representing the sound level of a particular site. They allow the
reviewer to quickly determine the approximate, predicted sound level at any given location in the model, and
determine expected compliance with the noise ordinance. In our model, the sound levels on the noise contour
maps are calculated on a 20-foot x 20-foot grid at a height of 5 feet, and further interpolated between points on
the grid. Sound level ranges are represented with bands of color. For our purposes, most color bands
represent a 5 dBA range, with individual noise contour lines (black) within each range representing 2.5 dBA
steps. Also on the noise contour maps are buildings shown as brown shapes and the property boundary shown
as a black line.
httos://weathersoark.com/y/20225(Averane-W eather-in-Charlottesville-Virainia-United-States-Year-Round#Sections-Wind
6 ISO 9613-2 states that the correction factor for wind is typically small and around 0 — 2 dBA. Any correction would cause a reduction in the
upwind sound level and an increase in the downwind sound level.
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SOUND LEVEL PREDICTIONS
Using the CadnaA model, we are able to predict sound levels and generate associated noise contour maps for
individual sound sources or groups of sources. In an effort to provide clarity to the sound sources at the Collina
Farm site we have create three variants, one with only sound due to the gathered crowd of 300 people, the next
with the addition of amplified sound at Clifton event reference levels, and finally the same but with amplified
sound reduced by 5 dBA. Table 2 shows the variant name, description, and referenced figures that are enclosed
with this report. The noise contour maps of these variants are discussed in further detail below.
TABLE 2: CONFIGURATION OF CADNAA NOISE MODEL VARIANTS
Variant #
Description
Noise Contours
1
Collina Farm — 300 Person Crowd
Figure 2
2
Collina Farm — Crowd & Amplified Sound
Figure 3
3
Collina Farm — Crowd & Reduced Level of Amplified Sound
Figure 4
The noise ordinance sound level limits are 60 dBA during the day and 55 dBA during the night (starting at
10PM). Color bands in the noise contour map represent sound levels. Any bands colored a shade of white,
gray, or green are predicted to be within the daytime and nighttime noise ordinance sound level limits (< 55
dBA). Yellow is the first band that is predicted to be within the daytime but not nighttime sound levels (55 — 60
dBA). Red, purple and blue represent areas of higher sound levels (> 60 dBA) that are predicted to exceed the
noise ordinance limits.
To determine compliance with the daytime noise ordinance sound level limits, simply verify that all bands of red
(> 60 dBA) are inside the property boundary. To determine compliance for nighttime use, simply verify that all
bands of yellow (> 55 dBA) are within the property boundary. Figure 1 shows the source locations inside the
Collina Farm event structure. Figures 2, 3, and 4 are the noise contour maps, set to the same zoom level for
each variant, and include rough approximations of nearby homes, buildings, and major roads for reference.
Variant 1— Collina Farm, 300 Person Crowd
This variant characterizes the impact of a crowd of 300 people centered in the event structure at Collina Farm,
with the west and south walls rolled up. Figure 1 shows the location of this crowd drawn as a red rectangle with
hatch marks. Figure 2 shows the noise contour map for this variant, which is predicted to produce sound levels
well within the noise ordinance sound level limits. The highest predicted property line sound levels are near 45
dBA across Hurtts Pond at the nearest eastern and southern properties, which are below the ambient sound
levels we measured and reported earlier in this review.
Variant 2 — Collina Farm, 300 Person Crowd & Amplified Sound
This variant characterizes the impact of the amplified sound and the large gathered crowd with the west and
south walls rolled up. Based on the proposed event structure, we have assumed that the loudspeaker locations
are on the east side of the venue. The music is expected to be loud near the loudspeakers, as is typical of such
events. As described in the sound level modeling section above, the sound level of each speaker is based on
reference measurements made at actual events at The Clifton, which were measured to be around 85 dBA at a
distance of 90 feet. Each loudspeaker was positioned as shown by the red plus symbols in Figure 1.
