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Perdido River and Bay - Florida Department of Environmental ...

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Water Quality Status Report: <strong>Perdido</strong> <strong>River</strong> <strong>and</strong> <strong>Bay</strong><br />

51<br />

Category 5 waterbodies are determined to be impaired <strong>and</strong> require<br />

TMDLs. These are included on the Verified List <strong>of</strong> impaired waters<br />

adopted by the <strong>Department</strong>’s Secretary. However, no waters are formally<br />

assigned to this category until the listing process has been completed, even<br />

though sufficient data may be available <strong>and</strong> a waterbody may meet the<br />

requirements for impairment under the IWR.<br />

Planning Units<br />

The <strong>Perdido</strong> <strong>River</strong> <strong>and</strong> <strong>Bay</strong> Basin encompasses approximately 1,219<br />

square miles, 399.6 square miles <strong>of</strong> which is within <strong>Florida</strong>. To provide a<br />

more detailed geographic basis for identifying <strong>and</strong> assessing water quality<br />

improvement activities, the basin was subdivided into smaller areas called<br />

planning units. Planning units in this basin were based on hydrological<br />

units. Planning units help organize information <strong>and</strong> management strategies<br />

around prominent watershed characteristics.<br />

Water quality assessments were conducted for waterbody segments<br />

within planning units. Each <strong>of</strong> these smaller, hydrologically based drainage<br />

areas within a planning unit is assigned a unique waterbody identification<br />

number (WBID). Waterbody segments are assessment units (or geographic<br />

information system polygons) that the <strong>Department</strong> used to defi ne waterbodies<br />

when it biennially inventoried <strong>and</strong> reported on water quality to the<br />

EPA under Section 305(b) <strong>of</strong> the federal Clean Water Act. These WBIDs<br />

are the assessment units identified in the <strong>Department</strong>’s lists <strong>of</strong> impaired<br />

waters submitted to the EPA in reports under Section 303(d) <strong>of</strong> the Clean<br />

Water Act.<br />

Although WBIDs <strong>of</strong>ten encompass several waterbodies, water quality<br />

data usually reflect the main waterbody conditions within a polygon. In<br />

some instances, however, the data from several waterbodies within the polygon<br />

have been aggregated. As the water quality assessments are refined in<br />

Phase 2 <strong>of</strong> the watershed management cycle, individual waterbodies within<br />

these aggregations that have unique water quality concerns will be assigned<br />

unique WBIDs <strong>and</strong> evaluated individually.<br />

The <strong>Perdido</strong> <strong>River</strong> <strong>and</strong> <strong>Bay</strong> Basin contains two planning units:<br />

<strong>Perdido</strong> <strong>River</strong> <strong>and</strong> <strong>Perdido</strong> <strong>Bay</strong>. Figure 3.2 shows their locations <strong>and</strong><br />

boundaries. In general, planning units are delineated as the drainage<br />

boundaries <strong>of</strong> watersheds that drain to major rivers <strong>and</strong> bays. Major river<br />

<strong>and</strong> bay watersheds in the Panh<strong>and</strong>le are typically defined by unique<br />

hydrologic unit (HUC) codes.<br />

The remainder <strong>of</strong> this chapter provides a general description <strong>of</strong> each<br />

planning unit, information on l<strong>and</strong> use <strong>and</strong> potential point sources <strong>of</strong> pollution,<br />

water quality assessments for individual waterbody segments, <strong>and</strong><br />

summaries <strong>of</strong> ecological issues <strong>and</strong> watershed quality improvement plans<br />

<strong>and</strong> projects.<br />

To determine the status <strong>of</strong> surface water quality in the <strong>Perdido</strong> <strong>River</strong><br />

<strong>and</strong> <strong>Bay</strong> Basin, chemistry data, biological data, <strong>and</strong>, if available, fi sh<br />

consumption, bathing beach closures, <strong>and</strong> shellfish-harvesting advisories<br />

were evaluated to determine potential impairment. Appendix B contains

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