|
A
Type II project
includes studying noise abatement
for:
-
Existing
Fully controlled-access
state highways
(Freeways/Interstates).
-
State highways in urban areas.
-
Noise
abatement projects sponsored
by a state or local
government sponsor.
Federal Regulations
For different land uses, there are
different noise criteria for
impacts.
|
NAC
Leq(h), dBA* |
Description of Land Use |
|
57
(Exterior) |
Lands on which serenity and
quiet are of extraordinary
significance and serve an
important public need and
where the perservation of
those qualities is essential
if the area is to continue
to serve its intended
purpose. |
|
67 (Exterior) |
Picnic areas, recreation
areas, playgrounds, active
sports areas, parks,
residences, motels, hotels,
schools, churches,
libraries, and hospitals. |
|
72
(Exterior) |
Developed lands, properties,
or activities not included
in the other categories. |
|
-- -- |
Undeveloped Lands. |
|
52
(Interior) |
Residences, motels, hotels,
public meeting rooms,
schools, churches,
libraries, hospitals, and
auditoriums. |
A traffic noise impact occurs when
noise levels approach, meet or
exceed the
Noise Abatement Criteria (NAC)
warranting a noise abatement
analysis.
IDOT Policy
In Illinois, traffic noise impacts
are determined to occur in the
following situations:
Design year (typically 20 years
into the future) traffic noise
levels are predicted to
approach, meet, or exceed the
NAC, with approach defined as 1
dBA from NAC.
OR
Design year (typically 20 years
into the future) traffic noise
levels are predicted to
substantially increase (greater
than 14
dBA) over existing
traffic-generated noise levels.
Noise Monitoring
Noise
monitoring is conducted at selected
locations to measure existing noise
levels.
A typical noise meter is about the
size of a large camera and is placed
on a tripod approximately 5 feet
high.
Each monitoring period is
approximately 10 minutes.
Noise Monitoring Location
Typical Noise Meter
During the noise monitoring,
automobile and truck traffic volumes
are counted and other conditions
such as weather, wind speed, and
other background noises are recorded
on field sheets. Noise
monitoring is conducted at times
when there is peak traffic traveling
at peak speeds. Noise monitoring
provides an instantaneous snapshot
of existing highway noise levels
including other common background
sources (i.e. lawn mowers, barking
dogs, and playground areas).
Noise Monitoring versus Computer
Noise Modeling
Noise monitoring is a tool that
only provides information for
existing
conditions. Computer
noise modeling is used to predict
traffic noise levels for existing
and future conditions and is the
tool used to predict potential
traffic noise impacts.
Computer Noise Modeling
The
FHWA
approved computer noise model is
used to predict noise levels.
-
Select representative noise
sensitive areas
-
Determine model inputs
- Compare
existing and future noise levels
predicted by the model to
Illinois policy for
purposes of determining noise
impacts
Scenarios evaluated in the model
include:
|
Condition |
Definition |
|
Existing |
Existing Traffic Volumes and
Existing Roadway Layout |
|
No Build |
Projected Traffic Volumes and
Existing Roadway Layout |
|
Proposed Build |
Traffic Volumes and Proposed
Roadway Layout |
The
first step in conducting a noise
analysis is to select representative
receptors that characterize
Noise
Sensitive Areas (NSA)
with:
-
Similar land use
-
Similar distance to roadway
-
Same basic topography
IDOT defines a receptor as a
sensitive land use where frequent
human use occurs and where a low
noise level would be of benefit.
Receptors typically include homes,
schools, hospitals, nursing homes,
parks, motels, and may include
business locations.
There are
10 inputs needed to estimate noise
by model:
Predicted noise levels for each
receptor are compared to the Noise
Abatement Criteria (NAC). For
example, (as shown on the chart
below) the noise level at Receptor
R1 in the Existing and Future
Without Improvement conditions, meet
the NAC. The Future With
Improvement would raise the noise
level above the NAC.
Therefore, a noise abatement
evaluation would be required.
For Receptor R2 all noise levels
are below the NAC of 67 dBA.
Therefore, no further evaluation is
required.
|
Receptor |
Description |
Existing |
Future Without Improvement |
Future With Improvement |
Noise
Abatement Analysis |
|
R1 |
Multi-family |
63 |
65 |
68 |
Y |
|
R2 |
Single Family |
60 |
62 |
64 |
N |
|