Soil Classification Database: Categorization of County Soil Survey Data within the SFWMD Including Natural Soils Landscape Positions

Technical Publication WS-06

by

John Zahina, Ken Liudahl (NRCS), Tim Liebermann, Kurt Saari, Jerry Krenz, and Victor Mullen

October 2001

South Florida Water Management District

Soil Classification Database Table of Contents

TABLE OF CONTENTS

Table of Contents i

List of Tables iii

List of Figures v

Abstract vii

Acknowledgements ix

Introduction 1

General Methods 3 Classification by Depth and Duration of the SHWT ...... 3 Classification by Ecological Community Type...... 9 Classification by NSLP Type ...... 15

Use of the Soil Classifications 23

Summary 25

References 27

Glossary and List of Abbreviations 29

Appendix A: SHWT Classification Codes A-1

Appendix B: Ecological Community Category Definitions B-1

Appendix C: Landscape Classification Categories C-1

Appendix D: Selected Ecological Communities D-1 South Florida Coastal Strand ...... D-1 Sand Pine Scrub ...... D-3 South Florida Flatwoods

i Table of Contents Soil Classification Database

Scrub Cypress ...... D-7 Cypress Swamp...... D-8 Salt Marsh ...... D-10 Sawgrass Marsh ...... D-12 Freshwater Marsh and Ponds...... D-13 Slough ...... D-15

Appendix E: Natural Soil Landscape Positions Classification Database E-1

ii Soil Classification Database List of Tables

LIST OF TABLES

Table 1. Classification Codes Used to Classify Soils by Depth and Duration of the SHWT...... 5 Table 2. Ecological Community Category Definitions...... 10 Table 3. Sorting Criteria for Soils Data by NSLP Type...... 16 Table 4. Dates of Publication of County Soil Surveys by NRCS...... 24 Table A-1. Category Codes and Associated Ranges for the SHWT Used in the Categorization of Duration...... A-2 Table B-1. Category Definitions for the Ecological Community Categories...... B-1 Table C-1. Soil Series within Each NSLP Category with the Largest Aerial Extent...... C-1 Table C-2. Range of Map Unit Values within the NSLP Categories...... C-2 Table E-1. Three Digit Map Unit Symbols Used in the MUID...... E-2 Table E-2. LSPOS Codes...... E-3 Table E-3. Surface Soil Texture Codes...... E-4 Table E-4. Hydrological Group Codes...... E-5 Table E-5. Soil Drainage Class Codes...... E-5

iii List of Tables Soil Classification Database

iv Soil Classification Database List of Figures

LIST OF FIGURES

Figure 1. Map Extent of the Soils Classification Database, Indicated by the Shaded Counties...... 4 Figure 2. Map of the Level 1 SHWT Categories for a Sample Area on the West Side of Lake Okeechobeee...... 6 Figure 3. Map of the Ecological Community Categories for a Sample Area on the West Side of Lake Okeechobeee...... 11 Figure 4. Poster of NSLP (pullout)

v List of Figures Soil Classification Database

vi Soil Classification Database Abstract

ABSTRACT

Keywords: landscape position, soils, SSURGO, GIS

An updated single soil database of soil map units in South Florida, based on groups of similar morphologic characteristics, has improved the ability to visualize the spatial patterns of soils and to extract quantitative data for modeling and other hydrologic analyses. Soil characteristics reflect the complex interaction among topography, climate, vegetation, hydrology, and parent material. In South Florida, very small changes in topography can greatly affect hydrologic response. Soil survey maps compiled by the Natural Resources Conservation Service (NRCS) contain a wealth of spatial and analytical data but have been difficult to apply because of the large size, use of different names, and complexity of the database for each county.

As part of a previous cooperative effort by NRCS and staff at the South Florida Water Management District, spatial layers of county-level soil surveys (Soil Survey Geographic Data Base, or SSURGO) were edgematched and corrected to create a seamless Geographic Information System (GIS) database. The overall database included detailed soils for 19 counties, containing 195,000 polygons, with 909 soil mapping units and 220 distinct soil types. A set of 34 data fields (such as slope, hydric, and surface texture) was developed and checked and corrected for each mapping unit and is identified in the Natural Soils Lnadscape Positions (NSLP) database. Three classifications of the soil database were conducted, categorizing the large soils database into a relatively small number of categories (12 or less). These three classifications are based on depth and duration of the seasonal high water table, ecological community types, and NSLP types. The NSLP is a more complex classification based on the depth of the seasonal high-water table, soil morphological characteristics, and geographical location. These parameters were used to define 10 natural landscape positions that are significant to South Florida (water, tidal, marl and rocky, Everglades peat, muck depressions, sand depression, flats, flatwoods, knolls, Central Ridge & Dunes, and urban or made lands). The initial criteria were adjusted and evaluated until a consistent and useful classification was obtained.

vii Abstract Soil Classification Database

viii Soil Classification Database Acknowledgements

ACKNOWLEDGEMENTS

This project was a cooperative effort between the South Florida Water Management District (SFWMD) and the Natural Resources Conservation Service (formerly Soil Conservation Service). The SFWMD provided Geographical Information System (GIS), graphical, and planning support. Dale Woodruff provided technical assistance in analysis of the data base and map production. Steve Traver and Rick Miessau provided technical support on the creation the website. Ellen Negley and Debra Case provided graphical support for the production of the poster and some graphical aspects of this technical publication.

We would like to recognize the members of the Planning and Water Resource Evaluation Departments who converted the soils maps into digital form and updated and improved the SSURGO databases under SFWMD contract C-3119. Supporting staff includes Ed Biggs, Joe Chapa, Tim Scharff, Tim Liebermann, and Mike Rose. These coverages and databases form the foundation of the work described here.

This project has been funded in part by the United States Environmental Protection Agency (USEPA) under Assistance Agreement ID Number X9948864-96-0 to the South Florida Wetlands Conservation Strategy. The contents of this document do not necessarily reflect the views and policies of the USEPA, nor does mention of trade names or commercial product constitute endorsement or recommendation for use.

ix Acknowledgements Soil Classification Database

x Soil Classification Database Introduction

INTRODUCTION

The Soil Classification Database is a reclassification of county soil survey data published by the Natural Resources Conservation Service (NRCS), formerly the Soil Conservation Service (SCS). A total of 907 soil map units were sorted by similar hydrological, morphological, and vegetation characteristics. New classification fields resulting from this process were added to the database to allow the user to group soils data into categories based upon specific characteristics.

The purpose of developing these new classification fields was to bring the large digital county soil database into a single user-friendly database, and to provide a clearer understanding of the relationships that exist between soil, hydrology, and the vegetation community. The resulting data offers a simplified soil landscape layer within the South Florida Water Management District’s (SFWMD) Geographical Information System (GIS) that contains 34 fields.

The Soil Classification Database provides modelers, planners, and resource managers with an interpretation of the natural landscape not available from existing sources. Because the soils data can be categorized by hydrological characteristics and relative topography, regional patterns of hydrology become more evident. Correlation of hydrological conditions to ecological communities allows the soils data to be used to visualize the extent of certain habitats. This database can also be useful in determining the historical and present day areal extent of wetlands.

This document describes each classification of the soils in separate sections. The appendices contain the data table used in these classifications and other reference materials associated with the database. Other products resulting from this project include a poster (see foldout in the back of this document), a CD-ROM that contains the database, and a website (http://www.sfwmd.gov/org/pld/proj/wetcons/nslp/nslp_home.html). Each of these supplemental products are designed to distribute the data, map layer, and other information about this project to a wide audience of users.

The Soils Classification Database does not improve the accuracy, reliability, or quality of the soils data; the method presented here seeks only to improve the usability of the data. Please refer to the section entitled “Use of the Soils Classifications” before applying any classifications outlined in this publication.

1 Introduction Soil Classification Database

2 Soil Classification Database General Methods

GENERAL METHODS

As a base map layer, we used the seamless GIS coverage of the digital Soil Survey Geographic Data Base (SSURGO) for 16 counties within the boundaries of the SFWMD. This map layer was created as part of a previous cooperative effort between the SFWMD and the NRCS (contract #C-7271). Three additional counties (Indian River, Hardee, and DeSoto) which lie along the SFWMD boundary were included in the study area (Figure 1). Thirty-five data fields from the SSURGO Component (COMP) table and the Field Office Technical Guide (FOTG) table (SCS, 1992) for these 19 counties were combined into a single database. A list of the fields available in the Soil Classification database with the respective type and origin of the data are presented in Appendix E. The database was then modified so that only the largest soil component (SEQNUM 1 in SSURGO COMP table) of the map unit (MUID) was retained.

The edited database was then verified item-by-item across all data fields to search for errors and to update older soil data to values currently defined by the NRCS. These updates included a change from alphabetic to numeric identifiers for soils map units and a revision of the range for the seasonal high water table (SHWT) for a few flatwood soils.

The database was sorted for a number of value ranges for different characteristics, which were used to create new classification categories. The classification schemes are: 1) depth and duration of the SHWT, 2) ecological community types, and 3) NSLP type, which includes hydrological, morphological, and geographical considerations. The category ranges for these classifications are described in the following sections. The total area in each classification category were calculated (for county and study area) and are presented in the Appendices. Maps were created for each of the respective classification schemes by sorting on the respective category field, GIS software was then utilized to generate a map layer from the spatial database.

CLASSIFICATION BY DEPTH AND DURATION OF THE SHWT

This classification is based on the depth (relative to the soil surface) and persistence of the SHWT in an average year. The category designations use a multi-level numerical coding similar to the Florida Land Use Coding Classification System (SFWMD, 1994). Generally, the range of values for the depth to the SHWT, as defined for each map unit in SSURGO, were sequentially classified into eight groups (one group for “no data” is included). Each group contains the map units that have a SHWT depth and duration within a specified range. For example, one group contains all map units that have a SHWT above the soil surface. Another group contains all map units that have the upper range of the SHWT at the soil surface. These groups were arranged along a gradient of values and designated Level 1 category codes (100, 200, 300, etc.). Lower numbers indicate drier/shorter hydrology. Subgroups of SHWT values within each Level 1 category are designated by a Level 2 code (10, 20, 30, etc.). The Level 2 codes are the

3 General Methods Soil Classification Database

Orange

Osceola

Polk Indian River Okeechobee N Hardee Highlands St. Lucie De Soto W E Martin Glades Charlotte

Hendry S Lee Palm Beach

Broward Collier

Miami- Monroe Dade

Figure 1. Map Extent of the Soils Classification Database, Indicated by the Shaded Counties.

4 Soil Classification Database General Methods actual map unit ranges for the SHWT and were also assigned to reflect a gradient of values (i.e., 510 = 1.0 to 1.5 ft. below the soil surface; 520 = 1.0 ft. below the soil surface; 530 = 0.5 to 1.5 ft. below the soil surface; and 540 = 0.5 to 1.0 ft. below the soil surface). Because SHWT ranges are inconsistent between map units, the ranges at Level 2 are not mutually exclusive and overlap between classes. Level 3 codes (1, 2, 3, etc.) indicate the duration of the SHWT and is expressed as the number of months minus three. Level 1, Level 2, and Level 3 codes are given as separate fields (“SHWT-L1”, “SHWT-L2”, and “SHWT-L3”, respectively) in the database. Table 1 contains a general description of the category codes used in this classification. Please refer to Appendix A for a complete listing of category codes and related SHWT ranges.

Table 1. Classification Codes Used to Classify Soils by Depth and Duration of the SHWT.

Classification Level Level Code Description

100 SHWT deep, from 2 to more than 6 ft. below the soil surface. 200 Beaches, saltwater table from 0 to 6 ft. below the soil surface. 300 SHWT varies widely, from 0 to 6 ft. below the soil surface. 400 SHWT ranges1.0 to 4.0 ft. below the soil surface. Level 1: 500 SHWT ranges 0.5 to 1.5 ft. below the soil surface. Main Categories 600 SHWT-H at the soil surface. 700 SHWT-H above soil surface. 800 Water areas. 900 No data available.

