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650-050-38 ENVIRONMENTAL MANAGEMENT 06/17 STATE OF FLORIDA DEPARTMENT OF TRANSPORTATION TECHNICAL REPORT COVERSHEET Noise Study Report Florida Department of Transportation District One Immokalee Road (CR 846) at Randall Boulevard Intersection Collier County, Florida Financial Management Number: 435368-1-22-01 ETDM Number: 14125 Date: May 1, 2019 The environmental review, consultation, and other actions required by applicable federal environmental laws for this project are being, or have been, carried out by FDOT pursuant to 23 U.S.C. § 327 and a Memorandum of Understanding dated December 14, 2016 and executed by FHWA and FDOT.

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Page 1: STATE OF FLORIDA DEPARTMENT OF TRANSPORTATION …swflroads.com/.../randall/pde/images/05_435368-1_Noise_Study_Rep… · with the Build Alternative. Additionally, for the purposes

650-050-38 ENVIRONMENTAL MANAGEMENT

06/17

STATE OF FLORIDA DEPARTMENT OF TRANSPORTATION

TECHNICAL REPORT COVERSHEET

Noise Study Report

Florida Department of Transportation

District One

Immokalee Road (CR 846) at Randall Boulevard Intersection

Collier County, Florida

Financial Management Number: 435368-1-22-01

ETDM Number: 14125

Date: May 1, 2019

The environmental review, consultation, and other actions required by applicable federal environmental laws for this project are being, or have been, carried out by FDOT pursuant to 23 U.S.C. § 327 and a Memorandum of Understanding dated December 14, 2016 and executed by FHWA and FDOT.

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Executive Summary The Florida Department of Transportation (FDOT) District One, in conjunction with the FDOT Office of Environmental Management, is preparing a Project Development and Environment (PD&E) Study to evaluate potential improvements to the intersection of Immokalee Road (CR 846) at Randall Boulevard in unincorporated Collier County. The study extends along Immokalee Road (CR 846) from Wilson Boulevard to east of Randall Boulevard and along Randall Boulevard to east of 8th Street NE. The primary goal of the proposed project is to improve intersection operations to serve future travel demand through the year 2045. The PD&E Study also includes intersection concepts to enhance mobility, safety conditions, and access for emergency responders in the area. The project is anticipated to have minimal effects and will be documented as a Type II Categorical Exclusion.

The objectives of this NSR are to identify land uses adjacent to the project corridor for which there are Noise Abatement Criteria (NAC), to evaluate future traffic noise levels at the properties with and without the proposed improvements, and to evaluate the need for, and effectiveness of, noise abatement measures. Additional objectives include the consideration of potential construction noise impacts and the identification of noise impact “contours” adjacent to the corridor.

The analysis was performed following FDOT procedures that comply with Title 23, Part 772 of the Code of Federal Regulations (23 CFR 772), Procedures for Abatement of Highway Traffic Noise and Construction Noise. The evaluation uses methodologies established by the FDOT and documented in the FDOT PD&E Manual, Part 2, Chapter 18 – Highway Traffic Noise (January 2019).

A total of 60 receptors (discrete/representative locations of a noise sensitive area) were evaluated. The receptors were evaluated for 58 residences, a public institution (a fire station), and a restaurant with an outdoor dining area. The residences were evaluated as an Activity Category B land use (NAC of 66 decibels on the “A”-weighted scale (dB(A)). Because there are no areas of frequent human use outside of the fire station, the station was evaluated as Activity Category D (NAC of 51 dB(A)). Finally, the outdoor dining area of the restaurant was evaluated as Activity Category E (NAC of 71 dB(A)).

The results of the analysis indicate that existing (year 2018) exterior traffic noise levels at the residences and the restaurant are predicted to range from 51.0 to 65.0 dB(A), and the interior traffic noise at the fire station is predicted to be 47.4 dB(A). In the future (year 2045) without the proposed project improvements (the No Build Alternative), exterior traffic noise levels at the residences and the restaurant are predicted to range from 52.1 to 66.8 dB(A), and the interior level at the fire station is predicted to be 49.2 dB(A). In the future with the proposed project improvements (the Build Alternative), exterior traffic noise levels at the residences are predicted to range from 53.1 to 61.4 dB(A), the interior level at the fire station is predicted to be 49.6 dB(A), and the exterior level at the restaurant is predicted to be 67.5 dB(A).

Based on these results, highway traffic noise levels do not exceed the NAC in the future with the proposed project improvements. The results of the analysis also indicate that when compared to existing conditions, traffic noise levels with the proposed improvements would not increase more than 4.0 dB(A) at any of the evaluated receptors. As such, the project would not substantially increase highway traffic noise (i.e., an increase of 15 dB(A) or more).

