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VIBRATION REPORT
Vibration Existing Conditions and Expected Impacts:
Strong's Yacht Center — 5780 West Mill Road — Mattituck, NY
Prepared for:
Mr.Jeffrey Strong
Strong's Yacht Center
Engineers:
Sean Harkin
Sarah Babione
Dr. Bonnie Schnitta
November 3,2022
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Strong's Yacht Center—5780 West Mill Road—Mattituck, NY
Vibration Analysis Report— 11/3/22
TABLE OF CONTENTS:
Section 2.611—Executive Summary............................................................................................................3
Section l6.12—Equipment Utilized.............................................................................................................4
Section l6.12—Acoustic Criteria and Definitions........................................................................................4
Definitions..............................................................................................................................................4
VibrationCriteria....................................................................................................................................4
Section 3.6.14—Analysis of Vibration Data Collected..................................................................................6
Current Background Vibration Levels.....................................................................................................6
On Site Truck Data Collected..................................................................................................................9
Section I6.1G—Methodology for Analysis ................................................................................................10
FTAGuidelines Analysis........................................................................................................................10
ReferenceData Utilized........................................................................................................................11
Section 3.6.16—Potential Impact Analysis.................................................................................................12
Potential Impacts from Truck Vibration...............................................................................................13
Potential Impacts from Construction Vibration...................................................................................25
Section 3.6.17—Construction Vibration Monitoring Plan..........................................................................27
Vibration Monitoring Terminal Types and Locations...........................................................................27
Vibration Monitoring Thresholds.........................................................................................................28
Procedure for Potential Vibration Exceedances...................................................................................3U
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Vibration Analysis Report— 11/3/22
3.6.11 EXECUTIVE SUMMARY:
This document serves to summarize the evaluation of the existing acoustic conditions at Strong's Yacht
Center located at 5780 West Mill Road in Mattituck, NY ("Project Site") and provide analysis of the
expected vibration impacts to be incorporated into the SEQRA review. This vibration report addresses
concerns raised by the Town of Southold Planning Board and the New York State Historic Preservation
Office during review of the DEIS dated December 2021 regarding potential damage to historic structures
and impact to nearby residents from construction and truck traffic on local roads.
On August 2 d, 2022, SoundSense documented the existing vibration conditions at various locations near
the Project Site and vibration data from a representative truck expected to be used during construction.
The measurements collected provide a baseline for existing conditions and have been used in the
predictions completed for the Project. Predicted vibration levels were used in conjunction with the
methodology and data from the Federal Transportation Authority's 2018 Transit Noise and Vibration
Impact Assessment Manual ("FTA Guidelines") and the New Hampshire Department of Transportation's
2012 Ground Vibrations Emanating from Construction Equipment("New Hampshire Guidelines").A more
detailed description of the methodologies and analyses used can be found below in Section 3.6.15. The
predicted vibration compiled by SoundSense can be compared to the criteria provided in the FTA
Guidelines.
Analysis of the construction equipment has shown that there is no predicted impact to any nearby
neighbors.Additionally, using the data collected near the Project Site,there is no predicted impact to any
nearby historic structures from truck traffic. All the data collected during the site visit is well below the
threshold at which vibration would cause damage to a historic structure, which would be 0.12 in/s. This
conclusion was tested against the worst-case scenario using the reference data and calculation
methodology presented in the FTA guidelines detailed further in Section 3.6.15. The worst-case
conclusion was that there is a potential impact from truck traffic to the historic Water Tower and Building
located at 3380 W Mill Road in Mattituck,NY.These reference values,equations,and methodologies were
developed to be used throughout the United States and do not take Long Island's unique soil structure
into account. While there is no impact anticipated using the data collected on site, the risk of potential
vibration in the worst-case scenario is identified in this report. To ensure that vibration is responsibly
managed,the Applicant has committed to implementing a vibration monitoring plan during construction
at the Project Site to protect nearby historic structures of concern and ensure that ground-borne
vibrations are not a disturbance to nearby neighbors. Details on a vibration monitoring plan have been
provided in this vibration report in Section 3.6.17.
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Vibration Analysis Report— 11/3/22
SECTION 3.6.12-EQUIPMENT:
• Frequency Analyzer: Bruel & Kjaer Model 2250L,Serial No. 3009718
• Accelerometer: Bruel & Kjaer Model 4533-B-002,Serial No. 30014
SECTION 3.6.13—VIBRATION CRITERIA AND DEFINITIONS:
Definitions
Peak Particle Velocity (PPV)
The peak particle velocity is the maximum peak of the vibration signal. This metric is typically used to
evaluate stresses related to building damage. As defined in the Federal Transit Administration's Transit
Noise and Vibration Impact Assessment Manual.
RMS Velocity
The RMS velocity is used to describe a smoothed vibration signal and is used to evaluate human response
to vibration levels.The RMS is equivalent to the square root of the average of the average of the squared
level of the signal and is typically equivalent to 0.707 of a signal's peak. The RMS velocity is calculated in
decibels relative to 1 micro-inch per second and is typically noted in VdB. In this document all VdB values
are vibration levels in decibels with a reference quantity of 1 micro-in/sec.
Accelerometer
An accelerometer is a sensor used to measure acceleration at a given location. Due to the mathematical
relationships between acceleration, velocity, and displacement, velocity measurements are easily
calculated by converting the measured acceleration.
