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I-10 Twin Peaks Traffic Interchange, Environmental Assessment

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Affected Environment and <strong>Environmental</strong> Impacts October 2005<br />

within the model to accommodate areas where the roadway climbs and traffic<br />

volumes and speeds differed. Roadway geometry, topography, and receiver<br />

locations and elevations were established from MicroStation plan sets from project<br />

design engineers and PAG aerial photos and digital terrain model files.<br />

One hundred twenty-six representative properties throughout the study area were<br />

selected as model receiver locations (see Figures 4-4a-d). Residences and<br />

businesses within the study area were chosen as representative sensitive noise<br />

receivers and STAMINA was used to estimate the noise levels at these receiver<br />

locations under existing (2004) traffic and under predicted conditions (2030). The<br />

results of the analysis are presented in the table in Appendix C. Noise receivers<br />

were designed as NR# along the north side of <strong>Twin</strong> <strong>Peaks</strong> Road, RS# along the<br />

south side of <strong>Twin</strong> <strong>Peaks</strong> Road, I<strong>10</strong>F# in the area of I-<strong>10</strong> and its frontage roads, or<br />

LVR# along Linda Vista Boulevard.<br />

Impacts<br />

No Build Alternative<br />

The noise monitoring and modeling analyses suggested that the NAC are exceeded<br />

at a number of locations within the study area. Because traffic noise levels are<br />

dependent upon traffic volumes, and traffic volumes are predicted to increase in the<br />

area, noise levels would increase also. As a result additional properties in the project<br />

area would be impacted by traffic noise regardless of whether or not the project is<br />

constructed. According to the table in Appendix C, the entire area near I-<strong>10</strong> (all<br />

receivers beginning I<strong>10</strong>F#) exceeds the NAC under current conditions. All<br />

modeled locations in this area are commercial land uses. Although one residential<br />

property exists within this area, this residence would be acquired by the proposed<br />

improvements; therefore, this residential site was not modeled. With the exception<br />

of this area near I-<strong>10</strong>, only one other receiver (LVR12) within the study area<br />

approached or exceeded the NAC for the year 2004. This receiver, located at the<br />

intersection of Linda Vista Boulevard and Manatee Drive is adjacent to Linda<br />

Vista Boulevard and substantially lower in elevation than the roadway. This<br />

residence (as opposed to most in the area) is not separated from the roadway by a<br />

wall. It is reasonable to assume that, with additional traffic growth, additional<br />

residences in this area would exceed the NAC.<br />

Preferred Alternative<br />

Temporary Impacts<br />

Construction noise differs from traffic noise in several ways:<br />

• Construction noise lasts only for the duration of the construction contract,<br />

and it is usually limited to daylight hours when most human activity<br />

occurs.<br />

• Construction activities generally are of a short-term nature, and depending<br />

on the nature of construction operations, it could last from seconds (e.g., a<br />

truck passing a receiver) to months (e.g., constructing a bridge).<br />

Interstate <strong>10</strong> <strong>Traffic</strong> <strong>Interchange</strong> at<br />

<strong>Twin</strong> <strong>Peaks</strong>/Linda Vista<br />

4-51<br />

Project No.: NH-0<strong>10</strong>-D (AIW)<br />

TRACS No.: <strong>10</strong> PM 236 H5838 01D

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