Figure 3 shows the noise contour map for this variant. The amplified sound system and crowd, as modeled, is
predicted to produce sound levels within the daytime noise ordinance sound level limits. The highest predicted
property line sound levels are around 56 dBA outside the western boundary of the Stone -Robinson Elementary
School. Beyond the property line to the south, as the elevation increases after traversing Hurtts Pond, the
sound levels are predicted to increase to nearly 58 dBA. The predicted sound levels do not meet the nighttime
sound level limit at these locations and exceed the measured ambient sound levels by around 10 dBA.
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Variant 3 — Collina Farm, 300 Person Crowd & Reduced Level of Amplified Sound
This variant is identical to variant 2, except the sound level of amplified sound level has been reduced by 5 dBA
to a level of 80 dBA at 90 feet (85 dBA at 50 feet, near the expected edge of a dance area).
Figure 4 shows the noise contour map for this variant. The 5 dBA reduction in amplified sound level resulted in
a 5 dBA reduction across the entire contour map. Beyond the western boundary with Stone -Robinson
Elementary School now peaks with around 51 dBA, while the area below the southern boundary across Hurtts
Pond is now around 53 dBA. The predicted sound levels meet both the daytime and nighttime noise limits at all
locations at or beyond the property boundary. Additionally, these loudest locations are predicted to be only 5
dBA above the measured ambient sound levels.
ADDITIONAL CONSIDERATIONS
Loudspeaker Orientation
Changes to the loudspeaker orientations and positions may change the noise contour maps for the site. Subtle
changes should not have a large impact on the contours, but you should make efforts to ensure that
loudspeakers are oriented and positioned roughly as shown. If significant changes to location or orientation are
made then we recommend the model be re -run with the updated details to review the noise contour maps to
verify the project maintains compliance with the noise ordinance.
DJ versus Live Band
As discussed in the Background section, the DJ and live bands had similar A -weighted sound levels. However,
the DJ generated significantly more bass, which is often found to cause higher amounts of annoyance since the
rhythmic beat of music is generally dominated by bass, and that will be the most identifiable part of distant
amplified music. Care could be taken to limit the amount of bass generated by a DJ.
Live music has an added variable of possible stage monitors and guitar amplifiers being introduced outside the
house sound system. Additionally, instruments such as drum kits have the potential of being quite loud even
when unamplified. The variability of stage monitor loudness might be most easily addressed by requiring
performers to use in -ear monitors. Bands should be informed of sound level restrictions and will be expected to
comply with any administrative requests.
Community Acceptance
As you might expect, a noise ordinance is not fully capable of characterizing a neighbor's acceptance of noise.
If community members have an adverse reaction to event sound, additional considerations can be made to
better address human acceptance of noise due to distant amplified music. These considerations can take the
form of a lower overall sound level from the source(s), defining specific sound levels that cannot be exceeded in
a given frequency band (such as limiting bass output), or closing the roll -up doors to take the party inside.
DISCUSSION & RECOMMENDATIONS
In summary, the sound level predictions including the exempt crowd noise and amplified sound meet the
daytime noise ordinance limits when using the typical source sound levels measured at current Clifton events.
To meet the nighttime sound level limits, we estimate that the amplified music at the Collina Farm events would
need to be lowered by 5 dBA (to around 85 dBA at 50 feet, from 90 dBA at 50 feet). You may also consider
ending amplified sound at 10PM (the start of nighttime) rather than the 11PM characteristic end time of Clifton
events. This would allow the events to only require compliance with the daytime noise ordinance limits and
more easily maintain margins between sound levels at1beyond the property line and the maximum allowable
sound levels. We recommend aiming to comply with the nighttime sound level limits as outlined above, and
limiting amplified sound to 85 dBA at 50 feet from the loudspeaker.
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Areas shown in the noise contour maps in medium green (45-50 dBA) are expected to have sound levels similar
to the ambient sound levels we measured and reported above. Light green areas (50-55 dBA) are expected to
have sound levels about 5 dBA above the ambient, and yellow areas (55-60 dBA) about 10 dB above ambient.
Based on the noise contour map, the majority of the area along and outside the project's property boundary is
expected to have event sound levels near or below ambient, though this does not imply inaudibility.