Vibration Criteria
FTA Guidelines Vibration Criteria
It is common to use the FTA Guidelines during vibration analyses for impact from transit projects or
construction as a benchmark for evaluation of vibration impact both for damage to structures as well as
impact to building occupants. Recommended design criteria to prevent damage to historic and residential
buildings can be found in Table 1,and criterion for impact to various structure types can be found in Table
2.
Table 1: Construction Vibration Damage Criteria from the FTA Guidelines
Building/Structural Category PPV, in/sec Approximate L,,*
I. Reinforced-concrete,steel,or timber(no plaster) 0.5 102
11. Engineered concrete and masonry(no plaster) 0.3 98
Ill. Non-engineered timber and masonry buildings 0.2 94
IV. Buildings extremely susceptible to vibration damage 1 0.12 90
*RMS velocity in decibels,VdB re 1 micro-in/sec
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SECTION 3.6.13—VIBRATION CRITERIA AND DEFINITIONS(Continued):
Definitions(Continued)
FTA Guidelines Vibration Criteria (Continued)
Table 2: Indoor Ground-Borne Vibration (GBV) Impact Criteria for General Vibration Assessment from
the FTA Guidelines
GBV Impact Levels(VdB)
Land Use Category
Frequent Events Occasional Events Infrequent Events
Category 1: Buildings where vibration
would interfere with interior 65 65 65
operations.
Category 2: Residences and buildings 72 75 80
where people normally sleep.
Category 3: Institutional land uses with 75 78 83
primarily daytime use.
For this analysis, buildings extremely susceptible to vibration damage, structural category IV as shown in
Table 1, will be used to evaluate predicted vibration to historic structures, while structural category III,
non-engineered timber, and masonry buildings will be used for evaluation of damage to residential
structures. For evaluation of the criteria presented in Table 2 for impact to occupants, category 2 for
residences with frequent events will be used.The FTA Guidelines define frequent events as more than 70
events per day and occasional events as between 30-70 events per day.There will be up to, but no more
than,40 truck trips per day during excavation,with a trip to and from the site.Consequently,the frequent
events category is appropriate and chosen since it would be worse case scenario. It should also be made
clear that using Category 1 is not appropriate for evaluation to residences.As noted by the FTA Guidelines,
Category 1 uses criteria including below the threshold of human annoyance but is used for high sensitivity
buildings such where vibration-sensitive research,hospitals,and universities conducting physical research
operations that has not been shown to correlation with building damage.
Town of Southold Vibration Criteria
Based on a review of the Town of Southold Town Code, there are no requirements related to vibration
limits on construction and vehicle traffic.Therefore, no Town of Southold codes have been considered in
this analysis.Analysis will be performed in accordance with the FTA Guidelines and additional information
in the New Hampshire Guidelines, which have also been consulted due to its additional research into
propagation of construction vibration over distance.
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Vibration Analysis Report— 11/3/22
SECTION 3.6.14—ANALYSIS OF EXISTING CONDITIONS:
Current Background Vibration Levels
To monitor vibration levels at the Project Site, a sound level meter and accelerometer were used to
measure ground vibration levels from traffic at four locations at or near the Project Site. To establish
background vibration levels, a frequency analyzer and accelerometer were used to measure existing
traffic vibration levels at each location. Figure 1 below shows each location where measurements were
collected during the site visit on August 2nd, 2022. Locations 1 and 2 were measured at the Mattituck
Creek Tide Mill (Old Mill Restaurant) and the Frame Water Tower, respectively. As these locations are
connected to the road surface as noted in Figure 2, the accelerometer was adhered to concrete at the
foundation of the structure during the readings collected. Location 3 was as close to the southern property
line of the Project Site as possible, and Location 4 was located at the entrance to the Mill Road Preserve
at 25 feet from the roadway to match reference data presented in the FTA Guidelines(see Section 3.6.15).
At Locations 3 and 4,the accelerometer was attached to a 6" stake driven into the ground.A summary of
the measurements collected including PPV measurements can be found below in Table 3. No frequency
analyzer and accelerometer measurements were collected at the Water Tower and Building to be able to
collect readings along the unimpeded path through the soil to best determine the existing conditions.
Figure 1:Vibration Measurement Locations at the Project Site
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SECTION 3.6.14—ANALYSIS OF EXISTING CONDITIONS(Continued):
Current Background Vibration Levels(Continued)
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Figure 2:Accelerometer Installation at Location 2
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SECTION 3.6.14—ANALYSIS OF EXISTING CONDITIONS(Continued):
Current Background Vibration Levels(Continued)
Table 3: Summary of Background Vibration Data Collected on August 2"d, 2022
Ambient Peak Particle
Location RIMS L„(VdB)
Velocity(in/s)
Location 1 0.022 84
Location 2 0.009 76
Location 3' 0.011 78i
Location 4 0.007 74
All ambient readings were collected for 10 minutes each.Ambient PPV measurements collected occurred
during a vehicle passing at each location apart from Location 3 which was collected as a scissor lift was
operating near the measurement location as a part of the normal operation at the Project Site. As can be
seen in Table 3, vibration levels measured at all locations are below the 0.12 in/s which would be
necessary to cause damage to a historic structure, as previously stated as classified by FTA Guidelines.At
Location 4, traffic regularly passed on Cox Neck Road during the data collection period. During the data
collection,it was noted that passenger vehicles,construction vehicles,delivery trucks,and trucks all travel
on the local roads currently, which cause low levels of vibration transmission into nearby structures.