Based on the results of the PD&E Study, there are no highway traffic noise impacted land uses within the project that require abatement consideration. Should the proposed improvements change during the project’s final design phase such that a re-analysis of highway traffic noise is warranted and impacts are identified in the analysis, an evaluation of noise abatement measures would be performed at that time. The Florida Department of Transportation is committed to the construction of feasible and reasonable noise abatement measures at noise-impacted locations contingent on the following:

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1. Detailed noise analyses during the final design process support the need, feasibility and reasonableness of providing abatement;

2. Cost analysis indicates that the cost of the noise barrier(s) will not exceed the cost reasonable criterion;

3. Community input supporting types, heights, and locations of the noise barrier(s) is provided to the District Office; and

4. Safety and engineering aspects as related to the roadway user and the adjacent property owner have been reviewed and any conflicts or issues resolved.

The residences and the fire station within the project limits are considered to be construction noise and vibration sensitive sites. Implementing the proposed roadway improvements is not expected to have a significant noise or vibration impact on these sites because it is anticipated that application of the FDOT Standard Specifications for Road and Bridge Construction will minimize or eliminate the potential for such impacts. Should unanticipated noise or vibration issues arise during the construction process, the Project Engineer, in coordination with the District Noise Specialist and the Contractor, will investigate additional methods of controlling these impacts.

Land uses such as residences, motels, medical facilities, schools, churches, recreation areas, and parks are considered incompatible with highway traffic noise levels that exceed the NAC. In order to reduce the possibility of noise-related impacts on land uses that may be approved for construction in the future, noise level contours were developed for the future improved roadway facility. Local officials will be provided a copy of the NSR that delineates/illustrates the contours to promote compatibility between land development and the proposed improvements to the Immokalee Boulevard and Randall Road intersection.

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Table of Contents Page EXECUTIVE SUMMARY .......................................................................................................................... i 1.0 INTRODUCTION .................................................................................................................... 1-1

1.1 Project Overview .............................................................................................................. 1-1 1.2 Purpose and Need ............................................................................................................ 1-2 1.3 Alternatives ...................................................................................................................... 1-2

2.0 METHODOLOGY .................................................................................................................... 2-1 2.1 Evaluation Process ........................................................................................................... 2-1 2.2 Noise Model ..................................................................................................................... 2-1 2.3 Traffic Data ....................................................................................................................... 2-1

3.0 NOISE ANALYSIS ................................................................................................................... 3-1 3.1 Noise-Sensitive Land Uses ............................................................................................... 3-1 3.2 Measured Noise Levels .................................................................................................... 3-2 3.3 Results of the Noise Analysis ........................................................................................... 3-3

4.0 CONCLUSIONS ...................................................................................................................... 4-1 5.0 NOISE CONTOURS ................................................................................................................. 5-1 6.0 CONSTRUCTION NOISE AND VIBRATION ............................................................................... 6-1 7.0 PUBLIC INVOLVEMENT .......................................................................................................... 7-1 8.0 REFERENCES ......................................................................................................................... 8-1 LIST OF APPENDICES Appendix A Project Aerial

Appendix B Traffic Data for Noise Studies

Appendix C Typical Noise Levels

Appendix D Validation Documentation

Appendix E Traffic Noise Model (TNM) Files (provided on CD)

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LIST OF FIGURES Figure Page 1-1 Project Location Map .................................................................................................................... 1-1 5-1 Noise Contours .............................................................................................................................. 5-2 LIST OF TABLES Table Page 2-1 Hourly Traffic Volumes/Speeds Used in TNM ............................................................................... 2-2 3-1 FHWA/FDOT Noise Abatement Criteria ........................................................................................ 3-1 3-2 Validation Data ............................................................................................................................. 3-3 3-3 Predicted Traffic Noise Levels ....................................................................................................... 3-4 5-1 Noise Contours .............................................................................................................................. 5-1

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SECTION 1.0

Introduction 1.1 Project Overview The Florida Department of Transportation (FDOT) District One, in conjunction with the FDOT Office of Environmental Management, is preparing a Project Development and Environment (PD&E) Study to evaluate potential improvements to the intersection of Immokalee Road (County Road (CR) 846) at Randall Boulevard in unincorporated Collier County. The study extends along Immokalee Road (CR 846) from Wilson Boulevard to east of Randall Boulevard and along Randall Boulevard to east of 8th Street NE. Figure 1-1 presents the Project Location Map. The primary goal of the proposed project is to improve intersection operations to serve future travel demand through the year 2045. The study also includes intersection concepts to enhance mobility, safety conditions, and access for emergency responders in the area. The project is anticipated to have minimal effects and will be documented as a Type II Categorical Exclusion.

