Harlem Avenue Interchange Design Discussion August 24, 2015 1 - - PowerPoint PPT Presentation

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Harlem Avenue Interchange Design Discussion August 24, 2015 1 - - PowerPoint PPT Presentation

Harlem Avenue Interchange Design Discussion August 24, 2015 1 Expressway Construction Pre-dates Modern Design Standards Expressway designed and constructed in 1950s No past experience to base design standards on Little or no data


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Harlem Avenue Interchange Design Discussion

August 24, 2015

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Expressway Construction Pre-dates Modern Design Standards

§ Expressway designed and constructed in 1950’s § No past experience to base design standards on § Little or no data – safety vs. design § No noise or air quality standards at the time § Existing ramps designed to minimize ROW footprint.

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§ Safety § Mobility § Facility condition and design § Create an asset for the communities

PROJECT NEEDS

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§ Constrained existing right-of- way § CTA Blue Line § CSX Railroad § Vehicle & non-motorized crossings § Drainage

DENSE URBAN SETTING POSES MULTIPLE DESIGN CONSTRAINTS

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EXISTING DRAINAGE SYSTEM IN OAK PARK

§ I-290 trunk sewer begins at Central Avenue § Drains west to Pump Station #4 @ DesPlaines River § Drains I-290, CTA and CSX in this area

Austin Blvd.

Pump Station #4

Central Ave.

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EXISTING DRAINAGE SYSTEM IS UNDERSIZED & RESULTS IN EXPRESSWAY AND RAIL FLOODING

DesPlaines River DesPlaines Ave. Circle Ave. Harlem Ave. Oak Park Ave. East Ave. Ridgeland Ave. Lombard Ave. Austin Blvd. Central Ave.

Existing Flood Elevation

Pump Station #4

Existing I-290 Profile

§ Existing system cannot adequately convey storm water during heavy storms § Existing expressway system designed for 10-year storm § I-290, CTA, and CSX are subject to frequent flooding

CSX Profile

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MULTIPLE FACTORS INFLUENCE HARLEM AVENUE DESIGN

CSX Over CTA CSX Over DesPlaines Ave. CSX Under Harlem Ave. CSX Siding to Ferrara Pan CSX under Circle Ave

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LOWERING OF CSX REQUIRES LOWERING OF CTA, I-290 & DESPLAINES AVE.

Circle Ave. I-290 CTA DesPlaines Ave. Harlem Ave. I-290 Main Drain Existing CSX Profile

Existing CSX Clearance 19.4 ft.

Proposed Stormwater Elevation Existing Flood Elev.

Insufficient CSX Clearance

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LOWERING OF CSX REQUIRES LOWERING OF CTA, I-290, & DESPLAINES AVENUE

Circle Ave. DesPlaines Ave. Existing CSX Profile < 1% I-290 Main Drain I-290 CTA Harlem Ave. Lowered CSX Profile (1% max grade) Proposed Stormwater Elevation Existing Flood Elev.

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Lowered CSX Profile (1% max grade) I-290 CTA

LOWERING OF CSX REQUIRES LOWERING OF CTA, I-290, & DESPLAINES AVENUE

Circle Ave. DesPlaines Ave. Existing CSX Profile I-290 Main Drain Harlem Ave. 2.2% RR Grade to clear Existing I-290 is too steep Proposed Stormwater Elevation Existing Flood Elev.

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PROPOSED PROFILE LOWERS MAINLINE & MEETS DRAINAGE REQUIREMENTS

– Lowers mainline up to 9’ – Lowers Harlem Avenue & ramp intersection by 2’ – No impacts to CSX or CTA profile/clearance – Avoids cumulative construction impacts of lowering CSX – Meets drainage requirements

CSX CTA

Proposed 100 yr. Flood Elev.