In addition to the low vibration levels measured during the data collection, it is known that soil
composition has a significant impact on vibration transmission into nearby structures. Long Island's sandy
soil structure efficiently reduces vibration over short distances. SoundSense has experienced this type of
vibration reduction numerous times when collecting measurements for passing railways where vibration
from a rail line may be of concern to a new structure under design.This is further validated by truck traffic
readings collected in the area.Vibration levels are consistently less than what would be predicted through
a standard calculation method that equates vibration solely on distance from vibration source to receiver.
Due to Long Island's unique soil composition, these site measurements that can help to determine the
vibration level in a specific region along with standardized methodologies from the FTA Guidelines and
New Hampshire Guidelines.
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SECTION 3.6.14—ANALYSIS OF EXISTING CONDITIONS(Continued):
On Site Truck Data Collection
Given Long Island's unique soil structure, it was important to collect vibration readings of truck activity
near the Project Site to determine the level of vibration transmission into any nearby residential and
historic structures. To facilitate this, measurements of a truck like the ones to be used during the
excavation of the site were measured at 25 feet from the road surface to be comparable to the data
presented in the FTA Guidelines,which are presented in Table S.Vibration data from a Peterbilt 389 2020
edition dump truck with a Paccar MX13 engine passing by Locations 1-4 was collected. The dump truck
was loaded with 39 tons of sand/dirt at the time of the readings, which is equivalent to 28-29 yards of
material. This truck is Tier 4 compliant with EPA standards, using the latest technology to reduce
environmental emissions. The truck operator was directed to operate the trucks as he would during
normal conditions and operation. For Locations 1 and 2, this meant passing by at 10-15 mph. The truck
operator conveyed that these slow speeds were necessary due to the decline coming into Strong's Yacht
Center from West Mill Road, as well as the curve at the bottom of the hill entering Strong's Yacht Center.
Data was collected with the trucks both entering and leaving Strong's Yacht Center. Data was also
collected from trucks moving northbound and southbound at Location 4 with the truck passing at 35 mph,
which is the speed limit on W Mill Road.The results of the data collected can be found below in Table 4.
Table 4:Vibration Readings Collected from Truck Passbys at the Project Site
Peak RMS
Location Description Particle Velocity
Velocity (VdB)
Location 1 Truck Entering the,Project Site 0.003 66
Truck Exiting the Project Site 0.002' 61
Location 2 Truck Entering the Project Site 0.004 68
Truck Exiting the Project Site 0.002 64
Truck Traveling South on W Mill Road 0.00"7 74
Location 4 Truck Traveling North on W Mill Road 0.006 73
All the data collected during the site visit is well below the threshold at which vibration would cause
damage to a historic structure, which would be 0.12 in/s. Although trucks can have higher airborne noise
levels than a passing car, they typically need to travel at a slower speed due to their size and weight,
especially when there is a road elevation change and curve in the road, as there is in this scenario. In
addition, the suspension and the tires of the trucks that will be utilized at the Project Site provide
additional vibration isolation from the body and engine of the truck itself and reduces vibration
transmission into the ground. As seen in Table 3, vibration levels of 0.022 in/s when there were no
construction vehicles of concern were measured at Location 1.This was during a car passing the location
at a higher speed. Since the structure has direct concrete connections with the road, there is little
vibration mitigation due to the soil. However,the slower speed needed for the trucks to navigate the area
will transmit less vibration into Locations 1 and 2 due to truck traffic associated with the Project Site. It
was also noted that the Mattituck Creek Tide Mill is proposed to go under renovation. Construction at
this location is anticipated to cause vibration levels in the structure higher than those associated with
trucks passing the location.
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SECTION 3.6.15—METHODOLOGY FOR ANALYSIS:
FTA Guidelines Analysis
The FTA Guidelines present an analysis methodology for prediction of vibration data over a specified
distance for both the PPV and the RMS vibration level.This equation can be used both for truck vibration
and construction vibration. Equation 1 below presents the equation for predicting PPV levels with
distance and Equation 2 presents the equation for predicting RMS vibration levels in VdB with distance.
25 1.5
PPVequip = PPVref * (D) Equation 1
where:
PPVequip =the peak particle velocity of the equipment adjusted for
distance in in/sec
PPVre f =the source reference vibration level at 25 feet
D =distance from the equipment to the receiver, in feet
Lndistance — Lvref — 30 log (D) Equation 2
where:
Lndistance =the RMS velocity level adjusted for distance,VdB
Lvre f =the source reference vibration level at 25 feet, VdB
D =distance from the equipment to the receiver, in feet
The velocity reference data noted above is provided in the FTA Guidelines and will be discussed further in
this section. Equation 1 can be used to predict PPV vibration levels at various distances to evaluate the
risk of potential damage to structures as provided in Table 1. In addition to the FTA Guidelines the State
of New Hampshire has published additional data and analysis which calls doubt into the FTA Guideline's
exponent of 1.5 used in the equation. While the FTA guidelines are meant to be used for a wide variety
of soil surfaces nationwide, and the work by the State of New Hampshire is unique to New Hampshire, it
has recommended using an exponent of 1.1 instead of 1.5.Although it has been established in this report
that Long Island's unique soil structure typically attenuates vibration more effectively than many other
soils of geological areas, the exponent of 1.1 has been used in Equation 1 to present a conservative
estimation of the predicted vibration levels at nearby structures. This modified equation can be found
below in Equation 3 for reference.