Figure 1-1. Project Location Map

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1.2 Purpose and need The purpose of this project is to improve overall traffic operations at the existing at-grade intersection of CR 846 (Immokalee Road) and Randall Boulevard to meet future travel demand. Without the proposed improvement, the intersection will experience high levels of delay and operate below level-of-service (LOS) targets before the year 2045.

Immokalee Road (CR 846) is categorized as a Freight Distribution Route and a High Crash Corridor in the Collier 2040 Long Range Transportation Plan (LRTP).1 The roadway is critical in facilitating movement of local and regional traffic (including truck traffic) in northern Collier County. Immokalee Road (CR 846) is one of three east-west connections to Interstate 75 (I-75) in Collier County and is the only east-west connection from I-75 in northern Collier County that connects to northeastern Collier County. The Immokalee Road (CR 846) and Randall Boulevard intersection is essential in that traffic from northeastern Collier County via State Road (SR 29), Oil Well Road (CR 858), and Randall Boulevard, must pass through the intersection to access I-75. Immokalee Road (CR 846) is also a designated emergency evacuation route.

Other objectives of the proposed improvements are to:

• Improve turning movements and overall traffic operations at the intersection

• Enhance regional mobility and access between I-75 and eastern Collier County

• Improve freight mobility and access

• Enhance safety conditions by increasing the number of residents from a fairly isolated area of Collier County that can be evacuated

• Improve access for emergency responders

• Reduce motorist, pedestrian, bicyclist, and transit user conflicts

1.3 Alternatives A single Build Alternative is proposed to improve the intersection in two phases. Phase 1 includes widening Randall Boulevard from two lanes undivided to four lanes divided. Providing an at-grade intersection with three left turn only lanes from Westbound Randall Boulevard to Westbound Immokalee Road and, providing a continuous flow right turn from Eastbound Immokalee Road to Eastbound Randall Boulevard. Phase 1 is intended to serve as an interim improvement until additional mobility and capacity is needed.

Phase 2 of the Build Alternative proposes a grade-separated flyover bridge to allow the Westbound Randall Boulevard left turns to bypass the signalized intersection at Immokalee Road. Phase 2 would provide the ultimate intersection improvement. The future widening of Randall Boulevard to six lanes, as shown in the LRTP Needs Plan, can be accomplished within the proposed right of way footprint by widening into the median.

Notably, the No Build Alternative is included in the PD&E Study and serves as a baseline for comparison with the Build Alternative. Additionally, for the purposes of this Noise Study Report (NSR), only Phase 2 of the Build Alternative was evaluated since it is the ultimate improvement and has the larger footprint.

1 Collier 2040 Long Range Transportation Plan Final Report. December 2015. Figure 4-5 & 4-6. Accessed on Dec. 13, 2018 from

http://www.colliermpo.org/modules/showdocument.aspx?documentid=7725

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SECTION 2.0

Methodology 2.1 Evaluation Process The highway traffic noise analysis discussed in this NSR was prepared in accordance with Part 772 of Title 23 of the Code of Federal Regulations (23 CFR 772), Procedures for Abatement of Highway Traffic Noise and Construction Noise, and the policies/procedures documented in the FDOT’s PD&E Manual, Part 2, Chapter 18 (Highway Traffic Noise, January 14, 2019), and guidance from the FDOT’s Traffic Noise Modeling and Analysis Practitioners Handbook. The predicted highway traffic noise levels presented in this report are expressed in decibels on the “A”-weighted scale (dB(A)). This scale most closely approximates the response characteristics of the human ear to traffic noise. The noise levels in this NSR are reported as equivalent levels (Leq), which are equivalent steady-state sound levels that contain the same acoustic energy as time-varying sound levels over a period of one hour (Leq(h)).

2.2 Noise Model The prediction of existing and future highway traffic noise levels with and without the roadway improvements was performed using the Federal Highway Administration’s (FHWA’s) computer model for highway traffic noise prediction and analysis – the Traffic Noise Model (TNM-Version 2.5). The TNM propagates sound energy, in one-third octave bands, between highways and nearby receptors taking the intervening ground’s acoustical characteristics/topography and rows of buildings into account.