Mainline 8’ Lower I-290 Maintain Existing CSX Clearance Proposed Harlem Avenue Bridge Profile Harlem Ave. lowered by 2 feet Mainline Shifted 25’

Profile Grid Scale 5’ vertical 50’ horizontal

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Condo

10 ft. above existing

PROPOSED RAMPS LOWER MAINLINE & SHIFT EXPRESSWAY AWAY FROM COMMUNITY

Existing Left Ramps Up to 8’ low er Mainline Shifted 25’

*

Noise walls to be determined

*

XS Grid Scale 5’ vertical 10’ horizontal

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Air Quality Effects

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§ USEPA National Ambient Air Quality Standards for 6 pollutants (carbon monoxide, nitrogen dioxide, ozone, particulate matter, sulfur

dioxide & lead)

§ Significant progress in reducing mobile source emissions

(cleaner vehicles, cleaner fuels, inspection & maintenance)

REGIONAL AIR QUALITY TRENDS

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NE ILLINOIS TRANSPORTATION AIR QUALITY IN CONFORMANCE

§ Cook County is a:

– Non-attainment area for ozone – Maintenance area for small particulate matter

§ CMAP Long Range Plan & Program

– Region-wide transportation air quality conformity analysis – Region in conformance – I-290 Expressway improvements included

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PROJECT LEVEL AIR QUALITY SENSITIVITY TESTING

§ NEPA/FHWA Requirement: PM2.5 for Preferred Alternative § Threshold: 10,000 increase in truck ADT

– I-290 alternatives mostly below threshold – Further coordination needed

§ “Corridor” analysis, rather than location specific Sensitivity analysis undertaken as initial step – stakeholder comments

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AREA-WIDE AIR QUALITY SENSITIVITY ANALYSIS

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§ Pollutant emissions based on traffic volumes, speed, vehicle miles traveled, vehicle mix, meteorological conditions, etc. § Area-wide pollutant emissions for CO, NO2, Hydrocarbons, PM10 & PM2.5 § Change in emissions for all pollutants less than 1% for all alternatives § Conclusion:

– No significant change from No-Build – No significant change between alternatives

AREA-WIDE AIR QUALITY SENSITIVITY ANALYSIS

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CARBON MONOXIDE INTERSECTION SENSITIVITY ANALYSIS

§ Criteria:

– 62,500 ADT highest design 1-way volume – Harlem Ave 2-way ADT 28,900 - 39,000

§ Used as sensitivity analysis § CO concentration measured in parts per million (ppm)

– 70 ppm – some health concern – 150 - 200 ppm – serious heath concern

§ Greatest exposure – inside a car § Pass/Fail standard for transportation projects:

– Established to protect vulnerable populations (children, elderly, etc.) – 9 ppm - 8 hour average – 35 ppm - 1 hour average

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HARLEM AVENUE INTERSECTION CO ANALYSIS

§ CO Factors

– Background CO

§ 3 ppm assumed § 2 ppm measured in field

– Traffic volume – Proximity/location of receptors – Closest receptor locations:

§ R1 – CTA station entrance § R2 – Single family home § R3 – Condo building

R2 R1 R3

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4.5 4.1 3.6 0.5 0.1 0.1

5 10 15 20 25 30 35 40

R1 R2 R3

CO ppm

4 3.8 3.4 0.4 0.1

1 2 3 4 5 6 7 8 9 10

R1 R2 R3

CO ppm

8-Hour Average Concentration 1-Hour Average Concentration

HARLEM AVENUE INTERSECTION CO SENSITIVITY ANALYSIS

8-Hour NAAQS 1-Hour NAAQS

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Noise Effects

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TRAFFIC NOISE

§ Traffic noise is predicted by FHWA Traffic Noise Model, validated with field measurements § Receptors and Noise-Sensitive Land Uses

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NOISE ABATEMENT CRITERIA (NAC)

§ Category A: Serene lands - rarely applies. (Tomb of the Unknown Solider) § Category B: Residential § Category C: Hospitals, schools, places of worship, parks § Category D*: Hospitals, libraries, places of worship, institutions, schools § Category E: Hotels, offices, restaurants § Category F: Agricultural, industrial, retail, utilities § Category G: Undeveloped lands