Level 2: 10, 20, 30, Map unit SHWT ranges within a category Category Subgroups 40, 50, 60, 70

Level 3: 0 through 9 SHWT duration (code no. is equal to the duration of months minus 3). SHWT Duration

This classification method was developed to give the user a means to map local topography and hydrology, based on the location of the SHWT in an average year under natural conditions. Specifically, this method can also be useful in determining hydrological patterns and the course of major flow ways within the landscape. Category codes have been assigned to reflect a hydrological gradient. Lower category code numbers indicate a drier hydrological regime with respect to duration of the SHWT, depth to the SHWT, or duration of flooding or ponding of water on the soil surface. For instance, in an average year under natural conditions, a category 713 map unit has a shorter hydroperiod than a 719 map unit, since the latter has a SHWT that lasts 6 months longer. Similarly, a category 134 map unit lies higher in the landscape (i.e., has a greater depth to the SHWT) than a 713 map unit. A map was created using the Level 1 field data (Figure 2). It is important to remember that soil conditions are predictable over periods of time, but they are not predictable from year to year. For example, soil scientists can predict with a fairly high degree of accuracy that a given soil will have a high water table within certain depths in most years, but they cannot assure that a high water table will always be at a specific level in the soil on a specific date (NRCS, 1998).

5 General Methods Soil Classification Database

Figure 2. Map of the Level 1 SHWT Categories for a Sample Area on the West Side of Lake Okeechobeee.

6 Soil Classification Database General Methods

Level 1: 100

In these areas, the SHWT has a depth ranging from 2 to more than 6 ft. below the soil surface for most of the year. Flooding never occurs and the soils usually consist of deep sandy marine deposits mostly found in the highlands of Central Florida or along ancient coastal dunes or strands. For this reason, these sites are under heavy development pressure. Dominant vegetation can include pines, scrubby oaks, rosemary (Ceratiola ericoides), lichens, and cactus (Opuntia spp.). Fire plays a crucial role in determining the dominant vegetative components of these communities. The ecological communities (SCS, 1989) included in this category are the Sand Scrub and the Longleaf Pine-Turkey Oak Hills. Please refer to Appendix D for a detailed description of the Sand Scrub Ecological Community.

Level 1: 200

This category contains beaches, which have a saltwater table that ranges from 0 to 6 ft. below the soil surface. Variation of the water table is usually daily due to tidal action, however much larger extremes can occur during storm events. These areas include sand and shell beaches along both the Atlantic and Gulf coasts and beach foredune communities that develop on the unconsolidated deposits. Typical animals include beach mice, gulls, terns, shorebirds, sea turtles, and crabs. Typical plants include sea oats (Uniola paniculata) and other grasses, railroad vine (Ipomoea pes-caprae), seagrape (Coccoloba uvifera), scrub oaks (Quercus spp.), and Spanish bayonet (Yucca aloeifolia). Usually, all species are salt tolerant and tall woody vegetation is wind sculpted due to exposure to sea spray.

Level 1: 300

This category contains areas that have a highly variable SHWT. These sites have a freshwater table that varies from 0 to 6 ft. below the soil surface, mostly due to frequent flooding conditions. Vegetation can also vary with these sites, depending on local conditions and duration of soil saturation over the past several years. Fire can play a crucial role in determining the dominant vegetative components of these communities.

Level 1: 400

This category contains sites that have a SHWT that ranges from 1.0 to 4.0 ft. below the soil surface. Some of these areas may rarely flood. Plant communites found on these sites can vary, depending on the duration of the SHWT relative to the soil surface. Drier sites may support some xeric vegetation or scrubby flatwoods. Wetter sites may support pine flatwoods, dry prairies, or low hammocks. Fire plays a crucial role in determining the dominant vegetative components of these communities.

7 General Methods Soil Classification Database

Level 1: 500

This category contains sites that have a SHWT that ranges from 0.5 to 1.5 ft. below the soil surface. Flooding may occur frequently or occasionally in wetter years. These sites are most often dominated by pine or palm flatwoods, dry prairies, or low hammocks. Generally, flatwoods are characterized by a relatively open overstory of pines, an extensive low shrub stratum, and a variable herbaceous layer. Each of these components show xerophytic and pyrophytic physiognomy (Harper, 1914; Gunter, 1921; Laessle, 1942; Edmisten, 1963; Abrahamson and Hartnett, 1990). Pine canopy density can vary widely, from dense to very widely scattered. Slash pine is the dominant overstory flatwoods species in South Florida. The ecological communities (SCS, 1989) included in this category are South Florida Flatwoods, Everglades Flatwoods, and Cabbage Palm Flatwoods. For a detailed description of the South Florida Flatwoods Ecological Community, please see Appendix D.

Level 1: 600

This category contains sites that have a SHWT-High range at the soil surface. Flooding may frequently occur. These sites are mostly dominated by hydrophytic vegetation, either halophytic or halophobic. Mangrove swamps and salt marshes are found in saltwater areas of low to zero wave energy, such as along the coastline of the southern peninsula (e.g., the Ten Thousand Islands, Whitewater Bay, Florida Bay, and southern Biscayne Bay). Red mangrove (Rhizophora mangle), black mangrove (Avicennia germinans), and white mangrove (Laguncularia racemosa) are important tree species of the mangrove swamps. Tidal flat communities (e.g., oyster bars, seagrass beds) can be found along shallow tidal creeks, lagoons, or along the Intracoastal Waterway. Intra-tidal wetlands provide valuable habitat for a wide range of invertebrates, fishes, amphibians, reptiles, birds, and mammals (Odum and McIvor, 1990). A review of the literature by Odum et al. (1982) reported some 220 species of fish, 24 species of reptiles and amphibians, 18 species of mammals, and 181 species of birds depend on mangrove habitat. Please refer to Appendix D for more a detailed description of the Salt Marsh Ecological Community.

Freshwater marshes are nonforested wetlands of open expanses of grasses, sedges, and/or rushes. Wet prairies are the least flooded of any Florida marsh type (Kushlan, 1990). Species composition varies as a function of hydroperiod, soil type, fire frequency, and site history. Because of the shorter hydroperiods, wet prairies are species-rich and include a variety of grasses, sedges, and flowering forbes. Wetter sites may contain sawgrass and saw palmetto (Serenoa repens) and may invade drier sites. Ecological communities in this category are the Cutthroat Seeps and Sloughs (wet prairies). More detailed descriptions of the Sawgrass and Sloughs (wet prairie) Ecological Community can be found in Appendix D.

8 Soil Classification Database General Methods

Level 1: 700

This category contains sites that have a SHWT-High range above soil surface. These sites support wetland vegetation. Freshwater marshes and ponds are nonforested wetlands of open expanses of grasses, sedges, and/or rushes. Occasional open-water areas may be present, often inhabited by water lily (Nymphaea odorata), spadderdock (Nuphar luteum), bladderworts (Utricularia spp.), or stoneworts (Chara spp.). A number of marsh types are recognized, each based upon the dominant species. These include arrowhead (Sagittaria spp.) marshes, sawgrass (Cladium jamaicense) marshes, fire flag (Thalia geniculata) marshes, bulrush (Scirpus spp.) marshes, spike-rush (Eleocharis spp.) marshes, cattail (Typha spp.) marshes, and maidencane (Panicum hemitomon) marshes. More detailed descriptions of the Sawgrass Ecological Community and the Freshwater Marsh Ecological Community can be found in Appendix D.

Level 1: 800

Water areas are sites that are inundated by 2 ft. of water or more throughout the year. These sites usually support aquatic vegetation. A variety of aquatic communities can be found in open water bodies, each of which is a function of the history and characteristics of the site. For instance, borrow pits may have sparse plant or animal communities if they are remote from wetlands or other water bodies. Stagnant freshwater lakes or those that have somewhat elevated nutrient levels (e.g., from agricultural or urban runoff) may contain floating plants (e.g., Eichhornia crassipes, Pistia stratiotes), filamentous green algae (e.g., Spirogyra spp.), scuds (Hyalella azteca), seed shrimp (Ostracods), and water fleas (Daphnia spp.). Freshwater lakes with high water quality can host a variety of plants and animals, such as bladderworts (Utricularia spp.), calcareous algae mats, freshwater sponges (e.g., Spongilla lacustris), pupfish (Jordanella floridae), livebearers (e.g., Gambusia affinis, Heterandria formosa), and sunfish (e.g., Lepomis spp.).

Level 1: 900

No data is available for these sites because of resource limitations or inaccessiblity. Some private land owners denied soil survey staff access to thier property. Public lands were not mappped unless the managing agency was willing to fund.

CLASSIFICATION BY ECOLOGICAL COMMUNITY TYPE

This classification is base upon the ecological communities (defined by the NRCS) associated with map unit components in the SSURGO database. During the soil survey mapping process a soil series was taxonomically defined and a number of attributes were assigned to it, such as range of pH values, hydrological group, and ecological community present. The ecological community presented in the FOTG database for a given soil map unit component is that which was present when and where the map unit was defined. However, if a map unit component was defined in a coastal area in the mid-1970’s, it is

9 General Methods Soil Classification Database quite possible that the ecological community present today is different because of hydrological changes, nonnative vegetation invasions, or fire suppression. Furthermore, occurrences of that map unit much farther inland may have a different ecological community, especially where there is a climatic gradient. This is often the case in central- south Florida were tropical vegetation tends to be restricted to coastal areas.

Because of these difficulties, accurately assigning specific ecological communities to a soil map unit component that is regionally distributed can lead to considerable imprecision. For this reason, this generalized classification was derived to offer the soils database user a more accurate definition of what biological community types can be expected on a given soil. Biological communities are grouped into categories based on similarities of characteristics, such as saltwater wetlands, freshwater wetlands, flatwoods, uplands, etc. One category is included for mapping units that have no ecological data available. Table 2 shows the different categories and a description of each used in this classification. A map created from these ecological community categories (ECC) is shown in Figure 3. Appendix B contains the full description of the categories and specific ecological communities included within them.

Table 2. Ecological Community Category Definitions.

Category Number Category Name Category Description

1 Water Aquatic communities, usually inundated to a depth of 2 ft. or more

2 Intra-tidal Wetlands Coastal wetland communities; low wave energy coast line

3 Beaches Beach communities; high wave energy coastlines

4 Freshwater Wetlands Freshwater marshes and swamps

5 Swamp Hammock Forested mesic communities, usually transitional

6 Wet Prairie Short-period wetlands. Generally treeless and grass-dominated

7 Flatwoods Usually pine and/or palm-dominated flatwood communities

8 Uplands Upland forested communities that seldom flood

9 Highlands Scrub and xeric communities, usually pine and oak dominated

10 N/A No data available

ECC #1 Water

The water category denotes areas that were described as open water bodies in the county soil surveys. These sites are permanently inundated, usually to a depth of two feet or greater. This includes freshwater, saltwater, natural, and excavated sites. However, a variety of aquatic communities can be found in open water bodies, each of which is a function of the history and characteristics of the site. For instance, borrow pits may have sparse plant or animal communities if they are remote from wetlands or other water bodies. Stagnant freshwater lakes or those that have somewhat elevated nutrient levels (e.g., from agricultural or urban runoff) may contain floating plants (e.g., Eichhornia crassipes, Pistia stratiotes), filamentous green algae (e.g., Spirogyra spp.), scuds

10 Soil Classification Database General Methods

Figure 3. Map of the Ecological Community Categories for a Sample Area on the West Side of Lake Okeechobeee (beaches, intra-tidal wetlands, and swamp hammocks are omitted from this map, as they are not found in this area).

11 General Methods Soil Classification Database

(Hyalella azteca), seed shrimp (Ostracods), and water fleas (Daphnia spp.). Freshwater lakes with high water quality can host a variety of plants and animals, such as bladderworts (Utricularia spp.), calcareous algae mats, freshwater sponges (e.g., Spongilla lacustris), pupfish (Jordanella floridae), livebearers (e.g., Gambusia affinis, Heterandria formosa), and sunfish (e.g., Lepomis spp.).

ECC #2 Intra-Tidal Wetlands

Intra-tidal wetlands are saltwater marshes and swamps that are subject to regular tidal flooding. Mangrove swamps and salt marshes are found in areas of low to zero wave energy, such as along the coastline of the southern peninsula (e.g., the Ten Thousand Islands, Whitewater Bay, Florida Bay, and southern Biscayne Bay). Red mangrove (Rhizophora mangle), black mangrove (Avicennia germinans), and white mangrove (Laguncularia racemosa) are important tree species of the mangrove swamps. Tidal flat communities (e.g., oyster bars, seagrass beds) can be found along shallow tidal creeks, lagoons, or along the Intracoastal Waterway. Beach formation is negligible, allowing the substrate to be stabilized by vegetation. Halophytic species typically predominate. Intra- tidal wetlands provide valuable habitat for a wide range of invertebrates, fishes, amphibians, reptiles, birds, and mammals (Odum and McIvor, 1990). A review of the literature by Odum et al. (1982) reported some 220 species of fish, 24 species of reptiles and amphibians, 18 species of mammals, and 181 species of birds depend on mangrove habitat. Please refer to Appendix D for more a detailed description of the Salt Marsh Ecological Community.

