3.0 Affected Environment - Knik Arm Bridge and Toll Authority
3.0 Affected Environment - Knik Arm Bridge and Toll Authority
3.0 Affected Environment - Knik Arm Bridge and Toll Authority
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<strong>Knik</strong> <strong>Arm</strong> Crossing DraftFinal EIS<br />
<strong>Affected</strong> <strong>Environment</strong><br />
<strong>and</strong> explosives (OE) <strong>and</strong> soil <strong>and</strong> ground water contamination from leaking underground<br />
storage tanks, aboveground storage tanks, pesticides, <strong>and</strong> other chemical discharges.<br />
The ISA was prepared in general accordance with corridor screening guidelines as defined by<br />
the American Association of State Highway <strong>and</strong> Transportation Officials in Hazardous<br />
Waste Guide for Project Development (1990) <strong>and</strong> FHWA guidance documents on hazardous<br />
materials (FHWA 1980).<br />
Known <strong>and</strong> potential hazardous material sites in the Study Area were identified through<br />
review of federal <strong>and</strong> State databases, agency interviews, aerial photography, <strong>and</strong> site visits.<br />
Also, readily available information regarding known contaminated sites on Elmendorf was<br />
obtained from Internet databases <strong>and</strong> other information repositories. Identification of<br />
minimum search distances <strong>and</strong> the types of databases required for review were based on<br />
ASTM International’s St<strong>and</strong>ard E 1527-00, “St<strong>and</strong>ard Practice for Phase I <strong>Environment</strong>al<br />
Site Assessment Process” (2000). Initially, all contaminated sites listed in federal <strong>and</strong> State<br />
databases within 0.5 mile of the proposed alternatives were identified.<br />
For the purposes of investigating hazardous materials concerns, the Study Area was defined<br />
as the area within 100 feet of the outer limits of the ROW for the proposed alternatives. The<br />
Study Area has been organized into three subareas, from west to east:<br />
• the Mat-Su approach alternatives between the Burma Road intersection <strong>and</strong> the west<br />
shore of <strong>Knik</strong> <strong>Arm</strong> (includes the Point MacKenzie Road <strong>and</strong> the Northern Access<br />
Alternatives)<br />
• the two Southern Alignment bridge lengths across <strong>Knik</strong> <strong>Arm</strong> 28<br />
• Anchorage approach alternatives (includes the Degan <strong>and</strong> Erickson Alternatives).<br />
In the ISA, the Study team rated each known <strong>and</strong> potential hazardous material location for its<br />
potential to affect the project. The Study Team rated the sites as having a high, medium, low,<br />
or negligible impact risk. High- <strong>and</strong> medium-impact risk ratings were assigned to known or<br />
potentially contaminated sites that could cause contamination of property within 100 feet of<br />
the proposed ROWs. High- <strong>and</strong> medium-impact risk-rated sites are presented below for each<br />
of the Study Area subareas.<br />
3.5.4.1 Mat-Su approach alternatives<br />
Based on the ISA screening process, no hazardous waste or contaminated sites were located<br />
within the KAC Study Area for either the Point MacKenzie Road or Northern Access<br />
Alternatives. However, both the Point MacKenzie Road <strong>and</strong> Northern Access Alternatives<br />
would directly affect the Former Susitna Gunnery Range (FSGR). Except for approximately<br />
1 mile at the northern terminus of the Study Area, all of the Mat-Su approach alternatives<br />
would be within the former FSGR. The 86,570-acre FSGR is located northwest of Elmendorf<br />
28 The 14,000-foot bridge length was found to not be financially feasible <strong>and</strong> did not meet Purpose <strong>and</strong> Need<br />
criteria, however, this alternative was carried forward solely for comparative evaluation based on requests<br />
from environment resource <strong>and</strong> permitting agencies.<br />
3-124 12/18/07