We recommend that the Collina Farm event space include a "house sound system,' including all electronics and
loudspeakers necessary for these events, and specifically including a closed -loop sound level limiter. We
recommend the CESVA LF010 sound level limiter, which measures the sound level in real-time and lowers the
volume as necessary when a preset sound level limit is exceeded. This unit will not only help to maintain
compliance with the sound level limits, but also provide a record of sound levels during an event and also help
to control bass generated by various types of performances (as was apparent between the measured events
that included a DJ and live bands at The Clifton). We also recommend that the stage monitors be of the in -ear
variety to minimize additional amplified sound that is outside the control of the CESVA limiter. We understand
that following our initial discussion of these recommendations, you are pro -actively working with an AV
integrator to design such a "house sound system," which will include the CESVA limiter.
As a condition of your special use permit approval you may be asked to provide some form of noise monitoring
to verify sound levels stay within the noise ordinance. The CESVA sound level limiter should be acceptable for
use as a proxy sound monitoring location when used in conjunction with the predicted noise contour maps
presented in this report — If limiting to 85 dBA at 50 feet from the loudspeakers, all noise ordinance limits are
expected to be met. Specific details of sound monitoring placement and acceptable levels will need to be
determined from our model and made in conjunction with the AV integrator and applicable architectural details
of the venue.
Finally, the model assumes all surface finishes in the event structure (walls, floor, and ceiling) are entirely
reflective. While this could be true, we don't expect that you'll be happy with the acoustics of the space and we
recommend adding acoustical treatment to the ceiling and north wall. Such treatment will be particularly
important when the weather won't allow the walls to be rolled up and the room becomes very reverberant due to
the hard surfaces of these walls — reverberant rooms have poor speech intelligibility. We are available to assist
you or your architect with the design of room acoustic treatments as a separate service.
I hope this letter provides you with the information that you need at this time. If you have any questions, please
feel free to contact me at bvoder(dacentech.com or 434.218.0759.
Sincerely,
Acentech Incorporated
Bill Yoder
Principal Scientist
cc: Kelsey Schlein (Shimp Engineering)
Valerie Long (Williams Mullen)
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August 11, 2021
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GLOSSARY OF ACOUSTICAL TERMS
We understand that acoustic terminology can be confusing. The following is a brief glossary of some acoustical
terms used in this report that you may find useful.
Ambient Sound
The sound due to environmental, traffic, or other nearby sources that are unrelated to the source(s) being
measured or characterized.
dB = decibels, dBA = decibels, A -weighted
Decibels (abbreviated dB) are used to measure the relative loudness of sound, based on a logarithmic scale.
For reference, normal human speech is in the range of 65 decibels, painful rock music may be more than 110
decibels, while aircraft noise may be as loud as 130 decibels. A -weighting filters the sound in a way that is
similar to human hearing, and was found to be correlated to annoyance from environmental sound. Hence, dBA
levels are often referenced in various acoustical standards. Note that a 10 dB increase in sound is associated
with a perceived doubling in sound level.
Directivity
The pattern in which sound radiates from a given source. This could be spherical, hemi-spherical, or some
other pattern. Directivity changes with frequency and is related to the size and shape of the source.
Frequency, Hz
The number of cycles or oscillations per second. Low frequency is associated with bass and are low pitch, while
higher frequencies are high pitched.
Leq
The equivalent continuous sound level, or energy -average sound level, over a defined measurement period.
Note that the sound level may be higher or lower during a given measurement period.
Octave Band
An octave band is a frequency band where the highest frequency is twice the lowest frequency, and
characterized by its center frequency. Bands are proportional in width, being wider at higher frequency.
Pink Noise
Noise in which each octave band has equal energy.
Propagation Loss
A reduction of sound energy due to distance, absorption, and other means.
Sound Power Level
This is the level used to define the amount of acoustic power generated by a particular sound source.
Sound Pressure Level
This is the level used to characterize the loudness of a sound at a specific location. In this review, sound
pressure is implied unless the language specifically indicates sound power.
Temperature inversion
A reversal of the normal behavior of temperature near the ground. This occurs when a layer of warmer air
covers a layer of cool air at the surface. This can allow sound to reflect off the warmer air and travel to a greater
distance.
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Figure 1: Collina Farm Expected Outdoor Venue, 300 Person Crowd and Loudspeaker Pair Locations
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