Soils in these wetlands are usually Aquents (an Entisol) or Aquods (a Histosol), and are hydric. They are nearly level, very poorly to poorly drained soils of variable- textured mineral and organic materials subject to frequent tidal flooding. The water table, which is typically saltwater, can range from the soil surface to one foot above the surface throughout the year.

ECC #3 Beaches

Beach communities are found in areas where sand deposition or wave energy is high. Dunes are built up as vegetation increase the surface roughness, causing the wind to slow and to drop sand grains being moved across the beach (Barbour et al., 1987; Bagnold 1941). The highly variable, typically salt water table, can range from the soil surface to six feet below the surface. This includes sand and shell beaches along both the Atlantic and Gulf coasts and dune communities that develop on the unconsolidated deposits. Typical animals include beach mice, gulls, terns, shorebirds, sea turtles, and crabs. Plants include sea oats (Uniola paniculata) and other grasses, railroad vine (Ipomoea pes- caprae), seagrape (Coccoloba uvifera), scrub oaks (Quercus spp.), and Spanish bayonet (Yucca aloeifolia). Usually, all species are salt tolerant and tall woody vegetation is wind sculpted due to exposure to sea spray. As with intra-tidal wetlands, these communities play an important role in shoreline stabilization and preventing erosion of the coast during storms.

12 Soil Classification Database General Methods

ECC #4 Freshwater Wetlands

Freshwater wetlands can be either forested and nonforested. These can be roughly divided into three kinds: freshwater marshes, baldcypress swamps, and hardwood swamps. Freshwater wetlands can be found on a wide range of soils types and usually are inundated for at least a portion of the year. The SHWT can vary from two feet above to one foot below the soil surface for four or more months during the year. Occasional open- water areas may be present, often inhabited by water lily (Nymphaea odorata), spadderdock (Nuphar luteum), bladderworts (Utricularia spp.), or stoneworts (Chara spp.).

Marshes are treeless wetlands usually compose of sedges or other emergent plants. A number of marsh types are recognized, each based upon the dominant species. These include arrowhead (Sagittaria spp.) marshes, sawgrass (Cladium jamaicense) marshes, fire flag (Thalia geniculata) marshes, bulrush (Scirpus spp.) marshes, spike-rush (Eleocharis spp.) marshes, cattail (Typha spp.) marshes, and maidencane (Panicum hemitomon) marshes.

Cypress swamps inhabit the frequently flooded rock and marl soils of southern Florida, floodplains, seasonally flooded basins, and depressional areas. Typical species include bald cypress (Taxodium distichum), pond cypress (Taxodium distichum var. ascendens), willow (Salix caroliniana), wax myrtle (Myrica cerifera), red maple (Acer rubrum), dahoon (Ilex cassine), buttonbush (Cephalanthus occidentalis), sawgrass, and airplants (mostly Tillandsia spp.). Often these swamps are used as nesting sites for a number of birds and other wildlife. Included in this category are the Scrub Cypress Ecological Community and the Cypress Swamp Ecological Community. More detailed descriptions of both of these ecological communities can be found in Appendix D.

Hardwood swamps include all hardwood-dominated freshwater wetland forests. Bays, pop ash (Fraxinus caroliniana), red maple, cabbage palm (Sable palmetto), dahoon, and laurel oak (Quercus laurifolia) are usual components. Baldcypress and pond cypress may be present, but only occasionaly. The community can have an evergreen appearance since it can be dominated by laurel and water oaks, cabbage palm, and bays. Ferns and other shade tolerant herbaceous plants are common. These wetlands are important to a number of wildlife species. Owls, hawks, woodpeckers, ducks, and a variety of songbirds use these swamps as nesting and feeding sites. Black bear, raccoons, bobcat, deer, mink, and otter can also be found. These communities can be along rivers, streams, poorly defined drainage ways, depressions, and areas subject to constant seepage. The soils are very poorly drained and subject to high water tables.

ECC #5 Swamp Hammock

Swamp hammocks include forested mesic wetlands that are usually transitional areas. These seldom, if ever, are invaded by fires. Dominant overstory vegetation includes oaks, cabbage palms, occasional hardwoods (such as red maple), abundant ferns, and other herbaceous plants. These sites are occasionally flooded and have hydric soils.

13 General Methods Soil Classification Database

Although these wetlands have a shorter hydroperiod than hardwood swamps, they contain a number of species in common with them.

ECC #6 Wet Prairie

Wet prairies are the least flooded of any Florida marsh type (Kushlan, 1990). Species composition varies as a function of hydroperiod, soil type, fire frequency, and site history. Because of the shorter hydroperiods, wet prairies are species-rich and include a variety of grasses, sedges, and flowering forbes. Wetter sites may contain sawgrass and saw palmetto (Serenoa repens) will invade drier sites. The SHWT generally ranges from the soil surface to one foot below the surface for four to nine months of the year. Ecological communities in this category are the Cutthroat Seeps and Sloughs (wet prairies). Please see Appendix D for a detailed description of the Sloughs Ecological Community.

ECC #7 Flatwoods

Flatwoods are characterized by low, flat topography, and relatively poorly drained, acidic, sandy soil typically underlain by an spodic horizon. This is the most extensive type of terrestrial ecosystem in Florida. The SHWT is typically just below the soil surface, except during periods of flooding. The term flatwood includes several vegetationally distinct communities found on a variety of soil types (Laessle, 1942). Generally, flatwoods are characterized by a relatively open overstory of pines, an extensive low shrub stratum, and a variable herbaceous layer. Each of these components show xerophytic and pyrophytic physiognomy (Harper, 1914; Gunter, 1921; Laessle, 1942; Edmisten, 1963; Abrahamson and Hartnett, 1990). Pine canopy density can vary widely, from dense to very widely scattered. Slash pine is the typical dominant overstory flatwoods species in South Florida.

There are other biological community types that can result from pine flatwoods, depending on the conditions of the site. Over-burned flatwoods may lack pines altogether. These are referred to as “dry prairies” and are usually dominated by saw palmetto. Flatwoods that have had fire suppressed for many years will develop into a “low hammock”, dominated by oaks and palms. The ecological communities (NRCS, 1989) included in this category are South Florida Flatwoods, Everglades Flatwoods and Cabbage Palm Flatwoods. For a detailed description of the South Florida Flatwoods Ecological Community, please see Appendix D.

ECC #8 Uplands

The uplands category includes areas that flood as rarely as flatwoods do, but are too wet to support scrub vegetation. These communities support upland hardwood and tropical species (in the southern counties); a few pines may be present.

Uplands may be dominated by pines, hardwood forests, or grasslands, depending on local conditions. Frequent fires will result in pasture-like savanna, whereas fire

14 Soil Classification Database General Methods suppression will allow development of pine and oak forests. These sites seldom, if ever, flood and the water table is well below the surface most of the year.

Tropical hammocks generally appear as thick stands with a dense canopy cover. Soils may be thin with only a few inches of organic matter. Typical vegetation includes wild tamarind (Lysiloma latisiliqua), Jamaica dogwood (Piscidia piscipula), mastic (Masticodendron foetidissimum), poisonwood (Metopium toxiferum), strangler fig (Ficus aurea), wild coffees (Psychotria spp.), and marlberry (Ardisia escallionoides). Hammocks are good wildlife habitat for both resident and migratory birds. Many of the plant species produce fruit that are important food sources for wildlife. These habitats also provide cover for many mammals during periods of high water and resting sites for migratory birds.

ECC #9 Highlands

Highland communities are usually on elevated, well-drained sandy soils along the coast or in the interior highlands of Central Florida. Coastal Strand communities support a variety of tropical vegetation (South and Central Florida). Scrub communities support xeric species and are regarded as the most ancient biological communities found in Florida. They most often have a high number of endemic and endangered species. The SHWT is well below the soil surface and flooding rarely, if ever, occurs. For this reason, these sites are under heavy development pressure and are in a state of decline. Coastal Strand can be dominated by saw palmetto (Serenoa repens), sea grape (Coccoloba uvifera), and species originating from the Caribbean Basin. Dominant scrub vegetation includes pines, scrubby oaks, rosemary (Ceratiola ericoides), lichens, and cactus (Opuntia spp.). The ecological communities (see NRCS, 1989) included in this category are the Sand Scrub and the Longleaf Pine-Turkey Oak Hills. Please refer to Appendix D for a detailed description of the Sand Scrub Ecological Community.

ECC #10 No Data

This category includes map units that are urbanized, drained, or where no soil survey was conducted.

CLASSIFICATION BY NSLP TYPE

This classification is based on the landscape types found in South Florida, including flatwoods, Everglades, tidal areas, and urbanized areas. This classification includes consideration of the depth and duration of the SHWT, soil morphology, and the geographical location of the soil. This method of categorization of soils is referred to as the Natural Soils Landscape Position (NSLP) classification.

From the Soils Classification Database, we first selected all water body map units for water bodies, soils that are exposed to tidal flooding, and soils that have been disturbed (urbanized, excavated, or filled in). These were each assigned to separate categories.

15 General Methods Soil Classification Database

Another category for areas of which no soil survey was conducted (no data) was also created. The remaining map units from the database were then sorted by range and duration of the SHWT, soil morphology, and geographic location. The specifics for these classifications are outlined in Table 3. Most map units were found inside the range of values for the landscape position definitions. However a few units lie just outside of the category range of values but have characteristics associated with them that necessitated their inclusion into a group. A map was created from the NSLP classifications and is presented in the pullout at the end of this document (Figure 4).

Table 3. Sorting Criteria for Soils Data by NSLP Type.

NSLP Type General Sorting Criteria

#1 Water Areas designated as “Water” in SSURGO

#2 Tidal Soils Coastal soils that are subject to tidal influence, no freshwater table

Transitional area between saltwater and freshwater zone in the southern Everglades, #3 Marl & Rocky Soils freshwater table dominates, and hydric marl or rocky soils

#4 Everglades Peat Pure organic, hydric soils within the extent of the historic Everglades

#5 Muck Depressions Depressional hydric soils with an organic surface layer over sandy sediments

#6 Sand Depressions Depressional hydric soils composed of pure sands

#7 Flats Soils Nondepressional hydric soils composed of pure sands

Nonhydric soils of pure sandy sediments, SHWT 0.5 to 1.5 ft. below soil surface four #8 Flatwood Soils months annually

Nonhydric soils of pure sandy sediments, SHWT 1.5 to 6.0 ft. below soil surface less #9 Knolls than 7 months annually

Nonhydric soils of pure sandy sediments, SHWT 6 ft. or more below soils surface all #10 Central Ridge & Dunes year

#11 Urban or Made Lands Excavated or built lands, original soil morphology disturbed

#12 No Data No soil survey data available

NSLP #1 Water

The Water landscape position denotes areas that were described as open water bodies in the county soil surveys. Water areas are permanently inundated, usually to a depth of two feet or greater. This includes freshwater, saltwater, natural, and excavated sites. There are no soils data that are associated with the Water landscape position

A variety of aquatic communities can be found on this landscape position, each of which is a function of the history and characteristics of the site. For instance, borrow pits may have sparse plant or animal communities if they are remote from wetlands or other water bodies. Stagnant freshwater lakes or those that have somewhat elevated nutrient levels (e.g., from agricultural or urban runoff) may contain floating plants (e.g., Eichhornia crassipes, Pistia stratiotes), filamentous green algae (e.g., Spirogyra spp.), scuds (Hyalella azteca), seed shrimp (Ostracods), and water fleas (Daphnia spp.). Freshwater lakes with high water quality can host a variety of plants and animals, such as

16 Soil Classification Database General Methods bladderworts (Utricularia spp.), calcareous algae mats, freshwater sponges (e.g., Spongilla lacustris), pupfish (Jordanella floridae), livebearers (e.g., Gambusia affinis, Heterandria formosa), and sunfish (e.g., Lepomis spp.).

NSLP #2 Tidal Soils

Tidal soils are found along coastal areas in salt marshes, mangrove or tidal swamps, and areas adjacent to the Intracoastal Waterway that have tidal flooding influence. These soils are usually Aquents (an Entisol) or Aquods (a Histosol), and are hydric. These soils can be nearly level to sloping sandy beaches, or very poorly drained coastal marshes and swamps consisting of variable-textured mineral and organic materials, subject to frequent tidal flooding. The water table, which is typically saltwater, can range from one foot below to one foot above the soil surface throughout the year. Examples of these soils include Wulfert, Durbin, and Peckish.