2.3 Traffic Data Traffic noise levels are low when traffic volumes are low (LOS A or B) and when traffic is so congested that movement is slow (LOS D, E, or F). For the purpose of a highway traffic noise assessment, it is assumed that the maximum hourly traffic noise level occurs between these two conditions—when operating conditions are considered to be LOS C. As such, the traffic volume characteristics used in the analysis reflect either the forecast demand volumes, if the level meets the LOS A or B criteria, or the LOS C volume, whichever is less. The operating conditions used in TNM to predict existing (year 2018) highway traffic noise and future (year 2045) levels with and without the CR 846/Randall Boulevard intersection Build Alternative are summarized in Table 2-1. Detailed project-related traffic data are provided in Appendix B.

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Table 2-1. Hourly Traffic Volumes/Speeds Used In TNM

SEGMENT SCENARIO PEAK DIRECTION

VOLUME

OFF-PEAK DIRECTION VOLUME

DEMAND OR LOS C

POSTED SPEED (MPH)

Randall Boulevard

Existing 743 608 Demand 45

No-Build 830 830 LOS C 45

Build 1,376 1,126 Demand 45

Immokalee Road west of Randall Boulevard

Existing 2,079 1,701 Demand 45

No-Build 2,940 2,940 LOS C 45

Build 2,940 2,940 LOS C 45

Immokalee Road east of Randall Boulevard

Existing 1,693 1,385 Demand 45

No-Build 2,673 2,187 Demand 45

Build 2,673 2,187 Demand 45 Source: Final Project Traffic Report, Traf-O-Data, Corp., February 2019

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SECTION 3.0

Noise Analysis 3.1 Noise-Sensitive Land Uses Noise-sensitive land uses occur where frequent human use occurs and where a lowered noise level would be of benefit. To evaluate traffic noise at these properties, the FHWA established Noise Abatement Criteria (NAC). As shown in Table 3-1, the criteria vary according to the activity category for the land use of a property. For comparative purposes, typical noise levels for common indoor and outdoor activities are provided in Appendix C.

Table 3-1. FHWA/FDOT Noise Abatement Criteria [Leq(h) Expressed In dB(A)]

ACTIVITY CATEGORY DESCRIPTION OF ACTIVITY CATEGORY

ACTIVITY Leq(h)1

FHWA FDOT

A

Lands on which serenity and quiet are of extraordinary significance and serve an important public need and where the preservation of those qualities is essential if the area is to continue to serve its intended purpose.

57 (Exterior)

56 (Exterior)

B2 Residential 67

(Exterior) 66

(Exterior)

C2

Active sports areas, amphitheaters, auditoriums, campgrounds, cemeteries, day care centers, hospitals, libraries, medical facilities, parks, picnic areas, places of worship, playgrounds, public meeting rooms, public or nonprofit institutional structures, radio studios, recording studios, recreational areas, Section 4(f) sites, schools, television studios, trails, and trail crossings.

67 (Exterior)

66 (Exterior)

D

Auditoriums, day care centers, hospitals, libraries, medical facilities, places of worship, public meeting rooms, public or nonprofit institutional structures, radio studios, recording studios, schools, and television studios.

52 (Interior)

51 (Interior)

E2 Hotels, motels, offices, restaurants/bars, and other developed lands, properties or activities not included in A-D or F.

72 (Exterior)

71 (Exterior)

F

Agriculture, airports, bus yards, emergency services, industrial, logging, maintenance facilities, manufacturing, mining, rail yards, retail facilities, shipyards, utilities (water resources, water treatment, electrical), and warehousing.

-- --

G Undeveloped lands that are not permitted. -- -- 1 The Leq(h) Activity Criteria values are for impact determination only and are not design standards for noise abatement measures. 2 Includes undeveloped lands permitted for this activity category. Source: CFR, Title 23, Part 772.

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When predicted traffic noise levels “approach” or exceed the NAC, or when predicted future noise levels increase substantially from existing levels, the FHWA requires that noise abatement measures be considered. FDOT defines the word “approach” to mean within one dB(A) of the NAC. The FDOT’s NAC are also shown in Table 3-1. Additionally, the FDOT criteria states that a substantial increase would occur if traffic noise levels are predicted to increase 15 dB(A) or more above existing conditions as a direct result of a transportation improvement project.

Within the project limits, 60 properties with noise sensitive land uses have the potential to be impacted by highway traffic noise as a result of the proposed project improvements. The land use review that identified these properties was performed on December 30, 2018. The 60 sites are comprised of the following:

1. Activity Category B – 58 residences (five north of Immokalee Road, one south of Immokalee Road, 46 north of Randall Boulevard (Valencia Lakes), and six south of Randall Boulevard). The FDOT’s NAC for Activity Category B land uses is 66 dB(A).