*Interior noise, to be studied only after exterior is studied, or if noise abatement is not feasible and reasonable

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INTERIOR VS EXTERIOR NOISE

§ IDOT and FHWA stipulate that outdoor areas of frequent human use be given primary consideration § Interior noise for private residences not studied, as that analysis focuses on noise levels interfering with outdoor conversations

“Only consider the interior levels at these land uses after fully completing an analysis of any outdoor activity areas or determining that exterior abatement measures are not feasible or reasonable.”

  • - FHWA’s Highway Traffic Noise: Analysis and Abatement Guidance
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67 dB(A)

NAC Category B & C

dB(A) Examples

90

Food blender @ 3 feet, freight train at 100 feet

80 70 60

Dishwasher in next room, large business office

50 40

  • Library. 45dB(A) – quiet urban nighttime

30 20 10 3

Threshold of human hearing

Common Noise Levels

72 dB(A)

NAC Category E

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Oak Park - Existing vs. No-Build Noise Levels

§ 75% of receptors above NAC for Existing or Future No Build (without project) § Noise abatement appears constructible through Oak Park § October: Recommended wall locations and heights

Studied I-290 Noise Receptors* Receptors with Existing Levels Higher than NAC Receptors with 2040 No Build Levels Higher than NAC

48 35 36

* Representative receptors representing nearly 2,000 individual receptors within Oak Park through the project area

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§ Amount of traffic

– Doubling of traffic is 3 dB(A) increase (barely perceptible)

§ Traffic composition § Distance from roadway to receptor

– Doubling distance is 4.5 dB(A) reduction

§ Land cover type between roadway & receptor

(vegetation or pavement)

§ Vehicle speed & traffic control § Topography & elevation between roadway & receptor

What Can Affect Traffic Noise Levels?

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Existing Ramps at Harlem Avenue

Condo

100,000 ADT Westbound I-290 (no-build) 26,000 Ramp ADT Existing Ramps

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2nd Floor

§ 11,000 ramp ADT (Build) vs, 100,000 WB mainline ADT § Analysis is without noise walls

Proposed Ramps at Harlem Avenue

  • 7 dB(A)

3rd Floor 1st Floor

  • 4 dB(A)
  • 2 dB(A)

Proposed retaining wall shields mainline noise at Harlem Avenue Westbound I-290 Traffic

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Existing Mainline Near Proposed WB Ramp Terminal

100,000 ADT Westbound I-290 (no-build)

Kenilworth Ave. & Harrison St.

Existing slope Harrison St.

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Proposed Harlem Avenue WB Ramp Terminal

Kenilworth Ave. & Harrison St.

100,000 ADT Westbound I-290

Change 0 dB(A)

Proposed retaining wall shields mainline & ramp noise near Kenilworth Avenue. WB Off- Ramp 11,000 ADT Harrison St.

§ No net change in noise level due to proposed design § Without noise walls

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Harlem Ave. Ramp Geometry Noise Sensitivity Analysis

EB on ramp shifts south

Noise Receptor

Key findings:

§ Mainline is the predominant noise source § Ramp location does not significantly affect overall noise levels

Noise Receptor Noise Receptor Noise Receptor

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VISUALIZATIONS

§ 3D Model § Before & After Photo Simulations

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PROPOSED DESIGN FEATURES

§ Expressway lowered by 8 ft. & shifted by 25 ft. § Proposed design features

– Ramps split – high volume ramp shifted further south – Traffic volume tradeoff

§ 11,000 ramp ADT instead of 100,000 WB I-290 ADT

§ Design offers built-in noise reductions – up to 7dba § Ramp design does not influence air quality § Improved bike & pedestrian environment

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NEXT STEPS

§ Follow up presentations/discussions as requested § Aesthetics development § Austin Boulevard presentation - September