This landscape position includes beaches that can have a hydrological range that is a much wider range than the category for the SHWT. Perrine Variant soils (silt loam and fine sandy loam) of Broward and Indian River counties are currently an exception to the rest of the soils in this category. These soils are found in low flats that may have an intermittent freshwater SHWT, lie adjacent to tidal areas along estuaries, support halophytic vegetation, and may occasionally be inundated by salt water during exceptionally high tides. Please refer to Appendix C for a detailed description of the range of values for map units in this category.

A number of diverse biological communities may be found on this landscape position, the type of which is mostly a function of the wave energy exposure of the site. Mangrove swamps and salt marshes can be found in areas of low to zero wave energy, such as along the coastline of the southern peninsula (e.g., the Ten Thousand Islands, Whitewater Bay, Florida Bay, and southern Biscayne Bay). Tidal flat communities (e.g., oyster bars, seagrass beds) can be found along shallow tidal creeks, lagoons, or along the Intracoastal Waterway. In areas where sand deposition or wave energy is high, beach or littoral communities tenaciously colonize the unstable substrate or rocky shoreline. Please refer to Appendix D for a more detailed description of the Salt Marsh, which is a common ecological community found on this landscape position.

NSLP #3 Marl & Rocky Soils

Marl and rocky soils occur in Miami-Dade, Monroe, and Collier counties along the southern extent of the Everglades. The Marl & Rocky Soils landscape denotes that area near the southern tip of the Florida peninsula adjacent to the tidal area of Florida Bay. Marl soils (mostly Aquents, an Entisol) are hydric and originate from the precipitation of calcite in the water by calcareous algae mats. Rocky soils have exposed limestone at or near the surface. These areas are poorly to very poorly drained. The seasonal high water table ranges from one foot below to one foot above the soil surface for four to seven months annually. Examples of these soil series include Biscayne, Perrine, and Rock Outcrops. Some areas are noted as drained phases which means that there has been

17 General Methods Soil Classification Database artificial drainage implemented, however the degree or effectiveness of the drainage is not expressed. Please refer to Appendix C for a detailed description of the range of values for map units in this category.

A number of biological communities may be found on this landscape position. Since this area includes the transition zone between saltwater and freshwater tables, but is dominated by the latter. Both salt and freshwater marsh vegetation can be found on this landscape position, sparse sawgrass marsh being a common type of the latter found in this area. Wet prairie (marl prairie) species composition varies greatly and depends on local conditions. These are often dominated by a variety of grasses, sedges, and flowering forbs. Muhly (Muhlenbergia spp.), maidencane (Panicum hemitomon), cordgrass (Spartina spp.), and beak rush (Rhynchospora spp.) are common dominant species (Kushlan, 1990). Other communities that may occur include tropical hammocks and scrub cypress. Scattered dwarf (scrub) cypresses are found on the thin, rocky soils along the southern extent of the Everglades. Please refer to Appendix D for a more detailed description of the Scrub Cypress ecological community.

NSLP #4 Everglades Peat

Everglades peat soils are very poorly drained organic hydric soils, usually derived from sawgrass (Cladium jamaicense), that have formed over the limestone bedrock. These soils are normally found within the geographic extent of the historic Everglades Basin. Examples of these soil series include Pahokee, Terra Ceia, and Lauderhill. Typically, these are pure organic soils with no significant sand layer deposit between the organic layer and the limestone bedrock. This category contains Histosols, which are morphologically distinguished from Muck Depressions (NSLP #5) and Sand Depressions (NSLP #6) although they may have similar hydrological conditions. The seasonal high water table can range from the soil surface to two feet above the surface for nine to eleven months annually. Please refer to Appendix C for a detailed description of the range of values for map units in this category.

The principle biological communities that may be found on this landscape position include dense sawgrass marsh and freshwater marsh. Please refer to Appendix D for a more detailed description of the Sawgrass Marsh ecological community.

NSLP #5 Muck Depression

Muck depression soils are very poorly drained hydric soils that have an organic surface layer underlain by sandy marine sediments. A few areas may have a thin organic surface layer only a few inches thick. This category includes the transitional area between the Everglades pure organic soils (NSLP #4) and the coastal sandy marine sediments. Often, Muck Depressions (NSLP #5) lie adjacent to Flats (NSLP #7) and Flatwood (NSLP #8) landscapes. The seasonal high water table typically ranges from one-half foot below to two feet above the soil surface for seven to eleven months annually. Examples of these soils include Hontoon, Kaliga, and Samsula. Also included within this unit are frequently flooded alluvial areas that have a muck surface for the majority of the area. These

18 Soil Classification Database General Methods frequently flooded map units may have a shorter SHWT duration, but are subject to frequent flooding during the wet season. Frequently flooded map units are known to have surface flooding at least one out of every two years. Please refer to Appendix C for a detailed description of the range of values for map units in this category.

Several biological communities may be found on this landscape position, including freshwater marsh, sawgrass marsh, bay heads, hardwood swamps, and cypress swamps. Local conditions favor one community over the other, with fire frequency and site hydrology playing large roles in their distribution. Please refer to Appendix D for more a detailed description of the Cypress Swamp ecological community.

NSLP #6 Sand Depression

The Sand Depression landscape position denotes all areas that have sandy marine sediments throughout the profile. A few areas may have mucky sand, loamy sand, or sandy loam surfaces with sandy or loamy subsurfaces. All of these soils are hydric. Often, these areas are depressions adjacent to Flats (NSLP #7) and Flatwood (NSLP #8) landscapes. These soils are very poorly drained and the seasonal high water table can typically range from one foot below to two feet above the soil surface for seven to ten months annually. Examples of these soil series include Basinger, Boca, and Riviera. Also included within this unit are frequently flooded alluvial soils that have a sandy surface for the majority of the area. These frequently flooded map units have a shorter duration for the SHWT, but are subject to frequent flooding during the wet season. Frequently flooded map units are known to have surface flooding at least one out of every two years. Please refer to Appendix C for a detailed description of the range of values for map units in this category.

Several biological communities that may be found on this landscape position, including freshwater marsh, sawgrass marsh, hardwood swamps, wetland hardwood hammocks, and cypress swamp. Local conditions favor one community over the other with fire frequency and site hydrology playing large roles in their distribution. Generally, sites that burn less frequently tend to support swamp forests, whereas more frequently burned sites tend to support marsh vegetation. Please refer to Appendix D for a detailed description of Freshwater Marsh and Ponds ecological communities.

NSLP #7 Flats Soils

Flats (referred to as “sloughs” by the NRCS) soils are poorly drained hydric soils with sandy marine sediments throughout the profile, or more rarely with loamy sand or sandy loam. Flats are located between the Flatwood (NSLP #8) and depressional landscapes (NSLP #5 or #6), and are generally regarded as transitional areas. The seasonal high water table can typically range from the soil surface to one foot below the surface for four to nine months annually. Examples of these soil series include Basinger, Malabar, and Riviera. Also included within this unit are occasionally flooded alluvial areas that have a sandy surface for the majority of the area. These areas may have a slightly shorter SHWT duration, but may be flooded for less than a few weeks by large

19 General Methods Soil Classification Database storm events. Please refer to Appendix C for a detailed description of the range of values for map units in this category.

Biological communities associated with this landscape position include cabbage palm flatwoods and hammocks, Everglades flatwoods, cutthroat seeps, wetland hardwood hammocks, scrub cypress, freshwater marsh, and wet-prairies. Local conditions favor one community over the other with fire frequency, soil thickness, and site hydrology playing large roles in controlling the dominant vegetation type. The fire dependant cutthroat grass (Panicum abscissum), an endemic, is restricted to seepage slopes and swales of south central Florida (Abrahamson and Hartnett, 1990). Dwarf (scrub) cypress forests are found on thin, rocky soils such as those along the southern peninsula. Generally, seldom burned sites tend to develop swamp forests, whereas frequently burned sites tend to support marsh or wet prairie vegetation. Please refer to Appendix D for a detailed description of Slough (wet prairie) ecological communities.

NSLP #8 Flatwood Soils

Flatwood soils are poorly drained nonhydric, upland soils with sandy marine sediments throughout the profile, some of which may have loamy sand substrates. Most of the soils in this category are Spodosols, (i.e., they have a subsurface spodic horizon). The seasonal high water table can range from one-half to one and one-half feet below the soil surface for four months annually. Examples of these soil series include Immokalee, Myakka, and Smyrna. Some areas may become inundated for less than a couple weeks during large storm events. Please refer to Appendix C for a detailed description of the range of values for map units in this category.

Biological communities associated with this landscape position include dry prairies, flatwoods (pine and cabbage palm), and low hammocks (i.e., hardwood, cabbage palm, and oak). Fire plays a key role in the development of one community type over another. Fire excluded sites tend to develop low hammocks, whereas frequently burned sites tend to develop flatwoods. Over-burned sites tend to become dry prairies, which are treeless (or nearly so) expanses dominated by grasses (e.g., Aristida spp., Andropogon spp.), saw palmetto (Serenoa repens), and low shrubs (e.g., wax myrtle, fetterbrush, gallberry, and shining blueberry) (Abrahamson and Hartnett, 1990). Please refer to Appendix D for a more detailed description of South Florida Flatwoods ecological community.

NSLP #9 Knolls

Knolls soils are nonhydric, moderately well to somewhat poorly drained upland soils with sandy marine sediments throughout the profile. These soils are Psamments (an Entisol), which typically have no unique diagnostic horizons throughout the soil profile. The seasonal high water table can range from one and one-half feet to six feet below the soil surface for four to seven months annually. Examples of these soils include Krome, Tavares, and Zolfo. Please refer to Appendix C for a detailed description of the range of values for map units in this category.

20 Soil Classification Database General Methods

Biological communities associated with this landscape position include sand pine scrub, pine flatwoods, South Florida coastal strand, oak hammocks, tropical hammocks, and upland hammocks. Fire plays a key role in the development of one community over another. Fire-excluded sites develop hammocks, whereas frequently burned sites will support pine scrub or flatwoods. Tropical hammocks tend to be found along the coastal areas or along the extreme southern peninsula. Sand pine scrub (dominated by Pinus clausa), pine flatwoods (dominated by Pinus elliottii) and scrubby flatwoods (a community intermediate between the two) are fire-dependant forests that inhabit the dry soils of the coastal ridge and interior highlands north of Lake Okeechobee. Please refer to Appendix D for a more detailed description of the Sand Pine Scrub ecological community.

NSLP #10 Central Ridge & Dunes

Central Ridge & Dune landscapes are excessively drained, nonhydric, Psamments (an Entisol of drier upland soils) with sandy marine sediment throughout the profile. The seasonal high water table is more than six feet below the soil surface throughout the year. Common soils of this landscape position include Astatula, Candler, and Neilhurst. Please refer to Appendix C for a detailed description of the range of values for map units in this category.

Ecological communities that may be found on this landscape include sand pine scrub, scrubby flatwoods, South Florida coastal strand, and upland hardwood hammock. Fire plays an important role in the maintenance of sand pine scrub and scrubby flatwood habitats; these habitats will convert to hammock if burning is suppressed. Coastal strand is found primarily along the barrier islands of the Atlantic coast. Please refer to Appendix D for a more detailed description of the South Florida Coastal Strand ecological community.

NSLP #11 Urban or Made Lands

Urban or made land areas have been altered, excavated, or disturbed and no longer have their natural morphological soil features. These soils no longer function as they did in their original state, so there is little information available. The seasonal high water table varies by site and is usually controlled to inhibit flooding of developed areas. Common soils of this landscape position include Arents, Matlacha, Pits, Udorthents, and Urban Land.

NSLP #12 No Data

No data is available for these sites because of resource limitations or inaccessiblity. Some private land owners denied soil survey staff access to thier property. Public lands were not mappped unless the managing agency was willing to fund.

21 General Methods Soil Classification Database

22 Soil Classification Database Use of the Soil Classifications

USE OF THE SOIL CLASSIFICATIONS

The classification schemes outlined in this document do not represent the only or best categorizations of the soils data. Our purpose is to present several classifications that are most needed by users of the soils data. The methods outlined in this technical publication do not improve the original county soil survey data quality, rather serves only to aid in its use. Other fields that may be categorized in the soils data base include: hydrological group, drainage class, depth to the bedrock, hydric soils, leaching potential, and runoff potential. It is then possible to generate a GIS map layer for that attribute. For example, a map of hydric soils or a map of soil drainage classes may be useful to hydrological modelers. It is recognized that different disciplines and different projects will have unique needs, and our purpose is to make the soils data more easily used by these groups.