2. Activity Category D – Interior traffic noise levels were evaluated at a public/nonprofit institutional structure (North Collier Fire and Rescue Station). The FDOT’s NAC for Activity Category D land uses is 51 dB(A). Interior traffic noise levels were predicted by applying the noise reduction factor for light frame buildings (20 dB(A)) to the predicted exterior noise levels as recommended by FHWA’s Highway Traffic Noise: Analysis and Abatement Guidance.

3. Activity Category E – A restaurant with an outdoor dining area (L’Appetito restaurant in the Armando’s Supermarket Plaza). The FDOT’s NAC for Activity Category E land uses is 71 dB(A).

In the TNM, the 60 properties were evaluated using 60 receptors (i.e., discrete or representative locations of a noise sensitive land use). Notably, there is a six-foot tall concrete privacy wall located between the Valencia Lakes community and Randall Boulevard.

3.2 Measured Noise Levels As previously stated, existing and future noise levels with and without the Build Alternative were modeled using the TNM. To validate the TNM and verify that the model accurately predicts the existing traffic noise based on current conditions, measured sound levels were obtained within the project corridor. Traffic data including motor vehicle volumes, vehicle mix, vehicle speeds, and meteorological conditions were recorded during each measurement period.

The field measurements were conducted in accordance with the FHWA’s Noise Measurement Field Guide. The measurements were obtained using a Larson Davis LxT Type II integrating sound level meter (SLM). The SLM was calibrated before and after the measurement periods with a Larson Davis CAL200 calibrator.

The recorded traffic data were used as input for the TNM to determine if, given the topography and actual site conditions of the area, the computer model could “re-create” the measured levels with the existing roadway. Following FDOT policy, a noise prediction model is considered within an acceptable level of accuracy if the measured and predicted noise levels are within a tolerance standard of 3 dB(A).

Table 3-2 presents the field measurements and the validation results. As shown, the ability of the model to predict noise levels within the FDOT limits of plus or minus 3 dB(A) for the project was confirmed. Documentation in support of the validation is provided in Appendix D.

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Table 3-2. Validation Data

LOCATION MEASUREMENT

PERIOD MODELED MEASURED DIFFERENCE

North side of Randall Boulevard midway between the Publix entrance and 8th Street NE

1 62.9 62.8 0.1 2 62.8 62.7 0.1 3 62.8 63.4 -0.6

Note: The field measurement location is identified on the project aerial in Appendix A of this report.

3.3 Results of the Noise Analysis Table 3-3 presents the results of the traffic noise analysis for the proposed improvements. As shown, existing (2018) exterior traffic noise levels at the residences and the restaurant are predicted to range from 51.0 to 65.0 dB(A), and the interior traffic noise at the fire station is predicted to be 47.4 dB(A). In the future (2045) without the proposed project improvements (No Build Alternative), exterior traffic noise levels at the residences/restaurant are predicted to range from 52.1 to 66.8 dB(A), and the interior level at the fire station is predicted to be 49.2 dB(A). Finally, in the future with the proposed project improvements (Build Alternative), exterior traffic noise levels at the residences and the restaurant are predicted to range from 53.1 to 67.5 dB(A), and the interior level at the fire station is predicted to be 49.6 dB(A). As such, based on the results of the analysis, highway traffic noise levels in the future with the proposed improvements are not predicted to approach, meet, or exceed the NAC at any of the evaluated receptors.

The results of the analysis also indicate that when compared to existing conditions, traffic noise levels would not increase more than 4.0 dB(A) with the proposed project improvements. As such, the project would not substantially increase traffic noise (i.e., increase traffic noise 15 dB(A) or more) at any of the evaluated receptors.

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Table 3-3. Predicted Traffic Noise Levels

Site ID

Activity Category Description Location

Leq(h) (dB(A)) Approaches, Meets, or

Exceeds the NAC? (Y/N)

Existing (2018)

No-Build (2045)

Build (2045)

