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2012 FDOT Mitigation Plan - Southwest Florida Water Management ...

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groundwater evaluation for the Cockroach Bay area was required to determine the extent of freshwater and<br />

various saltwater wetland creation and restoration components.<br />

Pre- and post-construction habitat conditions are depicted on the attached aerial figures and photographs. Dominant<br />

vegetation in the emergent marsh zones of both sites include black needle rush (Juncus roemericanus) and soft-stem<br />

bulrush (Scirpus validus). Subdominant species include arrowhead (Sagittaria lancifolia), pickerelweed (Pontederia<br />

cordata), water hyssops (Bacopa monnieri), water pennywort (Hydrocotyle umbellate), saltmash aster (Aster<br />

subsulatus), and ludwigia (Ludwigia leptocarpa). Dominant vegetation in the high marsh/wet prairie includes sand<br />

cordgrass (Spartina bakeri), marsh-hay cordgrass (Spartina patens), salt grass (Distichlis spicata), hairawn muhly<br />

(Muhlenbergia capillaries). Subdominant species include seaside oxeye (Borriachia frutescens). The emergent zones<br />

and wet prairies are evident on the post construction aerials (Figures D & E). Cabbage palm (Sabal palmetto), saw<br />

palmetto (Serenoa repens) and various sedge species provide the dominant species in the coastal hammock areas that<br />

buffer the constructed marshes. Cattails (Typha spp.) comprise less than 1% total coverage. Appropriate wetland<br />

hydrology and hydroperiods are present within the created marsh habitat, providing ephemeral marsh habitats of<br />

variable hydroperiods and concentrated emergent zones during the dry seasons (Figure E – existing habitats aerial,<br />

photographs).<br />

The concentration and variation of surface waters in the marshes provides substantial foraging opportunities for wildlife<br />

use. As depicted on the figure aerials, the created marshes are buffered by upland restoration areas, including a 20-acre<br />

upland parcel located between the two designated mitigation areas. This combination and mosaic of upland and wetland<br />

habitats at Cockroach Bay provide more opportunities for wildlife access, foraging and denning. Observed and<br />

documented wildlife use of the project sites is extensive, evident by the substantial foraging opportunities available to the<br />

extensive bird populations that visit the created marsh habitats. Commonly observed species include red-winged<br />

blackbird (Agelaius phoeniceus), anhinga (Anhinga anhinga), great blue heron (Ardea herodiaa), cattle egret (Bubulcus<br />

ibis), red-tailed hawk (Buteo jamaicensis), red-shouldered hawk (Buteo lineatus), great egret (Casmerodius albus),<br />

turkey vulture (Cathartes aura), belted kingfisher (Ceryle alcyon), killdeer (Charadrius vociferous), black vulture<br />

(Coragyps atratus), little blue heron (Egretta caerulea), snowy egret (Egretta thula), tricolored heron (Egretta tricolor),<br />

white ibis (Eudocimus albus), common moorhen (Gallinula chloropus), <strong>Florida</strong> sandhill crane (Grus canadensis),<br />

wookstork (Mycteria americana), white pelican (Pelecanus erythrorhynchos), double-crested cormorant (Phalacorcorax<br />

auritus), rosette spoonbill (Platalea ajaja), glossy ibis (Plegadis falcinellus), common grackle (Quiscalus quiscula), royal<br />

tern (Stema maxima), American robin (Turdus migratorius), mourning dove (Zenaida macroura), mosquito fish<br />

(Gambusia holbrooki), and raccoon (Procyon lotor).<br />

Attachment B – Maintenance & Monitoring, Success Criteria<br />

The maintenance activities are conducted by a licensed herbicide contractor working for the SWFWMD through 2010,<br />

and predominantly associated with herbicide eradication and control of invasive exotic vegetation that primarily included<br />

minimal coverage of cattails generated in the emergent zones and Brazilian pepper in the coastal hammock.<br />

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