Users of soil map data must also realize that even at the scales and levels of detail of the SSURGO maps, the map unit data are generalized to some degree. In reality, soils are highly variable across the landscape. Mapping efforts are limited by scale, time, monetary, and other limitations that can cause considerable imprecision in most soil maps (Brown et al., 1990). The landscape and soils are even more complex than depicted in the SSURGO maps.

Soil morphology reflects the complex interaction among topography, climate, time, vegetation, hydrology, and parent material. The morphological characteristics of soils are influenced by the hydrological conditions under which they formed, especially in South Florida where very small changes in topography can greatly affect hydrologic response. This fact is useful in interpreting map layers developed from the Soils Classification Database. Because soil morphology data yields information about the historic conditions of a site, it can be useful in interpreting the landscape before changes from development. By definition, hydric soils were formed in wetlands. The extent of hydric soils is also the historic extent of wetlands. This can have important implications for the management and restoration of wetlands, as well as in understanding the landscape in which they are situated. This can aid in understanding historical hydrological flow paths, runoff, and conditions, as well as predicting impacts to landscape-level features by encroaching development.

Some of our classifications generally define a hydrological gradient from lower, wetter landscapes (e.g., Water) to higher landscapes (Knolls, Central Ridge & Dunes). In undisturbed (e.g., nonurban, nonagricultural) areas, these classifications and the associated map layers are useful for understanding natural relationships between adjacent landscapes (relative topography), as well as regional patterns of hydrological and topographical gradients.

County soil surveys were conducted during different years and as a result, some contain more current data than others. In some coastal counties that have older surveys, the area of drained soils or urban lands are most likely under represented. Some soils that

23 Use of the Soil Classifications Soil Classification Database are present in the database were converted to agriculture or urban areas after the soils survey was taken. Some large-scale hydrological alterations (e.g., canals and levees) may have permanently changed the natural drainage patterns of an area. When using data from counties that have older data, a more recent source of information should be sought for verification. Table 4 shows the year that soil surveys were published.

Table 4. Dates of Publication of County Soil Surveys by NRCS.

County Soil Survey Date(s) of Publication

Broward County (East) 1984

Charlotte County 1984

Collier County 1998

Miami-Dade County 1996

Glades County 1999

Hendry County 1990

Highlands County 1990

Indian River County 1987

Lee County 1984

Martin County 1981

Monroe County 1995

Okeechobee County (update) 1999

Orange County 1989

Osceola County 1979

Palm Beach County 1978

Polk County 1990

St. Lucie County 1980

Desoto County 1989

Hardee County 1984

As a result of substantial changes to local hydrology some peat soils are declining, necessitating a change in the classification of these soils (Collins et al., 1986; Griffin et al., 1982; Stephens et al., 1984; Snyder et al., 1978). It is recommended that organic soils within drained areas be verified before using data from the site.

Efforts will be made by the NRCS to keep this database updated, however its strength is in landscape-level application. It is recommended that when applying these data to a discrete location that a site-specific observation is used to confirm the map data. This data is intended to assist in analyzing the characteristics of soils, but can never replace site-specific observations when that level of resolution is required.

24 Soil Classification Database Summary

SUMMARY

The Soil Classification Database is a compilation and generalization of soil databases that is suitable for categorizing soils of similar characteristics. County soil surveys published by the Natural Resource Conservation Service (NRCS, formerly the Soil Conservation Service) are often difficult to use because of the format, size, and complexity of the data. The Soil Classification Database allows the soils data to be presented in a more user-friendly format.

The Soil Classification Database was derived from the Soil Survey Geographical Database (SSURGO) Component (COMP) table. The first (largest) soil components for each map unit and the most-used data fields were retained, then combined with several useful data fields from the Field Office Technical Guide (published by the Florida NRCS). Data were checked for accuracy and updated where necessary. The result was an updated single soils database that can be used to group soils into understandable categories of similar characteristics, such as the NSLP component.

The Soil Classification Database includes all counties within and several adjacent to the boundaries of the South Florida Water Management District (SFWMD) and is current to 1999 NRCS data standards and definitions. This project is a joint effort between the Comprehensive Conservation, Permitting, and Mitigation Strategy (Wetland Conservation Strategy) and the NRCS. Funding was provided as part of the USEPA’s grant to the SFWMD for the Wetland Conservation Strategy.

25 Summary Soil Classification Database

26 Soil Classification Database References

REFERENCES

Abrahamson, W.G. and D.C. Hartnett. 1990. Pine flatwoods and dry prairies. In: R.L. Myers and J.J. Ewel , eds. Ecosystems of Florida. pp. 103 - 149. Bagnold, R.A. 1941. The Physics of Blown Sand and Desert Dunes. Methuen, London. Barbour, M.G., M. Rejmanek, A.F. Johnson, and B.M. Pavlik. 1987. Beach vegetation and plant distribution patterns along the northern Gulf of Mexico. Phytocoenologia, vol. 15, no. 2, pp. 201-233. Brown, R.B., E.L. Stone, and V.W. Carlisle. 1990. Soils. In: R.L. Myers and J.J. Ewel , eds. Ecosystems of Florida. pp. 46. Cohen, A.D., and W. Spackman. 1984. The petrology of peats from the Everglades and coastal swamps of southern Florida. In: P.J. Gleason, ed. Environments of South Florida: Present and Past II. Miami Geological Society, Coral Gables, FL., pp. 352- 374. Collins, M.E., G.W. Schellentrager, J.A. Doolittle, and S.F. Shih. 1986. Using ground- penetrating radar to study changes in soil map unit composition in selected Histosols. Soil Sci. Soc. Am. J. 50:408-412. Davis, J. H., Jr. 1946. The peat deposits of Florida: their occurrence, development, and uses. Fla. Geol. Surv. Bull. No. 30. Edmisten, J.E. 1963. The Ecology of the Florida Pine Flatwoods. Ph.D. Thesis, Univ. of Florida, Gainesville, FL. Gleason, P.J. and P. Stone. 1994. Age, origin, and landscape evolution of the Everglades peatlands. In: S.M. Davis and J.C. Ogden, eds. Everglades, the Ecosystem and Its Restoration. St. Lucie Press, Delray Beach, FL., pp. 149-198. Griffin, G.M., C.C. Wieland, L.Q. Hood, R.W. Good, III, R.K. Sawyer, and D.F. McNeill. 1982. Assessment of the peat resources of Florida, with a detailed survey of the northern Everglades. Dept. Geology, University of Florida, for U.S. Dept. of Energy under Grant # DE-FGT18-81FCO5114. State of Florida, Governor’s Energy Off., Tallahassee, FL. Gunter, H. 1921. Fla. Geol. Survey Report. 13: 207-209.

Harper, R.M. 1914. Geography and Vegetation of Northern Florida. Fla. Geol. Surv., 6th Annual Report, pp. 163-451. Kushlan, J.A. 1990. Marshes. In: R.L. Myers and J.J. Ewel , eds. Ecosystems of Florida. pp. 324 - 363. Laessle, A.M. 1942. The Plant Communities of the Welaka Area with Special Reference to Correlation between Soils and Vegetational Succession. Biol. Sci. Ser. 4, Univ. of Florida Pub., Gainesville, FL.

27 References Soil Classification Database

Odum, W. E. and C.C. McIvor. 1990. Mangroves. In: R.L. Myers and J.J. Ewel , eds. Ecosystems of Florida. pp. 517 - 548. Odum, W. E., C.C. McIvor, and T.J. Smith, III. 1982. The Ecology of the Mangroves of South Florida: A Community Profile. U.S. Fish and Wildlife Service Off. of Biol. Serv., Technical Report FWS/OBS 81-24. Natural Resources Conservation Service. 1995. Soil Survey Geographic (SSURGO) Data Base. Miscellaneous Publication. no. 1527. Natural Resources Conservation Service. 1998. Soil Survey of Collier County, Florida. National Technical Committee for Hydric Soils. 1994. Federal Register. vol. 59. no. 113. 35680-35695. Soil Conservation Service. 1989. The 26 Ecological Communities of Florida. July 1989 revision reprinted by the Florida Chapter of the Soil and Water Conservation Society, P.O. Box 2025, Gainesville, Florida, 32602. Soil Conservation Service. 1992. Field Office Technical Guide. Natural Resources Conservation Service, Gainesville, FL. South Florida Water Management District, 1994. SFWMD Land Use and Land Cover. SFWMD, RFP C-6796. Stephens, J.C. 1984. Subsidence of organic soils in the Florida Everglades- a review and update. In: P.J. Gleason, ed., Environments of South Florida: Past and Present II. Miami Geological Society, Coral Gables, FL., pp. 375-384. Snyder, G.H., H.W. Burdine, J.R. Crockett, G.J. Gascho, D.S. Harrison, G. Kidder, J.W. Mishoe, D.L. Myhre, F.M. Pate, and S.F. Shih. 1978. Water table management for organic soil conservation and crop production in the Florida Everglades. Fla. Agric. Exp. Stn. Inst. Food Agric. Sci. Bull. No. 801.

28 Soil Classification Database Glossary

GLOSSARY AND LIST OF ABBREVIATIONS

Component The individual soil types that sidered ponding. Frequency, duration, and make up a map unit. probable dates are estimated. Frequency generally is expressed as none or frequent. Duration The length of time that the None means that flooding is not probable. SHWT expresses itself. The duration of Frequent means that flooding occurs under the SHWT is not a definite time span, normal weather conditions (more than a 50 rather it is a range typical for the map unit percent chance of flooding in any year). or category. This range is shorter in drier Duration is expressed as long (7 days to 1 years and longer in unusually wet years. month), and very long (more than one Also, the beginning and ending of the month), The time of year that floods are SHWT depends on the timing of rainfall most likely to occur is expressed in events for the season. Usually the rainy months. November-June, for example, season (which fuels the SHWT) begins in means that flooding can ocur during the May. However, in some years the rainy period November through June. About season can begin in April or June, depend- two-thirds to three-forths of all flooding ing on climatic factors. occurs during the stated period.

Ecological Community Categorization FOTG Field Office Technical Guide. (ECC) A classification of the SSURGO data presented in this document. GIS Geographic Information System.

Entisols A soil order that consists of Histosols A soil order that are predomi- poorly developed soils. In these soils, pro- nantly organic, consisting of peat or muck file development is either minor or lacking deposits of varying thickness over sand, altogether. Diagnostic characteristics marl, limestone, or other material. The found in other soil orders are not found, organic soil has accumulated in an such as an organic, spodic, or argillic hori- extremely wet environment and can vary in zon. The most common Entisols found in consistency from fibrous to slimy (Davis, South Florida are the Aquents (formed in 1946; Brown et al., 1990). Different types wet environments) and the Psamments of peat have been classified based on the (found in naturally drier environments). parent plant material from which they are Aquents are the dominant Entisols in South derived, the texture, composition, and state Florida, are found along the Rocky Glades of decay (Davis, 1946; Cohen and Spack- area. Psamments are found along the Cen- man, 1984). Peat deposits in South Florida tral Ridge and along the ancient dune line are fairly recent, the oldest in the historic on the Coast. Everglades being approximately 5,000 years old (Gleason and Stone, 1994). It is Flooding The temporary covering of the important to note that when drained, peat is soil surface by flowing water caused by subject to subsidence, shrinking, and overflowing streams, by runoff from adja- decomposition). Some estimated rates cent slopes, or by inflow from high tides. place this on the order of 2.5 cm/yr. In Shallow water standing in swamps and some areas where drainage has been marshes or in a closed depression is con- effected, the extent of peat soils is declin-

29 Glossary Soil Classification Database ing, prompting a change in the classifica- unit of the United States Department of tion of these soils (Collins et al., 1986; Agriculture. Griffin et al., 1982; Stephens et al., 1984; Snyder et al., 1978). NSLP Natural Soils Landscape Positions, a classification of the SSURGO data pre- Map Unit The fundamental graphic fea- sented in this document. ture in the SSURGO database which links the graphic feature to the attribute data- SCS Soil Conservation Service (see base. Each map unit represents an area NRCS). dominated by one to three kinds of soil. However, there are no graphic deliniations Seasonal High Water Table (SHWT) for the locations of components within the The shallowest depth to free water that map unit. stands in an unlined borehole or where the soil moisture tension is zero for a signifi- Hydric Soils Soils that are saturated, cant period (more than a few weeks). The flooded, or ponded long enough during the depth to the SHWT is the most used/ growing season to develop anaerobic con- requested soil interpretation in Florida. ditions in the upper part (USDA, Soil Con- This method of estimating SHWT applies servation Service, 1987). This definition only to those areas lacking significant identifies soils that are either saturated or hydrological modifications. Hydrological inundated long enough during the growing modification such as ditches and dikes can season to support the growth and reproduc- make the soil either wetter or drier. The tion of hydrophytic vegetation. The con- depth to the SHWT is not a definite value, cept of hydric soil indicators is based on rather it is a range typical for the map unit the theory that soils develop diagnostic or category. This range may be larger morphological features associated with the anaerobic decomposition of organic mat- Spodosols A soil order that consists of ter and the reduction of iron and other min- soils that have a spodic horizon. The erals in their upper part. In other words, spodic, or Bh, horizon is a subsurface layer that when soils are wet enough for a long in which organic matter in combination enough duration to be considered hydric, with aluminum and/or iron has accumu- they should exhibit certain visible proper- lated due to down-ward leaching. The ties that are observable in the field. Wet- upper boundary of this layer is within 2m lands possess three essential of the soil surface and the soil textures are characteristics: (1) hydrophytic vegeta- generally sandy. Two types of spodosols tion, (2) hydric soils, and (3) wetland can be further defined, the Aquods (that hydrology. All manual criteria for each of are wet for extended periods in most years) the three characteristics must be met before and the Humods (that are not naturally wet an area can be identified as a wetland. for extended periods in most years). Therefore, the synonymy of hydric soils and wetlands is implied (National Techni- SFWMD South Florida Water Manage- cal Committee for Hydric Soils, 1994). ment District.