Increase from

Existing

1 B Residential North of Immokalee Road 58.8 60.6 60.9 2.1 N

2 B Residential North of Immokalee Road 58.5 60.3 60.7 2.2 N

3 B Residential North of Immokalee Road 54.3 56.3 56.4 2.1 N

4 B Residential North of Immokalee Road 52.4 54.2 54.6 2.2 N

5 B Residential North of Immokalee Road 56.4 58.2 58.6 2.2 N

6 B Residential South of Immokalee Road 51.7 53.7 54.0 2.3 N

7 D Public Institution

North Collier Fire and Rescue Station 47.4 49.2 49.6 2.2 N

8 E Restaurant Outdoor eating area at L’Appetito in Armando’s Super Market Plaza

65.0 66.8 67.5 2.5 N

9 B Residential North of Randall Boulevard (Valencia Lakes) 58.0 59.0 60.3 2.3 N

10 B Residential North of Randall Boulevard (Valencia Lakes) 58.1 59.1 60.3 2.2 N

11 B Residential North of Randall Boulevard (Valencia Lakes) 57.8 58.8 59.8 2.0 N

12 B Residential North of Randall Boulevard (Valencia Lakes) 58.2 59.1 60.0 1.8 N

13 B Residential North of Randall Boulevard (Valencia Lakes) 58.4 59.3 60.0 1.6 N

14 B Residential North of Randall Boulevard (Valencia Lakes) 58.3 59.3 59.9 1.6 N

15 B Residential North of Randall Boulevard (Valencia Lakes) 58.6 59.5 60.3 1.7 N

16 B Residential North of Randall Boulevard (Valencia Lakes) 58.8 59.7 60.4 1.6 N

17 B Residential North of Randall Boulevard (Valencia Lakes) 59.0 59.9 60.6 1.6 N

18 B Residential North of Randall Boulevard (Valencia Lakes) 58.1 59.1 59.8 1.7 N

19 B Residential North of Randall Boulevard (Valencia Lakes) 58.8 59.8 60.5 1.7 N

20 B Residential North of Randall Boulevard (Valencia Lakes) 59.0 59.9 60.7 1.7 N

21 B Residential North of Randall Boulevard (Valencia Lakes) 57.8 58.7 59.3 1.5 N

22 B Residential North of Randall Boulevard (Valencia Lakes) 59.1 60.1 60.8 1.7 N

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Site ID

Activity Category Description Location

Leq(h) (dB(A)) Approaches, Meets, or

Exceeds the NAC? (Y/N)

Existing (2018)

No-Build (2045)

Build (2045)

Increase from

Existing

23 B Residential North of Randall Boulevard (Valencia Lakes) 59.1 60.0 60.6 1.5 N

24 B Residential North of Randall Boulevard (Valencia Lakes) 58.9 59.8 60.7 1.8 N

25 B Residential North of Randall Boulevard (Valencia Lakes) 59.7 60.6 61.4 1.7 N

26 B Residential North of Randall Boulevard (Valencia Lakes) 58.1 59.0 59.8 1.7 N

27 B Residential North of Randall Boulevard (Valencia Lakes) 57.6 58.5 59.0 1.4 N

28 B Residential North of Randall Boulevard (Valencia Lakes) 56.4 57.4 58.6 2.2 N

29 B Residential North of Randall Boulevard (Valencia Lakes) 53.8 54.8 55.7 1.9 N

30 B Residential North of Randall Boulevard (Valencia Lakes) 54.5 55.5 56.8 2.3 N

31 B Residential North of Randall Boulevard (Valencia Lakes) 53.2 54.2 55.7 2.5 N

32 B Residential North of Randall Boulevard (Valencia Lakes) 52.1 53.1 54.3 2.2 N

33 B Residential North of Randall Boulevard (Valencia Lakes) 52.5 53.5 54.7 2.2 N

34 B Residential North of Randall Boulevard (Valencia Lakes) 51.2 52.2 53.1 1.9 N

35 B Residential North of Randall Boulevard (Valencia Lakes) 54.8 55.7 56.7 1.9 N

36 B Residential North of Randall Boulevard (Valencia Lakes) 54.3 55.2 56.0 1.7 N

37 B Residential North of Randall Boulevard (Valencia Lakes) 55.8 56.7 57.3 1.5 N

38 B Residential North of Randall Boulevard (Valencia Lakes) 57.9 58.8 59.4 1.5 N

39 B Residential North of Randall Boulevard (Valencia Lakes) 56.6 57.5 57.8 1.2 N

40 B Residential North of Randall Boulevard (Valencia Lakes) 58.0 58.9 59.1 1.1 N

41 B Residential North of Randall Boulevard (Valencia Lakes) 57.5 58.4 58.8 1.3 N

42 B Residential North of Randall Boulevard (Valencia Lakes) 57.8 58.7 58.9 1.1 N

43 B Residential North of Randall Boulevard (Valencia Lakes) 57.7 58.6 58.6 0.9 N

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Site ID

Activity Category Description Location

Leq(h) (dB(A)) Approaches, Meets, or

Exceeds the NAC? (Y/N)

