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Alafia River Minimum Flows and Levels - Southwest Florida Water ...

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1) maintenance of minimum water depths in the river channel for fish<br />

passage <strong>and</strong> recreational use;<br />

2) maintenance of water depths above inflection points in the wetted<br />

perimeter of the river channel to maximize aquatic habitat with the least<br />

amount of flow;<br />

3) protection of in-channel habitat for selected fish species <strong>and</strong><br />

macroinvertebrate assemblages;<br />

4) inundation of woody habitats including snags <strong>and</strong> exposed roots in the<br />

stream channel; <strong>and</strong><br />

5) maintenance of seasonal hydrologic connections between the river<br />

channel <strong>and</strong> floodplain to ensure floodplain structure <strong>and</strong> function.<br />

These goals are consistent with management goals identified by other<br />

researchers as discussed in Chapter 1. The rationale for identifying these goals<br />

<strong>and</strong> the habitats <strong>and</strong> ecological indicators associated with the goals are<br />

addressed in subsequent sections of this chapter. Field <strong>and</strong> analytical methods<br />

used to assess hydrologic requirements associated with the habitats <strong>and</strong><br />

indicators are presented in Chapter 4, <strong>and</strong> results of the minimum flows <strong>and</strong><br />

levels analyses are presented in Chapter 5.<br />

3.3.1 Fish Passage <strong>and</strong> Recreational Use<br />

Ensuring sufficient flows for the passage or movement of fishes is an important<br />

component of the development of minimum flows. Maintenance of these flows is<br />

expected to ensure continuous flow within the channel or river segment, allow for<br />

recreational navigation (e.g., canoeing), improve aesthetics, <strong>and</strong> avoid or lessen<br />

potential negative effects associated with pool isolation (e.g., high water<br />

temperatures, low dissolved oxygen concentrations, localized phytoplankton<br />

blooms, <strong>and</strong> increased predatory pressure resulting from loss of habitat/cover).<br />

Tharme <strong>and</strong> King (1998, as cited by Postel <strong>and</strong> Richter 2004) in developing a<br />

"building block" approach for South African rivers listed the retention of a river's<br />

natural perenniality or nonperenniality as one of eight general principles for<br />

managing river flows. For many rivers within the District, flows <strong>and</strong><br />

corresponding water depths adequate for fish passage are currently or were<br />

historically maintained by baseflow during the dry season. For example, in the<br />

upper Peace <strong>River</strong>, historical flows were sufficient for maintaining a naturally<br />

perennial system <strong>and</strong> flow was sufficiently high during the low flow season to<br />

permit passage of fish along most of the river segment (SWFWMD 2002).<br />

Recent flows in the upper Peace <strong>River</strong> have not, however, been sufficient for fish<br />

passage much of the time. Historic flows in other District rivers, such as the<br />

Myakka <strong>River</strong> were probably intermittent, historically, but have increased in<br />

recent years. Evaluation of flows sufficient for fish in support of minimum flows<br />

development may, therefore, involve consideration of historic or recent flow<br />

conditions with respect to perenniality <strong>and</strong> the likelihood of fish passage being<br />

maintained naturally (i.e., in the absence of consumptive water use).<br />

3-3

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