25 1.1
PPVequip = PPVref * —D
New Equation 3
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SECTION 3.6.15—METHODOLOGY FOR ANALYSIS(Continued):
FTA Guidelines Analysis(Continued)
Equation 2 can be used to predict RMS velocity levels at a given distance to compare to the criteria
provided in Table 2. However,the criteria provided in Table 2 relates to interior vibration levels. Equation
2 provides the vibration level in the ground at a given distance. There is an adjustment for observed
vibration transmission into a structure.The FTA Guidelines recommends the wood frame structures that
there is a 5 VdB reduction for vibration levels into the foundation of a wood-frame home, but that there
can also be an amplification of 3-6 VdB depending on the floor in the home where vibration levels are
observed. Therefore, the 5 VdB reduction and 3-6 VdB amplification result in a maximum possible
amplification of 1 VdB compared to ground borne vibration levels. 1 VdB has been added to all ground
borne vibration levels to provide a conservative estimation for estimation of interior RMS velocity levels
to compare to the criteria in Table 2.The modified equation for evaluation of RMS velocity levels can be
found below in Equation 4.
Lv.distance - Lvref — 30 log(') + 1 Equation 4
Using Equations 3 and 4,safe distances at which construction vibration would no longer be a concern for
structural damage or disturbance to occupants inside a structure both for truck traffic and operating
construction equipment. These safe distances and a discussion of any impacts can be found in Section
3.6.16. The only locations where these equations were not applied were Locations 1 and 2 since data of
a passing truck was directly measured at each of these locations. The FTA guidelines instruct the user to
evaluate each piece of equipment individually for their impact as combined vibration levels cannot be
reliably calculated. All calculations completed use the distance from the closest point of construction to
the closest point to the receiving structure.
Reference Data Utilized for Analysis
As noted above, the Equations 3 and 4 use reference vibration data which is provided in the FTA
Guidelines. Using the construction equipment list provided by Red Rock Industries, equivalent vibration
levels for each type of equipment were used. Where a similar equipment type was not provided, a
conservative piece of equipment was utilized which has a higher vibration level than what would be
anticipated.These vibration levels were utilized for the analysis to find the minimum safe distance from
vibrations due to truck traffic and construction activities. The reference vibration levels can be found
below in Table S.
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SECTION 3.6.15—METHODOLOGY FOR ANALYSIS(Continued):
Reference Data Utilized for Analysis(Continued)
Table 5: Reference Vibration Data Utilized for Analysis.
Construction FTA Guidelines PPV at 25 ft, in/s from Approximate RIMS
Equipment Type Equivalent FTA Guidelines Velocity(VdB)at 25 ft
Loader Large Bulldozer 0.089 87
Dozer Large Bulldozer 0.089 87
Excavator Large Bulldozer 0.089 87
Water/Fuel Truck Loaded Trucks 0.076 86
Tub Grinder Vibratory holler 0.21 94
Woodchipper Vibratory Roller 0.21 94
Feller Buncher Large Bulldozer 0.089 87
Scissor Lift Small Bulldozer 0.003 58
Dump Truck Idling Loaded Trucks 0.003 58
Telescopic Forklift Small Bulldozer 0.003 58
Measured Truck at _ 0.007 74
Location 4
As seen above, there is a significant difference in the expected vibration from a Loaded Truck and the
vibration from a truck measured at Location 4 during the data collection near the Project Site. This is
supportive of the previous discussion of the nature of the soil in the area and its ability to organically
reduce vibrations from any impact into the soil. Although it is likely that vibration levels at 25 feet will be
less for all equipment,the values provided from the FTA guidelines have remained as a part of the analysis
to ensure that the worst-case scenario is evaluated. Additionally, the Vibratory Roller has the highest
vibration levels of any piece of construction equipment presented in the FTA Guidelines other than pile
driving equipment. Since various pieces of equipment such as the Tub Grinder and Woodchipper do not
have equivalents in the FTA Guidelines, it was important to include a piece of equipment with a higher
vibration level to evaluate a worst-case scenario. No pile driving will be a component of the project and
is not of concern.
SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS:
Two concerns were raised regarding vibration by the State Historic Preservation Office (SHPO), as well as
the Town of Southold. These concerns include vibration transmission into historic structures causing
potential damage along the truck route and due to construction as well as impact to nearby residences
for both potential damage and disturbance during construction. Both impacts are discussed in the
sections below.
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS:
Potential Impacts from Truck Vibration
Although the soil in and around the Project Area significantly attenuates vibration over short periods of
distances, Equations 3 and 4 were used to evaluate the minimum distance from trucks which would not
cause damage to historic and residential structures as well as impact to nearby residences as defined in
Table 2.The minimum distances can be found below in Table 6.