MUID Map unit identification number. SSURGO Soil Survey Geographical Data Base. NRCS Natural Resources Conservation Service (formally the Soil Conservation) A

30 Soil Classification Database Glossary

USDA United States Department of Agri- culture.

USEPA United States Environmental Pro- tection Agency.

31 Glossary Soil Classification Database

32 Soil Classification Database Appendix A

Appendix A SHWT CLASSIFICATION CODES

The classification codes for the SHWT ranges are shown in Table A-1. The values provided in SSURGO are the duration and range (high and low) for the SHWT in an average year. These values are for natural conditions at the time the county soil survey was undertaken. If drainage has been implemented, it is noted in the “other phase” or “OTHERPH” field in the Soils Classification Database. It is important to verify these data with currently available information before applying them since changes may have occurred since the soil survey was completed.

A-1 Appendix A Soil Classification Database

Table A-1. Category Codes and Associated Ranges for the SHWT Used in the Categorization of Duration. Category Codes and Associated Ranges for the SHWT

100 Deep SHWT (from 2.5 to more than 6 ft. below the soil surface).

110 SHWT more than 6.0 ft below the soil surface.

119 SHWT more than 6.0 ft below the soil surface all year.

120 SHWT 5.0 to 6.0 ft below the soil surface.

121 SHWT 5.0 to 6.0 ft below the soil surface for 4 months annually.

122 SHWT 5.0 to 6.0 ft below the soil surface for 5 months annually.

129 SHWT 5.0 to 6.0 ft below the soil surface for 12 months annually.

130 SHWT 4.0 to 6.0 ft below the soil surface.

132 SHWT 4.0 to 6.0 ft below the soil surface for 5 months annually.

134 SHWT 4.0 to 6.0 ft below the soil surface for 7 months annually.

140 SHWT 4.0 to 5.0 ft. below the soil surface.

143 SHWT 4.0 to 5.0 ft. below the soil surface 6 months annually.

144 SHWT 4.0 to 5.0 ft. below the soil surface 7 months annually.

150 SHWT 3.5 to 6.0 ft. below the soil surface.

153 SHWT 3.5 to 6.0 ft. below the soil surface 6 months annually.

154 SHWT 3.5 to 6.0 ft. below the soil surface 7 months annually.

160 SHWT 3.5 to 5.0 ft. below the soil surface.

162 SHWT 3.5 to 5.0 ft. below the soil surface 5 months annually.

163 SHWT 3.5 to 5.0 ft. below the soil surface 6 months annually.

164 SHWT 3.5 to 5.0 ft. below the soil surface 7 months annually.

170 SHWT 3.0 to 5.0 ft. below the soil surface.

172 SHWT 3.0 to 5.0 ft. below the soil surface 5 months annually.

173 SHWT 3.0 to 5.0 ft. below the soil surface 6 months annually.

180 SHWT 2.5 to 5.0 ft. below the soil surface.

181 SHWT 2.5 to 5.0 ft. below the soil surface 4 months annually.

182 SHWT 2.5 to 5.0 ft. below the soil surface 5 months annually.

183 SHWT 2.5 to 5.0 ft. below the soil surface 6 months annually.

190 SHWT 2.0 to 8.0 ft. below the soil surface.

193 SHWT 2.0 to 8.0 ft. below the soil surface 6 months annually.

200 Beaches (Salt water table from 0.0 to 6.0 ft. below the soil surface).

210 Salt water table from 0.0 to 6.0 ft. below the soil surface.

219 Salt water table from 0.0 to 6.0 ft. below the soil surface all year.

300 SHWT varies widely (from 0 to 6 ft. below the soil surface).

310 SHWT 0.0 to 6.0 ft. below the soil surface.

312 SHWT 0.0 to 6.0 ft. below the soil surface 5 months annually.

314 SHWT 0.0 to 6.0 ft. below the soil surface 7 months annually.

400 SHWT well below the soil surface (from 1.0 to 4.0 ft. below the soil surface).

410 SHWT 2.5 to 3.5 ft. below the soil surface.

A-2 Soil Classification Database Appendix A

Table A-1. (Continued) Category Codes and Associated Ranges for the SHWT Used in the Categorization of Duration. Category Codes and Associated Ranges for the SHWT

411 SHWT 2.5 to 3.5 ft. below the soil surface 4 months annually.

413 SHWT 2.5 to 3.5 ft. below the soil surface 6 months annually.

420 SHWT 2.0 to 4.0 ft. below the soil surface.

421 SHWT 2.0 to 4.0 ft. below the soil surface 4 months annually.

425 SHWT 2.0 to 4.0 ft. below the soil surface 8 months annually.

429 SHWT 2.0 to 4.0 ft. below the soil surface 12 months annually.

430 SHWT 2.0 to 3.5 ft. below the soil surface.

431 SHWT 2.0 to 3.5 ft. below the soil surface 4 months annually.

432 SHWT 2.0 to 3.5 ft. below the soil surface 5 months annually.

433 SHWT 2.0 to 3.5 ft. below the soil surface 6 months annually.

436 SHWT 2.0 to 3.5 ft. below the soil surface 9 months annually.

440 SHWT 2.0 to 3.0 ft. below the soil surface (includes 2.0 to 2.0).

441 2.0 to 3.0 ft. below the soil surface 4 months annually.

442 2.0 to 3.0 ft. below the soil surface 5 months annually.

443 2.0 to 3.0 ft. below the soil surface 6 months annually.

450 SHWT 1.5 to 3.5 ft. below the soil surface.

451 SHWT 1.5 to 3.5 ft. below the soil surface 4 months annually.

453 SHWT 1.5 to 3.5 ft. below the soil surface 6 months annually.

460 SHWT 1.5 to 3.0 ft. below the soil surface.

461 SHWT 1.5 to 3.0 ft. below the soil surface 4 months annually.

463 SHWT 1.5 to 3.0 ft. below the soil surface 6 months annually.

470 SHWT 1.5 to 2.5 ft. below the soil surface.

472 SHWT 1.5 to 2.5 ft. below the soil surface 5 months annually.

480 SHWT 1.0 to 3.5 ft. below the soil surface.

483 SHWT 1.0 to 3.5 ft. below the soil surface 6 months annually.

490 SHWT 1.0 to 3.0 ft. below the soil surface.

493 SHWT 1.0 to 3.0 ft. below the soil surface 6 months annually.

500 SHWT is shallow (from 0.5 to 1.5 ft. below the soil surface).

510 SHWT is 1.0 to 1.5 ft. below the soil surface.

511 SHWT is 1.0 to 1.5 ft. below the soil surface 4 months annually.

520 SHWT is 1.0 ft. below the soil surface.

529 SHWT is 1.0 ft. below the soil surface 12 months annually.

530 SHWT is 0.5 to 1.5 ft. below the soil surface.

530 SHWT is 0.5 to 1.5 ft. below the soil surface 3 months annually.

531 SHWT is 0.5 to 1.5 ft. below the soil surface 4 months annually.

532 SHWT is 0.5 to 1.5 ft. below the soil surface 5 months annually.

533 SHWT is 0.5 to 1.5 ft. below the soil surface 6 months annually.

536 SHWT is 0.5 to 1.5 ft. below the soil surface 9 months annually.

A-3 Appendix A Soil Classification Database

Table A-1. (Continued) Category Codes and Associated Ranges for the SHWT Used in the Categorization of Duration. Category Codes and Associated Ranges for the SHWT

540 SHWT is 0.5 to 1.0 ft. below the soil surface.

543 SHWT is 0.5 to 1.0 ft. below the soil surface 6 months annually.

600 High range for the SHWT is at the soil surface.

610 SHWT is 0.0 to 2.0 ft. below the soil surface.

619 SHWT is 0.0 to 2.0 ft. below the soil surface 12 months annually.

620 SHWT is 0.0 to 1.0 ft. below the soil surface.

620 SHWT is 0.0 to 1.0 ft. below the soil surface 3 months annually.

621 SHWT is 0.0 to 1.0 ft. below the soil surface 4 months annually.

622 SHWT is 0.0 to 1.0 ft. below the soil surface 5 months annually.

623 SHWT is 0.0 to 1.0 ft. below the soil surface 6 months annually.

624 SHWT is 0.0 to 1.0 ft. below the soil surface 7 months annually.

626 SHWT is 0.0 to 1.0 ft. below the soil surface 9 months annually.

629 SHWT is 0.0 to 1.0 ft. below the soil surface 12 months annually.

630 SHWT is 0.0 to 0.5 ft. below the soil surface.

631 SHWT is 0.0 to 0.5 ft. below the soil surface 4 months annually.

632 SHWT is 0.0 to 0.5 ft. below the soil surface 5 months annually.

633 SHWT is 0.0 to 0.5 ft. below the soil surface 6 months annually.

634 SHWT is 0.0 to 0.5 ft. below the soil surface 7 months annually.

638 SHWT is 0.0 to 0.5 ft. below the soil surface 11 months annually.

639 SHWT is 0.0 to 0.5 ft. below the soil surface 12 months annually.

640 SHWT is at the soil surface.

647 SHWT is at the soil surface 10 months annually.

700 High range for the SHWT is above soil surface.

710 SHWT is from 1 ft. above to 1 ft. below the soil surface.

711 SHWT is from 1 ft. above to 1 ft. below the soil surface 4 months annually.

712 SHWT is from 1 ft. above to 1 ft. below the soil surface 5 months annually.

713 SHWT is from 1 ft. above to 1 ft. below the soil surface 6 months annually.

714 SHWT is from 1 ft. above to 1 ft. below the soil surface 7 months annually.

716 SHWT is from 1 ft. above to 1 ft. below the soil surface 9 months annually.

719 SHWT is from 1 ft. above to 1 ft. below the soil surface 12 months annually.

720 SHWT is from the soil surface to 1 ft. above the surface.

722 SHWT is from the soil surface to 1 ft. above the surface 5 months annually.

725 SHWT is from the soil surface to 1 ft. above the surface 8 months annually.

726 SHWT is from the soil surface to 1 ft. above the surface 9 months annually.

728 SHWT is from the soil surface to 1 ft. above the surface 11 months annually.

730 SHWT is from 2 ft. above to 1ft. below the soil surface.

731 SHWT is from 2 ft. above to 1ft. below the soil surface 4 months annually.

732 SHWT is from 2 ft. above to 1ft. below the soil surface 5 months annually.

A-4 Soil Classification Database Appendix A

Table A-1. (Continued) Category Codes and Associated Ranges for the SHWT Used in the Categorization of Duration. Category Codes and Associated Ranges for the SHWT

