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Final Environmental Impact Report - Whittier Bridge/I-95 ...

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<strong>Whittier</strong> <strong>Bridge</strong>/I-<strong>95</strong> Improvement Project FEIR<br />

Chapter 1.0: Changes Since the Draft <strong>Environmental</strong> <strong>Impact</strong> <strong>Report</strong> and Resolution of Additional Issues<br />

preserved or extended to the maximum extent feasible. The post construction condition will result in<br />

a 70-foot side slope with natural vegetation, and consequently there will be a net environmental<br />

benefit to the RFA. No direct impacts will occur to the wetlands under the Amesbury end of the<br />

bridge.<br />

b. Stormwater is managed according to standards established by the Department in its<br />

Stormwater Policy.<br />

The project will comply with stormwater management requirements.<br />

c. Proposed work does not impair the capacity of the riverfront area to provide important<br />

wildlife habitat functions. Work shall not result in an impairment of the capacity to provide<br />

vernal pool habitat identified by evidence from a competent source, but not yet certified. For<br />

work within an undeveloped riverfront area which exceeds 5,000 square feet, the issuing<br />

authority may require a wildlife habitat evaluation study under 310 CMR 10.60.<br />

By constructing the new abutments behind the existing abutments, the project will maintain and<br />

enhance the corridors that currently allow wildlife to cross under the bridge on both the southern and<br />

northern banks of the Merrimack River. All temporarily impacted RFA will be restored in place. The<br />

939 square feet of alteration requiring mitigation in Newburyport will be addressed with 12,200<br />

square feet of on-site restoration of existing degraded areas. The RFA in this area contains several<br />

weedy non-native species, including Norway maple (Acer platanoides), oriental bittersweet<br />

(Celastrus orbiculatus), and Japanese barberry (Berberis thunbergii). The proposed impacts to the<br />

low-quality habitat present in this area will have little to no effect on overall wildlife habitat quality.<br />

In Amesbury, the 6,000 square feet of alteration requiring mitigation will be addressed with 11,800<br />

square feet of on-site restoration of existing degraded areas. The RFA in this area contains a mix of<br />

natives and non-native species, including Norway maple (Acer platanoides), privet (Ligustrum sp.),<br />

and oriental bittersweet (Celastrus orbiculatus). The proposed impacts to the low-quality habitat<br />

present in this area will have little to no effect on overall wildlife habitat quality.<br />

d. Proposed work shall not impair groundwater or surface water quality by incorporating<br />

erosion and sedimentation controls and other measures to attenuate nonpoint source<br />

pollution.<br />

The project will not impair groundwater or surface water quality. The design/build contractor will<br />

incorporate erosion and sedimentation controls during construction to minimize impacts to resource<br />

areas. An environmental monitor will inspect erosion and sedimentation control weekly and after<br />

significant rain events.<br />

(5) Redevelopment Within Previously Developed Riverfront Areas; Restoration and Mitigation.<br />

Notwithstanding the provisions of 310 CMR 10.58(4)(c) and (d), the issuing authority may allow work<br />

to redevelop a previously developed riverfront area, provided the proposed work improves existing<br />

conditions. Redevelopment means replacement, rehabilitation or expansion of existing structures,<br />

improvement of existing roads, or reuse of degraded or previously developed areas. A previously<br />

developed riverfront area contains areas degraded prior to August 7, 1996 by impervious surfaces<br />

from existing structures or pavement, absence of topsoil, junkyards, or abandoned dumping<br />

grounds. Work to redevelop previously developed riverfront areas shall conform to the following<br />

criteria:<br />

1-17

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