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Mitigation and Modification Alternatives <br />and steel, are subjects influencing the design process. Access routes and construction area <br />limits also help define the temporary and permanent ecological impacts associated with the <br />construction activity and the related ecological mitigation which may be necessary. <br />With this basic information available, preliminary engineering, which provides the basis <br />for an improved construction cost estimate, can proceed simultaneously with initial ecological <br />evaluations and preliminary permitting activity. Should engineering design options exist they <br />would be re-examined at this stage prior to proceeding to final design. Public and landowner <br />involvement and resolution of related concerns is a critical element at this stage in order to <br />proceed with final preconstruction activities. Remaining investigations would be conducted, <br />followed by final engineering design and completion of related ecological activities. Final <br />permitting activity is followed by construction. <br />Special construction issues at the sites of these structures will include: <br />• Mitigation of instream and riparian ecological disturbance during construction; <br />• Timing of construction to permit uninterrupted diversion of waters for off-stream <br />use; <br />• Timing of construction to minimize ecological disturbance; <br />• Timing of construction to minimize water handling requirements. <br />Fish Passage Criteria <br />Knowledge of fish behavioral characteristics is needed to determine the low-flow fish <br />passage design criteria. Fortunately, design and monitoring of the City of Craig diversion <br />structure have laid valuable groundwork here. <br />Most of the structure types have small enough head differentials to permit instream <br />passage by swimming. Design information required includes maximum swimmable velocity for <br />the full range of flows, minimum depth, maximum burst speed and duration (to determine <br />slope), and fish movement characteristics so that approach channels can be configured to direct <br />fish movement to passage routes. Rock size is also a significant consideration as rock voids <br />must either be large enough to swim through or small enough to be grouted closed (to force <br />water into navigable sections). <br />Fish passage provisions at each site are uniquely different due to site physical constraints <br />and the physical and behavioral characteristics of fish. In general, passage criteria address the <br />following key characteristics: <br />• Attraction water to signal the passage route. <br />• Adequate quantity, depth and velocity of flow to permit passage. <br />• Pools for resting areas, if the passage exceeds the swim-through capability of the <br />fish. <br />4-10