Existing (2018)

No-Build (2045)

Build (2045)

Increase from

Existing

44 B Residential North of Randall Boulevard (Valencia Lakes) 56.9 57.7 57.7 0.8 N

45 B Residential North of Randall Boulevard (Valencia Lakes) 56.5 57.4 57.3 0.8 N

46 B Residential North of Randall Boulevard (Valencia Lakes) 56.1 57.0 56.7 0.6 N

47 B Residential North of Randall Boulevard (Valencia Lakes) 57.1 58.0 57.5 0.4 N

48 B Residential North of Randall Boulevard (Valencia Lakes) 56.5 57.4 57.0 0.5 N

49 B Residential North of Randall Boulevard (Valencia Lakes) 55.5 56.4 56.0 0.5 N

50 B Residential North of Randall Boulevard (Valencia Lakes) 55.0 55.9 55.6 0.6 N

51 B Residential North of Randall Boulevard (Valencia Lakes) 54.4 55.3 55.0 0.6 N

52 B Residential North of Randall Boulevard (Valencia Lakes) 54.6 55.5 55.3 0.7 N

53 B Residential North of Randall Boulevard (Valencia Lakes) 55.4 56.3 56.1 0.7 N

54 B Residential North of Randall Boulevard (Valencia Lakes) 55.8 56.7 56.5 0.7 N

55 B Residential South of Randall Blvd 51.0 52.1 55.0 4.0 N

56 B Residential South of Randall Blvd 57.4 58.3 59.0 1.6 N

57 B Residential South of Randall Blvd 57.7 58.7 59.0 1.3 N

58 B Residential South of Randall Blvd 58.1 59.1 59.0 0.9 N

59 B Residential South of Randall Blvd 54.2 55.2 55.6 1.4 N

60 B Residential South of Randall Blvd 58.5 59.5 59.3 0.8 N Note: Site locations are identified on the project aerial in Appendix A of this report.

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SECTION 4.0

Conclusions

Based on the results of the noise analysis, there are no highway traffic noise impacted land uses within the project that require abatement consideration. Should the proposed improvements change during the project’s final design phase such that a re-analysis of highway traffic noise is warranted and impacts are identified in the analysis, an evaluation of noise abatement measures would be performed at that time. The Florida Department of Transportation is committed to the construction of feasible and reasonable noise abatement measures at noise-impacted locations contingent on the following:

1. Detailed noise analyses during the final design process support the need, feasibility and reasonableness of providing abatement;

2. Cost analysis indicates that the cost of the noise barrier(s) will not exceed the cost reasonable criterion;

3. Community input supporting types, heights, and locations of the noise barrier(s) is provided to the District Office; and

4. Safety and engineering aspects as related to the roadway user and the adjacent property owner have been reviewed and any conflicts or issues resolved.

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5-1

SECTION 5.0

Noise Contours Land uses such as residences, motels, medical facilities, schools, churches, recreation areas, and parks are considered incompatible with highway noise levels exceeding the NAC. In order to reduce the possibility of additional traffic noise-related impacts, noise level contours were developed for the future improved roadway facility to estimate where an “approach” of the NAC is predicted to occur. Specifically, these noise contours delineate the distance from the improved roadway’s edge-of-travel lane to where 56, 66, and 71 dB(A) (FDOT and FHWA Activity Categories A, B/C, and E, respectively) are expected to occur in the future (2045) with the proposed project improvements.

The contours are shown in Table 5-1 and in Figure 5-1. Within the project limits, the contours extend from 25 to 270 feet from the improved roadway’s edge-of-travel lane. Local officials will be provided a copy of the NSR to promote compatibility between land development and the proposed improvements to the Immokalee Boulevard and Randall Road intersection.

Table 5-1. Noise Contours

DISTANCE FROM IMPROVED ROADWAY’S EDGE-OF-TRAVEL LANE (FT)*

ACTIVITY CATEGORY A 56 dB(A)

ACTIVITY CATEGORY B/C 66 dB(A)

ACTIVITY CATEGORY E 71 dB(A)

270 75 25

*See Table 3-1 for a description of the activities that occur within each category. Distances do not reflect any reduction in noise levels that would occur from existing structures (shielding) and should be used for planning purposes only.