Table 6: Minimum Distances to Meet Vibration Criteria
Minimum Minimum Minimum
Distance to Cause Distance to Cause Distance to Meet
Description No Damage to No Damage to Recommended
Historic Structures Residential Indoor Vibration
(ft) Structures(ft) Levels(ft)
Loaded Truck from FTA Guidelines 17 11 79
Measured Truck at Location 4 2 21 29
Based on the data collected and calculations provided,it is anticipated that the minimum distance to meet
the criteria would be 17 feet based on the data collected and 79 feet based on a worst-case scenario using
the federally standardized FTA Guidelines methodology and Equation 3.Although several residences have
structures which are closer than 79 feet from the roadway,no residences along W Mill Road and Cox Neck
Road have distances closer than 29 feet from the roadway. Although this presents a potential quality of
life impact for homes with distances of less than 125 feet from the road, it should be noted that the
ambient PPV data collected from typical vehicle traffic on W Mill Road elicited similar vibration readings
to the truck passbys. Therefore, while there is a potential quality of life impact for truck traffic impact,
that impact is no greater than the existing typical vehicle passbys which are already using W Mill Road
and would therefore be no different than any vibration transmitted currently.
Once vehicles turn off W Mill Road and Cox Neck Road, and travel along Sound Avenue, Northville
Turnpike, and Route 58,there is also already existing significant truck traffic.A letter was provided to the
applicant from Benimax, Inc. a local trucking company noting that Benimax transports up to 500 tons of
materials including sand,stone, asphalt,and concrete to the North Fork daily. It is noted that the 500 tons
is equivalent to 14 tractor trailer loads of materials. Benimax notes that they use State Route 25, County
Road 48, Sound Avenue, Northville Turnpike, and Country Road 58 on a regular basis for their trucking
routes.These are metrics for only one of the trucking providers serving the area. Additional truck traffic
from other trucking providers would send additional traffic into the area daily. Therefore, truck traffic
along these roadways and associated vibration from loaded trucks is already a part of the existing
conditions of these areas.
For any potential damage to historic structures, worst-case scenario calculations conclude that a
minimum distance of 17 feet would be required from the roadway surface. However, based on the
vibration data collected near the Project Site, the distance would be 2 feet. For damage to residential
structures, the worst-case scenario for damage would be 11 feet and based on the data collected near
the Project Site,would be 2 feet. P.W.Grosser has compiled a list of historic structures along the trucking
route. A table identifying these historic structures has been included in Table 7. The figures prepared by
P.W. Grosser noting the location of each of the historic structures can be found in Figures 3-11 for
reference.
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Table 7: Potential, Eligible, and Listed Historic Structures and Their Distances to Roadway Surfaces
Map Structure Address Distance from Road Historic Status
Marking Surface (ft)
Mattituck Creek 5575 W Mill Rd- Connected to Road
1 Surface-Vibration Eligible
Tide Mill Mattituck, NY Measured
5670 W Mill Rd - Connected to Road
2 Frame Water Tower Mattituck, NY Surface-Vibration Undetermined
Measured
Robinson-D-Aires 5109 W Mill Rd -
3 58 Undetermined
House Mattituck, NY
4 Water Tower and 3380 W Mill Rd - 12—To Closest Point of Eligible
Building Mattituck, NY Water Tower Foundation g
Cox-Forman 100 W Mill Rd-
5 45 Undetermined
Carriage House Mattituck, NY
6 Luther Cox House 3539 Cox Neck Rd - 842 Undetermined
Mattituck, NY
Hallock Kirkup 4995 Sound Ave
7 46 Undetermined
House Mattituck, NY
Charles Aldrich 4100 Aldrich Ln Ext
8 47 Undetermined
House - Mattituck, NY
Reeve-Jens(II) 1150 Sound Ave
9 42 Undetermined
House Mattituck, NY
10 Howell House 125 Sound Ave- 79 Eligible
Mattituck, NY
Eugene Hallock 6038 Sound Ave-
11 House Riverhead, NY 74 Listed
12 Old Hallock 5976 Sound Aver 45 Eligible
Homestead Riverhead, NY
Harrison Downs 5793 Sound Ave-
13 House&Farm Riverhead, NY 160 Listed
14 George Luce House 5570 Sound Ave- 58 Eligible
Riverhead, NY
Daniel T. Luce 5528 Sound Ave-
15 58 Eligible
House Riverhead, NY
16 Salem Wells House 5412 Sound Ave - 38 Eligible
Riverhead, NY
17 Jabez Corwin House 5331 Sound Ave 58 Eligible
Riverhead, NY
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Vibration Analysis Report— 11/3/22
SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Table 7 Continued: Potential, Eligible, and Listed Historic Structures and Their Distances to Roadway
Surfaces
Map Structure Address Distance from Road Historic Status
Marking Surface
5298 Sound Ave-
18 John Luce House 34 Eligible
Riverhead, NY
Northville Academy
52 Sound Ave-
Riverhead,19 (Congregation v 63 ft Eligible
Church Parish Hall) erhead, NY
Sound Ave 5267 Sound Ave-
20 Congregational 77 ft Eligible
Church Riverhead, NY
Sound Ave 5258 Sound Ave-
21 Congregational 46 ft Eligible
Church Parsonage Riverhead, NY
George Mitchell 5185 Sound Ave
22 Terry House Riverhead, NY 56 ft ' Eligible
23 James Harvey 5161 Sound Aver 94 ft Eligible
Benjamin House Riverhead, NY
Thomas Wardle 5144 Sound Ave
24 House Riverhead, NY 37 ft ' Eligible
25 Buel Wells House 5074 Sound Ave 48 ft Eligible
Riverhead, NY
26 Daniel Wells House 5004 Sound Ave-Riverhead, NY 38 ft Eligible
27 Joshua Minor Wells 4933 Sound Aver 39 ft Eligible
House Riverhead, NY
Wheeler Wells 4928 Sound Ave-
28 House Riverhead, NY 91 ft Eligible
29 Hallock Luce House 4778 Sound Ave- 67 ft Eligible
Riverhead, NY
Mitchel Terry 4624 Sound Ave-
30 House Riverhead, NY 32 ft Eligible
31 District#10 School No Longer on N/A Eligible
House Sound Avenue
McCabe-McKay 219 A Middle Rd '-
32 111 ft ' Undetermined
Farm Riverhead, NY
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Figure 3: Potential, Eligible, and Listed Historic Structures on W Mill Road
i; u re I Legend
w NbU Rd Strong's Yacht tenter
Historic Structures E9lebls
9-Matfitask Creek Tide 69i t7ldAt3d Undsterrnined
Restaurant).5775 w MJ#Rd
s Lwsted
2-France water Tower-West Mill Rd
arl'i it 1° r"
3-Robinson D,A.ires House-.1980 Mill Rd
t
4-water Tourer and Building 3380 west.
