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4 <br /> ultimate success of the project should be judged according to these same <br /> measurements at the mitigation site. <br /> Criteria should be developed for assessing the progress of the project during <br /> its developmental stages as well. Assessment criteria should include rates of <br /> plant growth, plant health, and evidence of natural reproduction. Success <br /> criteria should be geared toward equaling or exceeding the quality of the <br /> highest quality habitat to be affected. In other words, the mitigation effort <br /> would be deemed a success in relation to this goal if the mitigation site met <br /> or exceeded habitat measurements at a "model" site (plant cover, density, <br /> species diversity, etc. ) . <br /> The plan should present the proposed ground elevations at the mitigation site, <br /> along with elevations in the adjacent areas. A comparison of the soils of the <br /> proposed mitigation and adjacent areas should also be included in the plan, <br /> and a determination made as to the suitability of the soils to support <br /> habitats consistent with the mitigation goals. <br /> Because" wetland ecosystems are driven by suitable hydrological conditions, <br /> additional information must be developed on the predicted hydrology of the <br /> mitigation site; The plan should describe the depth of the water table, and <br /> the frequency, duration, areal extent, and depth of flooding which would occur <br /> on the site. The hydrologic information should include an analysis of extreme <br /> conditions (drought, flooding) as well as typical conditions. <br /> The plan must include a time frame for implementing the mitigation in relation <br /> to the proposed project. We recommend that mitigation be initiated prior to <br /> the onset of construction. If there will be a substantial net <br /> lag between <br /> project construction and completion of the mitigation, a net loss of habitat <br /> values would result, and more mitigation would be required to offset this <br /> loss. <br /> Generally, monitoring of the mitigation site should occur annually for at <br /> least the first five years, semi-annually for years 6 through 11, and every <br /> five years thereafter until the mitigation has met all success criteria. The <br /> monitoring period should begin again if success criteria are not met during <br /> the first five years. Some projects will require monitoring throughout the <br /> life of the project. Reports should be -prepared after each monitoring <br /> session. <br /> The plan should require the preparation of "as-built" plans. Such plans <br /> provide valuable information, especially if the mitigation effort fails. <br /> Similarly, a "time-zero" report should be mandated. This report would <br /> describe exactly what was done during the construction of the mitigation <br /> project, what problems were encountered, and what corrections or modifications . <br /> to the plans were undertaken. <br /> The plan should detail how the site is to be maintained during the mitigation <br /> establishment period, and how long the establishment period will be. It will <br /> also be important to note what entity will perform the maintenance activities, <br /> and what entity will untimately own and manage the site. In addition, a <br /> mechanism to fund the maintenance and management of the site should be <br /> established and identified. A permanent easement should be placed on the <br /> property used for the mitigation that would preclude incompatible activities <br /> on the site in perpetuity. <br /> Finally, in some cases, a performance bond may be required as part of the <br /> mitigation plan. The amount of the bond should be sufficient to cover the <br /> costs of designing and implementing an adequate mitigation plan (and <br /> purchasing land if needed) should the proposed plan not succeed. <br /> C-42 <br />