734 SHWT is from 2 ft. above to 1ft. below the soil surface 7 months annually.

736 SHWT is from 2 ft. above to 1ft. below the soil surface 9 months annually.

737 SHWT is from 2 ft. above to 1ft. below the soil surface 10 months annually.

740 SHWT is from the soil surface to 2 ft. above the surface.

741 SHWT is from the soil surface to 2 ft. above the surface 4 months annually.

742 SHWT is from the soil surface to 2 ft. above the surface 5 months annually.

744 SHWT is from the soil surface to 2 ft. above the surface 7 months annually.

745 SHWT is from the soil surface to 2 ft. above the surface 8 months annually.

746 SHWT is from the soil surface to 2 ft. above the surface 9 months annually.

747 SHWT is from the soil surface to 2 ft. above the surface 10 months annually.

748 SHWT is from the soil surface to 2 ft. above the surface 11 months annually.

749 SHWT is from the soil surface to 2 ft. above the surface 12 months annually.

800 Water areas. Water table is 2 ft. or more above the soil surface 12 months annually.

900 No data available for this area.

A-5 Appendix A Soil Classification Database

A-6 Soil Classification Database Appendix B

Appendix B ECOLOGICAL COMMUNITY CATEGORY DEFINITIONS

Table B-1. Category Definitions for the Ecological Community Categories. Category Category Primary Ecological Communities Category Definition and Number Name (as defined by NRCS, 1989) Description Permanently inundated areas. 1 Water None "Water" map units selected from database. Low wave energy coastal wetlands. Intra-Tidal Salt Marsh (#18) 2 Ecological communities #18 and #19 Wetlands Mangrove Swamp (#19) selected from database. High wave energy coastal lands that support 3 Beaches None beach communities. "Beaches" map units selected from database. Freshwater marshes and ponds. Ecological Scrub Cypress (#16) communities #9 (if SHWT-CAT 1 = 700), #12 Cypress Swamp (#17) Freshwater (if SHWT-CAT 1 = 700), #16, #17, #21, #22 4 Swamp Hardwoods (#21) Wetlands (if SHWT-CAT 1 = 700), #24 (if SHWT-CAT 1 Sawgrass Marsh (#24) = 700), #25, and #26 (if SHWT-CAT 1 = 700) Freshwater Marsh (#25) selected from database. Transitional mesic forested communities. Ecological communities #11 (if SHWT-CAT 1 Swamp Wetland Hardwood Hammocks (#12) = 600), #12 (if SHWT-CAT 1 < 700), #13 (if 5 Hammock Shrub Bogs - Bay Swamps (#22) SHWT-CAT 1 = 600 and hydric soil), #14 (SHWT-CAT 1 = 600), and #22 (if SHWT- CAT 1 = 600) selected from database. Freshwater wet prairies. Ecological communities. Ecological communities #8 Cutthroat Seeps (#10) 6 Wet Prairie (SHWT-CAT 1 = 600), #10, #24 (SHWT-CAT Slough (#26) 1 = 600), and #26 (SHWT-CAT 1 = 600) selected from database. Pine or palm dominated flatwood communities. Ecological communities #6 (if South Florida Flatwoods (#6) SHWT-CAT 1 > 500), #8 (if SHWT-CAT 1 = 7 Flatwoods Everglades Flatwoods (#9) 500), #9 (if SHWT-CAT 1 = 500 or 600), #13 (if SHWT-CAT 1 = 600 and nonhydric soil) selected from database. Upland forested communities that seldom flood. Ecological communities #3 (if SHWT- CAT 1 = 400), #4 (if SHWT-CAT 1 > 300), #6 Upland Hardwood Hammocks (#11) (if SHWT-CAT 1 = 400), #11 (if SHWT-CAT 1 8 Uplands Tropical Hammocks (#14) = 400), #13 (if SHWT-CAT 1 = 500), #14 (if SHWT-CAT 1 = 400 or 500), #15, and #24 (if SHWT-CAT 1 = 400) selected from database. Scrub or xeric communities. Flooding never occurs. Ecological communities #1, #2 North Florida Coastal Strand (#1) (except beaches), #3 (if SHWT-CAT 1 < South Florida Coastal Strand (#2) 400), #4 (if SHWT-CAT 1 < 300), #6 (if 9 Highlands Sand Scrub (#3) SHWT-CAT 1 = 100), #9 (if SHWT-CAT 1 = Longleaf Pine - Turkey Oak Hills (#4) 100), #11 (if SHWT-CAT 1 = 100), and #14 (if SHWT-CAT 1 = 100) selected from database. Selected "No Data" ecological community 10 N/A No data available for these map units. entries, urbanized, and drained map units.

B-1 Appendix B Soil Classification Database

B-2 Soil Classification Database Appendix C

Appendix C LANDSCAPE CLASSIFICATION CATEGORIES

Table C-1. Soil Series within Each NSLP Category with the Largest Aerial Extent.

Percent of NSLP NSLP Category Total Area (ha) Dominant Soil Series Category Area

#1: Water N/A N/A N/A

Durbin and Wulfert 31 % #2: Tidal Soils 96,588 Wulfert 11 Peckish 9

Biscayne 38 % #3 Marl & Rocky Soils 86,571 Perrine 21 Ochopee 17

Pahokee 32 % #4 Everglades Peat 297,460 Terra Ceia 31 Lauderhill 22

Samsula 17 % #5 Muck Depressions 266,540 Hontoon 13 Kaliga 11

Riviera 13 % Basinger #6 Sand Depressions 534,888 10 Boca, Riviera, Limestone substr. and 9 Copeland Complex

Basinger 20 % #7 Flats Soils 712,990 Pineda 16 Riviera 12

Immokalee 20 % #8 Flatwood Soils 1,473,561 Myakka 16 Smyrna 13

Pomello 16 % Tavares 16 #9 Knolls 242,228 Krome 10 Zolfo 10

Candler 45 % #10 Central Ridge- 135,394 Astatula 24 Dunes Neilhurst 7

#11 Urban or Made N/A N/A N/A Lands

#12 No Data N/A N/A N/A

C-1 Appendix C Soil Classification Database

Table C-2. Range of Map Unit Values within the NSLP Categories. Percentages Indicate the Relative Amount of Map Unit Area of the NSLP Category.

Map Unit Map Unit Map Unit Map Unit Map Unit Hydrologic Drainage Runoff NSLP Category SHWT Ranges SHWT Durations Groups Classes Potentials

Water (1) N/A N/A N/A N/A N/A

0.0 to 0.5 (94 %) 1.0 to 1.0 (4 %) Jan-Dec (100 %) VP (94 %) Tidal Soils (2) D (100 %) High (100 %) 0.0 to 6.0 (2 %) Other (less than 0.5 %) P (7 %) Other (less than 0.5 %)

0.0 to 1.0 (64 %) Jun - Sep (38 %) P (78 %) Marl & Rocky Soils -1.0 to 1.0 (34 %) Jun - Oct (17 %) D (100 %) High (74 %) VP (21 %) (3) 0.5 to 1.0 (1 %) Jun - Nov (31 %) Med. (26 %) SP (1 %) 0.0 to 0.5 (1 %) Jun - Dec (14 %)

-2.0 to 0.0 (68%) Jun - Apr (68 %) Everglades Peat (4) D (100 %) VP (100 %) High (100 %) -1.0 to 0.0 (32 %) Jun - Feb (32 %)

Jun - Oct (11 %) -2.0 to 0.0 (70 %) Jun - Dec (3 %) -1.0 to 0.0 (13 %) Jun - Jan (7 %) Muck Depressions 0.0 to 0.5 (9 %) Jun - Feb (1 %) D (100 %) VP (100 %) High (100 %) (5) -2.0 to 1.0 (5 %) Jun - Mar (1 %) -1.0 to 1.0 (2 %) Jun - Apr (72 %) 0.0 to 1.0 (1 %) Jan - Dec (6 %)

Jun - Sep (17 %) Jun - Oct (7 %) -2 to 0.0 (67 %) Jun - Nov (1 %) Sand Depressions -2 to 1.0 (19 %) Jun - Dec (3 %) VP (92 %) D (100 %) High (100 %) (6) 0.0 to 1.0 (7 %) Jun - Jan (2 %) P (8 %) 0.0 to 0.5 (7 %) Jun - Feb (11 %) Jun - Mar (58 %) Jun - Apr (1 %)

Jun - Sep (8%) Jun - Oct (8 %) 0.0 to 1.0 (94 %) P (100 %) High (100 %) Jun - Nov (41 %) Flats Soils (7) 0.0 to 0.5 (2 %) D (100 %) VP (less than Med. (less Jun - Dec (13 %) -1.0 to 1.0 (4 %) 0.5 %) than 0.5%) Jun - Feb (25 %) Jun - Mar (5 %)

0.5 to 1.5 (99 %) Jun - Sep (93 %) 2.0 to 3.5 (1 %) Jun - Oct (2 %) D (99 %) P (95 %) Flatwood Soils (8) 1.0 to 1.5 (less than 0.5%) N/A Jun - Nov (1 %) C (1 %) SP (5 %) 1.5 to 3.5 (less than 0.5%) Jun - Feb (4 %) 2.5 to 3.5 (less than 0.5%)

1.5 to 3.5 (16 %) 2.0 to 3.5 (30 %) 2.5 to 5.0 (1 %) Jun - Sep (1 %) 3.5 to 6.0 (26 %) Jun - Oct (4 %) 0.0 to 6.0 (1 %) Jun - Nov (46 %) 1.5 to 3.0 (2 %) Jun - Dec (21 %) 3.5 to 5.0 (3 %) Jun - Feb (3 %) Knolls (9) 4.0 to 5.0 (11 %) Jul - Oct (6 %) N/A N/A N/A 3.0 to 5.0 (2 %) Jul - Nov (15 %) 2.0 to 3.0 (1 %) Jul - Dec (1 %) 4.0 to 6.0 (2 %) Jul - Jan (2 %) 5.0 to 6.0 (2 %) Jan - Dec (1 %) 2.0 to 8.0 (less than 0.5%) Aug - Feb (1 %) 2.5 to 3.5 (less than 0.5%) 1.0 to 3.0 (5 %)

C-2 Soil Classification Database Appendix C

Table C-2. (Continued) Range of Map Unit Values within the NSLP Categories. Percentages Indicate the Relative Amount of Map Unit Area of the NSLP Category.

Map Unit Map Unit Map Unit Map Unit Map Unit Hydrologic Drainage Runoff NSLP Category SHWT Ranges SHWT Durations Groups Classes Potentials

Central Ridge- 6.0 to 6.0 (98%) N/A (98%) E (92%) A (100%) N/A Dunes (10) 0.0 to 6.0 (2%) Jun - Oct (2%) W (6%)

Urban or Made N/A N/A N/A N/A N/A Lands (11)

No Data (12) N/A N/A N/A N/A N/A

C-3 Appendix C Soil Classification Database

C-4 Soil Classification Database Appendix D

Appendix D SELECTED ECOLOGICAL COMMUNITIES

The following descriptions of ecological communities are based on the NRCS publication The 26 Ecological Communities of Florida (SCS, 1989).

SOUTH FLORIDA COASTAL STRAND (ECOLOGICAL COMMUNITY NO. 2)

Range: The South Florida Coastal Strand ecological community occurs along the Atlantic Ocean south of Brevard County and along the Gulf of Mexico south of Pasco County. Individual communities are generally large in size, being narrow, long, and parallel to the coastal beaches. Small, isolated communities can also be found along some bays or sounds. This community generally encompasses the area affected by salt sprays from the ocean, gulf, and saltwater bays.

Soils: The soils are nearly level to strongly sloping, deep, mostly well to excessively drained with some moderately well drained or somewhat poorly drained. They are coarsely textured throughout. Representative soils include: Canaveral and Palm Beach. It also includes areas mapped as Coastal Beach and Coastal Beach Ridges.

Vegetation: The natural vegetation of this community is low growing grasses, vines, and herbaceous plants with few trees or large shrubs. These trees and shrubs often occur in stunted form due to the action of the wind. The natural forces of wind, salt, and blowing sand make plant establishment difficult on the foredunes. Plants which do establish here are well adapted to disturbance and are pioneer species. The backdunes will often have vegetation similar to the sand pine scrub or the wetland hardwood hammock ecological communities. Plants which characterize this community are: cabbage palm (Sabal palmetto), coconut palm (Cocos nucifera), sand live oak (Quercus virginiana var. maritima), bay cedar (Suriana maritima), inkberry (Scaevola plumieri), marsh elder (Iva imbricata), saw palmetto (Serenoa repens), silverleaf croton (Croton punctatus), Spanish bayonet (Yucca aloeifolia), sea grape (Coccoloba uvifera), bay bean (Canavalia maritima), railroad vine (Ipomoea pes-caprae), beachdune sunflower (Helianthus debilis), sea purslane (Sesuvium portulacastrum), sea oats (Uniola paniculata), seashore paspalum (Paspalum vaginatum), and seashore saltgrass (Distichlis spicata). The following endangered or threatened plants may occur in this community: beach star (Remirea maritima), small flowered lily-thorn (Catesbaea parviflora, Florida Keys), burrowing four-O’clock (Okenia hypogaea), sea lavender (Mallatonia gnaphalodes), beach creeper (Ernodea littoralis), west coast prickly apple (Cereus gracilis), and the fragrant prickly apple (Cereus eriophorus var. frangrans), St. Lucie County.