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5-2

Figure 5-1. Noise Contours

56 dB(A) 270 feet from

edge-of-travel lane

56 dB(A) 270 feet from

edge-of-travel lane

66 dB(A) 75 feet from

edge-of-travel lane

66 dB(A) 75 feet from

edge-of-travel lane

71 dB(A) 25 feet from

edge-of-travel lane

71 dB(A) 25 feet from

edge-of-travel lane

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SECTION 6.0

Construction Noise and Vibration The residences and the living quarters of the fire station within the project limits are construction noise and vibration sensitive sites. Construction of the proposed roadway improvements is not expected to have any significant noise or vibration impacts on these properties. If sensitive land uses develop adjacent to the roadway prior to construction, increased potential for noise or vibration impacts could result. It is anticipated that the application of the FDOT Standard Specifications for Road and Bridge Construction will minimize or eliminate potential construction noise and vibration impacts. However, should unanticipated noise or vibration issues arise during the construction process, the Project Engineer, in coordination with the District Noise Specialist and the Contractor, will investigate additional methods of controlling these impacts.

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SECTION 7.0

Public Involvement The FDOT conducted a Public Information Meeting for the Immokalee Road at Randall Boulevard Intersection PD&E Study on December 6, 2018 at the North Collier Regional Park in Naples. A Public Hearing is also scheduled during the spring of 2019. The hearing will inform the public of the results of the PD&E Study and provide the opportunity for the public to express their views regarding specific location, design, socio-economic effects, and environmental impacts associated with the No-Build and recommended Build Alternatives.

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SECTION 8.0

References Federal Highway Administration. U.S. Department of Transportation. July 13, 2010. Title 23 CFR, Part

772. Procedures for Abatement of Highway Traffic Noise and Construction Noise.

Federal Highway Administration. February 2004. Traffic Noise Model, Version 2.5.

Federal Highway Administration. December 2011. Highway Traffic Noise: Analysis and Abatement Guidance.

Federal Highway Administration. June 2018. Noise Measurement Field Guide. FHWA-HEP-18-066.

Florida Department of Transportation. January 14, 2019. Project Development and Environment Manual, Part 2, Chapter 18 – Highway Traffic Noise.

Florida Department of Transportation. July 22, 2009. A Method to Determine Reasonableness and Feasibility of Noise Abatement at Special Use Locations.

Florida Department of Transportation. January 1, 2019. FDOT Design Manual.

Florida Department of Transportation. 2018. Standard Specifications for Road and Bridge Construction.

Florida Department of Transportation. January 1, 2016. Traffic Noise Modeling and Analysis Practitioners Handbook.

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APPENDIX A Project Aerial

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APPENDIX B Traffic Data for Noise Studies

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APPENDIX C Typical Noise Levels

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APPENDIX D Validation Documentation

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NOISE MEASUREMENT DATA SHEET Measurements Taken By: Wayne Arner Date: 12/30/18 Time Study Started: 1:45 PM Time Study Ended: 2:55 PM Project Identification:

Financial Project ID: 435368-1 Project Location: Immokalee Road at Randall Boulevard Intersection

Collier County, FL

Site Identification: North side of Randall Boulevard, mid-way between the Publix entrance and 8th St NE, five feet in front of the Valencia Lakes privacy wall.

Weather Conditions: Sky: Clear Partly Cloudy X Cloudy Other Temperature 85F Wind Speed 2.0 mph Wind Direction SE Humidity 64%

Equipment: Sound Level Meter:

Type: Larson Davis LxT Serial Number(s): 1843 Did you check the batteries? Yes X No Calibration Readings: Start 114.0 End 114.0 Response Settings: Fast Slow X Weighting: A X Other

Calibrator: Type: Larson Davis CAL 200 Serial Number: 5592

Did you check the battery? Yes X No

TRAFFIC DATA

Roadway Identification Randall Blvd Westbound Randall Blvd Eastbound Vehicle Type Volume (1 hr) Speed (mph) Volume (1 hr) Speed (mph) Autos 306-396-312 50.2-49.0-48.2 528-462-462 43.9-44.8-45.7 Medium Trucks 6-6-6 46.0-46.0-46.0 6-0-18 45.0-NA-45.0 Heavy Trucks 0-0-0 NA-NA-NA 0-0-0 NA-NA-NA Buses 0-0-0 NA-NA-NA 0-0-0 NA-NA-NA Motorcycles 6-0-0 50.2-NA-NA 0-0-6 NA-NA-45.7 Duration Three 10 minute runs. Counts multiplied by 6 to get hourly volume.

RESULTS [dB(A)]

LEQ : 62.8-62.7-63.4 Background Noise: Bees. Major Sources: Randall Boulevard. Unusual Events: Occasional intermittent traffic due to traffic signal at Immokalee/Randall.

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APPENDIX E Traffic Noise Model (TNM) Files

(provided on CD)