htlll Road "f
5-Cox-Forman Carriage Nor se
(Residence)-100 Mill Rd
St`
t
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Figure 4: Potential, Eligible, and Listed Historic Structures on Bergen Avenue
Legend
t
NCB i-iistoric
trurss Found
r u V
P
y ;i
3.a' 21t
}
e+ u
1,
ro
3•
S
t
1
a MV
1
y) t F
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Figure 5: Potential, Eligible, and Listed Historic Structures on Cox Neck Road
Figure 3 Legend
Cox Neck Ltd
istorc Structures
6.Luther Cox douse»3539 Cox fleck Ru
ti
1,.4
� f
p ,
1 l+ y
n, t
tr'
x
�t
tt
s
vh`
U�
a
w 4 it a
w,
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Figure 6: Potential, Eligible, and Listed Historic Structures on Sound Avenue from Cox Neck Road to
Herricks Lane
Figure 4 Lt1
SouDd Ave:
Cos clock Rd to Heim",Ln Eligible
t3ndetermined
T-Hallook Kirkup House•4995 Bound Ave
I_iskeeS
8-Charles Aldrich Howse-Sound Ave
9-Roav -Jens(11)Hooso-Sound Ave
t
10-Nowell House-125 Sound Ave
11-Eugene Hallock Huse•Sound,
12-alit Hallook Hornestead-6838 Bound Ave
8
at,
r c
a,
�y
r
P;u
ti
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Figure 7: Potential, Eligible, and Listed Historic Structures on Sound Avenue from Herricks Lane to
Church Lane
t�
Figure Legend
una Ave
Hera cks LP to Church Ln(Rt 23)
storic troctartrs h5
�M �� ;�s,. UradeCarmrred
13-Hearison Downs House&Farm-5793 Sound Ave �usaed
14-George Luce House-6379 Sera#Ave
15-Daniel T.Lug House-65528 Sound Forte G
16-Ss1ery Waft House-123 Sound Ave
5f
57-Janos Conrtin House-Sound Five
5,.
18-John Luce House-Sound Ave � �
5
a
3
J
ti-
ti
r !
vv
r
� � 5
arr
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Vibration Analysis Report— 11/3/22
SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Impacts Due to Truck Traffic(Continued)
Figure 8: Potential, Eligible, and Listed Historic Structures on Sound Avenue from Church Lane to
Northville Turnpike
Figure` Legend
j
Sound Ave
Church Ln(Fit 23)to Nowthvt#e 7gtk Eligt@31e
Undeferminecl .
Lasted
J�
a, S
t
a
n.
n P5.
h
;,�'I19�OPi��twructtorB�
19-Northville Academy(Congregation CPrurcF F'arlst Hall j-SocrzS Awe 2fi-Ctanlel WUells tic use-t00 e urot Ave
20-Sound Ave Congregational Church-Sound,Ave 27-Joshua dinar Wells House-104 Sound Ave
21-Sound Ave Congregational Church Parsonage age-Sound Ave 28-Wheeler Shells House-99 Sound Ave
22 George Mitchell Terry House-113 Sound Ave 29-Halloclr Luce House-.97 sound Ave
23-lames Harvey Benjamin House-111 Sound Ave j 30'-Mitchel Terry House-'113 Sound Ave
t
24-Thomas Wardle House-109 Sound Ave i 31-Distract#10 School House. Sound Ave
5-Suel Wells Howse-108 Sound Ave
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Figure 9: Potential, Eligible, and Listed Historic Structures on Northville Turnpike from Sound Ave to
Doctors Path
Figure 7 Ltd
Sound Ate to 6autc F�t� „ � �,>, Na Historic
y.
t a Structures Found
u'
c s
v
1
z
�sr 1
� o
Rx„
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Vibration Analysis Report— 11/3/22
SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Figure 10: Potential, Eligible, and Listed Historic Structures on Northville Turnpike from Doctors Path to
Old Country Road (Route 58)
Figure 8 Legend
Nord wkeTp4
1)Detars Path to old CountryRd(Fat )
j
1 INS
ua�determmed
s
Historic Structures t i51e t
32-Mcccabe-Mekay Far - t 9 A Cvtie�dle art
t
s
a
u � �
q4
St
7`
?is.
qz
a,.
F
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Truck Vibration (Continued)
Figure 11: Potential, Eligible, and Listed Historic Structures from Route 58 to the Long Island Expressway
Legend
PJc�Historic
5trxackures Freund
3
As noted in Table 7,only the Water Tower and Building located at 3380 W Mill Road would fall within the
worst-case scenario threshold of 17 feet for potential damage to historic structures as calculated through
Equation 3. However, as with impact to residences, the data collected on W Mill Road clearly shows that
the structure would need to be located 2 feet from the road surface to cause any potential damage.
Furthermore, Location 4, where data was collected is only 950 feet away from the Water Tower and
Building and is anticipated to be analogous to the conditions at the Water Tower and Building including
the existing traffic which is like the existing vibration levels measured from traffic. However, a vibration
monitor near the Water Tower and Building has been included in the Construction Protection and
Monitoring Plan to ensure that vibration transmission into the structure is not a concern. Procedures such
as minimizing vehicle speeds near the Water Tower and Building can be put in place if necessary to
mitigate vibration during construction.
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Construction Vibration
In addition to vehicle traffic along local roadways,vibration from construction equipment and its impact
to nearby residences is also a concern. Using Equations 3 and 4, minimum distances from structures to
not cause damage to historic structures, to not cause damage to residential structures, and to meet
recommended indoor vibration levels were calculated for each type of construction equipment identified
in Table 6.The results of these calculations can be found below in Table 9.
Table 8: Minimum Distances to Meet Vibration Criteria
Minimum Minimum Minimum
Construction FTA Guideline Distance to Cause Distance to Cause Distance to Meet
Equipment Type Equivalent No Damage to No Damage to Recommended
Historic Residential Indoor Vibration
Structures(ft) Structures(ft) Levels(ft)
Loader Large Bulldozer 20 12 85
Dozer Large Bulldozer 20 12 85
Excavator Large Bulldozer 20 12 85
Water/Fuel Truck Loaded Trucks 17 11 79
Tub Grinder Vibratory Roller 42 27 146
Woodchipper Vibratory Roller 42 27 146
Feller Buncher Large Bulldozer 20 12 85
Scissor Lift Small Bulldozer 1 1 9
Dump Truck Idling Loaded Trucks 17 11 79
Telescopic Forklift Small Bulldozer 1 1 9
Measured Truck
at Location 4 -
Using these minimum distances, the risk for potential impact or damage to nearby structures can be
evaluated. To evaluate this risk, four receiving structures were identified. These sites can be seen below
in Figure 12. Using the proposed site plans as well as distances measured from Google Earth, the
approximate distance to the edge of the construction site and to the middle of the construction site were
measured for each receiving location. These distances along with the address/description of each
structure can be found below in Table 9.
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Construction Vibration (Continued)
Figure 12: Receiving Locations Evaluated for Construction Vibration
ro
v
i
'3
a` tt
P P
S
1
Table 9: Distances from Nearby Residences to the Construction Area at the Project Site
Receiving
Nearest Distance Distance to Center
Location
Address/Description to Construction of Construction
Site(ft) Site(ft)
Receiver 1 800 North Dr-Mattituck, NY 175 385
Receiver 2 805 North Dr- Mattituck, NY 351 561
Receiver 3 5106 W Mill Rd-Mattituck, NY 171 381
Receiver 4 Water Tower and Building-3380 Sound Ave 1001 1211
Water Tower and Building-3380 Sound Ave
Receiver 4 192 N/A
Distances to Haul Road
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SECTION 3.6.16—POTENTIAL IMPACTS ANALYSIS(Continued):
Potential Impacts from Construction Vibration (Continued)
None of the distances to the edge of the construction area from Table 9 are closer than the minimum
distances necessary to meet the vibration criteria presented in Tables 1 and 2 to avoid both potential
damage and adverse impact to nearby residences for feelable vibration within structures. This indicates
that there will be no impact to nearby structures due to construction.There can be an increase in vibration
levels due to multiple pieces of construction equipment operating simultaneously. The applicant has
committed to implementing vibration monitoring to ensure that there are not adverse vibration impacts
to nearby residents. Details on a proposed vibration monitoring plan can be found below in Section
3.6.17.
SECTION 3.6.17—CONSTRUCTION PROTECTION AND VIBRATION MONITORING PLAN:
Per the findings in Section 3.6.16, there is one potential impact with damage possible in the worst-case
condition at the Water Tower and Building located at 3380 W Mill Road using FTA guidelines for standard
soil conditions, but not using the data collected during the data collection on August 2nd, 2022. Analysis
completed from the construction site shows that there are no expected impacts to nearby structures and
residents during construction. In addition to the analysis completed, the applicant has committed to
implementing a construction protection and monitoring plan. It is proposed that vibration monitoring
terminals be installed at 4 locations and be monitored through all phases of construction to ensure that
vibration relating to construction activities and truck traffic do not have a negative and adverse impact to
neighbors and the Water Tower and Building at 3380 W Mill Road.
Vibration Monitoring Terminal Types and Locations
It is recommended that four vibration terminals be placed at locations near the closest residences to the
construction site as well as the Water Tower and Building at 3380 W Mill Road. Vibration monitoring
terminals should be installed as close to any impacted structures while also maintaining full access to the
vibration monitoring terminals. Possible locations can be found in Figure 13. The vibration monitoring
terminals should be cloud connected and able to send email or text message alerts should a specified
vibration threshold be exceeded such as Syscom ROCK or an approved equivalent. Exact vibration
monitoring sites will not be determined until the vibration monitors are installed based on accessibility to
the exact monitoring sites.
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SECTION 3.6.17—CONSTRUCTION PROTECTION AND VIBRATION MONITORING PLAN (Continued):
Vibration Monitoring Terminal Types and Locations(Continued)
Figure 13: Prospective Vibration Monitoring Sites
3
j tr.
8
}
Y R
�y
Vibration Monitoring Thresholds
The Syscom ROCK terminal or an equivalent terminal can set vibration thresholds in PPV. If these
thresholds are exceeded,an alert is sent via email or text message to the construction management team
to inform the team of an exceedance.To set the vibration thresholds, Equations 3 and 4 can be used,first
to determine the maximum reference 25-foot reference vibration levels to comply with the criteria in
Tables 1 and 2 if the vibration sources were located at the edge of the construction area,which would be
the worst-case scenario. Equations 3 and 4 can be rearranged into Equations 5 and 6 to accomplish this
as noted below.
l 1.1
PPv"f = PPvcriteria * C D�25/ Equation 5
where:
PPV,-ef = the maximum reference peak particle velocity at 25 feet if
the vibration source is located at the construction area
boundary
PPV,jteria. =the criteria for no impact, 0.12 in/s for historic structures and
0.2 in/s for residential structures
Dc =distance to the edge of the construction area, in feet
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SECTION 3.6.17—CONSTRUCTION PROTECTION AND VIBRATION MONITORING PLAN (Continued):
Vibration Monitoring Thresholds(Continued)
Lvref = Lcriteria + 30 log(25) — 1 Equation 6
where:
Lref =the maximum reference RMS velocity at 25 feet if the
vibration source is located at the construction area boundary
Lcriteria =the RMS velocity criteria for no impact, 72 VdB
DC =distance to the edge of the construction area, in feet
Once a reference maximum PPV and RMS velocity have been established for a piece of equipment at the
property line,Equations 3 and 4 can be applied to determine the vibration criteria at the installed distance
from the edge of the construction area.
The Syscom ROCK system, does not allow for alerts to be set using RMS velocity, but is provided through
its cloud portal if a PPV alarm is triggered. To set a threshold for a RMS velocity exceedance, it is
recommended that the relationship of the RMS velocity being equivalent to 0.707 of the peak velocity be
used.The RMS criteria in VdB can then be calculated to its corresponding PPV value. As a safety factor, 2
dB from the VdB level determined to be appropriate at each vibration monitoring location will be
subtracted to determine the appropriate threshold. This would lead to establishing a PPV value by using
Equation 7.
(Lmonitor Z
PPVmonitor = 1 * 20\\ lvo/ Equation 7
0.707
where:
PPVinonitor=the equivalent PPV alert criteria to meet the RMS velocity
criteria at the vibration monitoring terminal
Lmonitor =the RMS velocity criteria at the vibration monitoring terminal
Vo =the reference vibration level,0.000001 in/s
Should the PPV as defined in Equation 7 be exceeded,the measured RMS velocity must be confirmed in
the ROCK's cloud portal to determine if this is a confirmed exceedance.
At location 4, disturbance to inhabitants is not a concern.The criteria for Location 4 will be for vibration
damage only and should be the criteria for vibration damage to historic structures, 0.12 in/s. Ideally at
Vibration Monitoring Location 4,the vibration monitoring terminal will be installed as close as possible to
the foundation of the Water Tower and Building.
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SECTION 3.6.17—CONSTRUCTION PROTECTION AND VIBRATION MONITORING PLAN (Continued):
Procedure for Potential Vibration Exceedances
If vibration levels exceed permissible levels, the following steps will be taken for Vibration Monitoring
Locations 1-3:
- The acoustic consultant and construction management team should be notified if an exceedance is
measured.
- The time and location of construction activities when the exceedance is measured are to be provided
to the acoustic consultant.
- If the exceedance is an RMS exceedance, the RMS velocity should be verified in the ROCK'S cloud
portal.
- Should the cause of the exceedance be linked to the construction activities, construction should be
halted immediately until appropriate measures, such as operating fewer pieces of equipment or
moving construction activities away from the construction area boundary, can be completed.
- The only exception to halting construction would be if it would be a life safety issue for the
construction workers, or if it would result in an unsafe structure at the time of halting the
construction. In each of these cases. Construction should only be continued until such time that all
workers would be safe and that all structures are stable and would not be in danger of collapse.
The following procedure should be followed at Vibration Monitoring Location 4, located at the Water
Tower and Building:
- Arrival and departure times for all trucks to be loaded and leaving with building materials should be
logged by the construction management team. All scheduled traffic must occur within defined work
hours.
- Should an alert be triggered at Vibration Monitoring Location 4, the time of the alert should be
correlated with the arrival times of all trucks coming to the Project Site.
- If it is confirmed that exceedance is due to operation of a truck associated with the construction,truck
operators will be required to reduce speeds near the Water Tower and Building so that vibration is
reduced.All drivers are to be notified of any speed restrictions.
- Should two alerts confirmed to be due to truck vibration occur on the same day,truck trips are to be
halted until additional data can be collected and mitigation can be implemented.
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