Wildlife: A variety of shorebirds, terns, and gulls can be found on or near the beach. This community provides good food sources as well as nesting sites. Small mammals can also be found on the coastal dunes. Larger mammals also occur behind the

D-1 Appendix D Soil Classification Database foredunes. Some species that occur are: bobcat (Lynx rufus), eastern spotted skunk (Spilogale putorius), raccoons (Procyon lotor), mice, American kestrel (Falco sparverius), pelicans, gulls, terns, shorebirds, songbirds, frogs, and lizards. This area also serves as nesting grounds for sea turtles. Crustaceans such as crabs are numerous near the shorelines. The following protected species may be found in or around this community: pallid beach mouse (Peromyscus polionotus decoloratus), Goff’s pocket gopher (Geomys pinetis goffi), peregrine falcon (Falco peregrinus tundrius), piping plover (Charadrius melodus), southeastern snowy plover (Charadrius alexandrinus tenuirostris florida), least tern (Sterna antillarum), Atlantic green turtle (Chelonia mydas mydas), Atlantic coast only), Atlantic hawksbill turtle (Eretmochelys imbricata imbricata), Atlantic loggerhead turtle (Caretta caretta caretta), Atlantic ridley turtle (Lepidochelys kempi), and the leatherback turtle (Dermochelys coriacea).

Environmental Value as a Natural System: The coastal strand is highly endangered. Areas privately owned but undeveloped are in demand for residences, hotels and motels. This urban development can have serious effects on the community. Coastal strands are important in regulating wave action along the coast. This action tends to break away part of one beach and build up another. Unplanned structures and development which alter this process accelerates beach and coastal dune erosion through removal of native vegetation, which helps hold the dune together, and by removal of sand from the offshore transport system. Recreational use and wildlife values on the coastal strand are important. Recreation is much in demand in these areas but can cause damage due to trampling and destroying vegetation. When these plants die, their extensive root systems are no longer available to hold the soil together and build the dune. Occasional use may also degrade this fragile community.

Rangeland: This community is not generally used for rangeland.

Woodland: This community is not generally used for woodland.

Urbanland: The better drained areas inland from the ocean or gulf have few limitations for urban development. Areas adjacent to the water may be subject to coastal dune and beach erosion. This is especially true where construction alters the natural processes and destroys excessive amounts of native vegetation. Vegetation is difficult to establish because of the infertile, coarse textured, well to excessively well drained and saline soils and the salt spray. Intensive vegetation establishment and maintenance methods are needed for best results. Without vegetation, water and wind erosion can become a problem during and after construction. Plants native to the community should receive preference for beautification and landscaping. This is because they are more easily established and require less maintenance. Some of the trees are: cabbage palm, coco plum (Chrysobalanus icaco), Florida thatch palm (Thrinax spp.), Florida silver thatch palm (Coccothrinax argentata), live oak (Quercus virginiana), pigeon plum (Coccoloba diversifolia), red bay (Persea borbonia), slash pine (Pinus elliottii var. densa), magnolia (Magnolia grandiflora), wild tamarind (Lysiloma latisiliqua), and sand pine (Pinus clausa). Some of the shrubs are: prickly pear cactus (Opuntia spp.), sea grape (Coccoloba uvifera), coontie (Zamia pumila), coral bean (Erythrina herbaceae), yaupon holly (Ilex:vomitoria), lantanas, partridge pea (Cassia spp.), marsh elder (Iva spp.) saw

D-2 Soil Classification Database Appendix D palmetto, Spanish bayonet, and wax myrtle (Myrica cerifera). Some of the grasses and herbaceous plants include: sea oats (Uniola paniculata), marsh hay cordgrass (Spartina patens), seashore dropseed (Sporobolus virginicus), blanket flower (Gaillardia pulchella), sea purslane (Sesuvium portulacastrum), and wild grape (Vitis rotundifolia).

SAND PINE SCRUB (ECOLOGICAL COMMUNITY NO. 3)

Range: The Sand Scrub ecological community occurs throughout Florida. It is most commonly found inland from the coast and in the central portion of the state in and around Marion County. Individual communities are generally small in size, (several hundred acres) and a few remnants still exist along the southeast coast in Palm Beach and Martin counties. A large community (several thousands of acres in size) occurs just east of Ocala in the Ocala National Forest. It typically has a few smaller communities of wetland types interspersed throughout.

Soils: The soils are nearly level to strongly sloping, deep, acid, somewhat poorly to excessively drained and course textured throughout. Representative soils include Archbold and Pomello.

Vegetation: The natural vegetation of this community may be typically even-aged sand pine trees with a dense understory of oaks, saw palmetto (Serenoa repens), and other shrubs. Ground cover under the trees and shrubs is scattered and large areas of light colored sand are often noticeable. In other cases, the sand pine are scattered or absent, with oaks being the dominant vegetation. Satellite soils, which have a high water table for part of the year, support scrubby growth also, but the myrtle oak, Chapman oak, and sand pine become infrequent and gallberry (Ilex glabra) becomes prominent. Plants which characterize this community are: Chapman oak (Quercus chapmannii), myrtle oak (Quercus mytifolia), sand live oak (Quercus virginiana var. geminata), sand pine (Pinus clausa), gopher apple (Chrysobalanus oblongifolius), prickly pear (Opuntia spp.), saw palmetto, grassleaf goldenaster (Heterotheca graminifolia), deermoss (Cladonia spp.), cat greenbriar (Smilax glauca), yellow Indian grass (Sorghastrum nutans), and low panicum (Panicum spp.). The following protected plants may occur in this community: four-petal pawpaw (Asimina tetramera), pigmy fringetree (Chionanthus pyfmaea), Curtis’ milkweed (Asclepias curtissii), dancing-lady orchid, (Tolumnia bahamense), and Florida bonamia (Bonamia grandiflora).

Wildlife: Animals found in this community are adapted to high temperatures and droughty conditions. The wildlife food production is low. Dense vegetation provides good escape cover for animals such as deer (Odocoileus virginianus). The palmetto, various species of oaks and gopher apple provide good food sources. Typical animals of the sand scrub are: towhee (Popilo erythrophthalmus), great crested flycatcher (Myiarchus crinitus), Bachman’s sparrow (Aimophila aestivalis), black racer (Coluber constrictor), gopher tortoise (Gopherus polyphemus), scrub lizard (Sceloporus woodi), and the gopher frog (Rana areolata). The following protected wildlife species may be found in or around this community: Goff’s pocket gopher (Geomys pinetis goffi), Florida scrub jay (Aphelocoma coerulescens coerulescens), blue-tailed mole skink (Eumeces egregius

D-3 Appendix D Soil Classification Database lividus), sand skink (Neoseps reynoldsi), and the short-tailed snake (Stilosoma extenuatum).

Environmental Value as a Natural System: The sand scrub is a fire-based community. Understory vegetation is dense and fuel supplies build up in the trees. The thick understory creates a pathway for fire to the crowns of the trees. Fire normally occurs every 20 to 40 years. Sand pines have a low resistance to fire and the high density, even- aged stands make fire devastating to this community. Cones of the sand pine require the heat of a fire to open and release seeds. This method of regeneration helps to form even- aged stands. Without occasional fire, this community would tend to become a type of upland hammock community. The sand scrub is a valuable ecological community. The coarse textured, excessively well drained soils make the community important in aquifer recharge. It is a unique ecosystem which gives it an important scientific value. Heat and drought stress response by plants and animals are often studied on these sites. Uncontrolled fire and damage to vegetation by excessive foot or vehicle travel have adverse effects on the community.

Rangeland: This community supports a fairly dense stand of trees and shrubs and therefore has a limited potential for producing native forage. Livestock do not use this site if other ecological communities are available. For sites in excellent condition the average annual production of air dry plant material varies from 1,500 to 3,500 pounds per acre. The variation depends on plant growth conditions. From fifteen to more than forty acres are usually needed per animal unit depending upon amount and type of forage available. The relative percentage of annual vegetative production by weight is 40 percent grasses, 40 percent trees and shrubs and 20 percent herbaceous plants and vines. Adverse soils conditions make it infeasible to convert this community to cropland. It has been converted to some extent for citrus production in South Florida.

Woodland: Sand scrubs are good producers of sand pine and some areas are utilized for commercial wood production. Intensive management for wood production will not cause excessive damage to the community if good silvicultural practices are applied. There are severe equipment limitations and moderate seedling mortality problems due to loose, well to excessively well-drained and infertile soil conditions. Sand pine is a commercial species suitable for planting. It has a potential annual growth of approximately 0.5 cords per acre in North Florida. South of Hernando County in the west and Orange County in the east, the potential annual growth is 0.4 cords per acre.

Urbanland: The moderately well to excessively well drained areas have few limitations for urban development. The somewhat poorly drained Satellite soils, although very droughty in the surface layers, have a water table at 20 inches for part of the year and has more limitations. Vegetation is difficult to establish because of the infertile, coarse textured, and droughty surface soils. Water moves rapidly through the soil. Intensive vegetation establishment and maintenance methods, including irrigation are needed for best results. Without vegetation, wind erosion can be a problem during and after construction. Water erosion control and water retention facilities are usually not needed. Plants native to the community should receive preference for beautification and landscaping. This is because they are more easily established and require less

D-4 Soil Classification Database Appendix D maintenance. Some of the trees are: live oak, sand live oak, sand pine, turkey oak (Quercus laevis), and red cedar (Juniperus silicicola). Some of the shrubs are: Spanish bayonet (Yucca aloeifolia), coral bean (Erythrina herbaceae), gopher apple, pawpaw (Asimina spp.), prickly pear cactus (Opuntia spp.), rosemary (Ceratiola ericoides), saw palmetto, and shining sumac (Rhus copallinum). Some of the herbaceous plants are: asters, blanketflower (Gaillardia pulchella), blazing star (Liatris spp.), golden aster (Pityopsis graminifolia), goldenrods (Solidago spp.), lupine (Lupinus spp.), morning glories (Ipomoea spp.), and beach dune sunflower (Helianthus debilis).

SOUTH FLORIDA FLATWOODS (ECOLOGICAL COMMUNITY NO. 6)

Range: The South Florida Flatwoods ecological community occurs throughout South and Central Florida. The northern limit of its occurrence is approximately on a line from Levy County on the west to St. Johns County on the east. This community covers more land area than any other in South Florida. Individual communities may comprise several thousand acres and are typically interspersed with smaller communities of other types, especially wetlands. This community occurs on nearly level land. Water movement is very gradual to the natural drainageways, swamps, marshes, and ponds associated with this community. During the rainy season, usually June through September, this community may have water on or near the soil surface. It is easily identified by the flat topography and pine and palmetto vegetation.

Soils: The soils are nearly level, deep, acid, poorly to somewhat poorly drained. They are usually course textured in the upper part and variably textured below. Representative soils include: Electra, Immokalee, and Myakka.

Vegetation: The landscape position of this community affects plant-water relationships and causes slight differences in plant composition from wetter to drier areas. Although these differences are recognized, they are not significant enough to delineate as separate communities. The natural vegetation of this community is typically scattered pine trees with an understory of saw palmetto (Serenoa repens) and grasses. Some of these areas in South Florida have few, if any, trees. These are often called prairies or dry prairies. The largest of these areas occur north and west of Lake Okeechobee. Plants which characterize this community are: live oak (Quercus virginiana), South Florida slash pine (Pinus elliottii var. densa), ground blueberry (Vaccinium myrsinites), gallberry (Ilex glabra), tarflower (Befaria racemosa), shining sumac (Rhus copallinum), wax myrtle (Myrica cerifera), chalky bluestem (Andropogon capillipes), South Florida bluestem (Schizachyrium rhizomatum), and the pineland threeawn (Aristida stricta).

Wildlife: The South Florida Flatwoods community is host to a diverse and numerous wildlife population. Many larger animals are found in areas where the flatwoods join other communities. These ecotones provide nesting sites, den sites, food and cover. Typical animals of the flatwoods are: armadillo (Dasypus novemcinctus), rabbits, cotton rat (Sigmodon hispidus), deer (Odocoileus virginianus), eastern spotted skunk (Spilogale putorius), raccoons (Procyon lotor), opossum (Didelphis virginiana),

D-5 Appendix D Soil Classification Database

Bachman’s sparrow (Aimophila aestivalis), bobwhite quail (Colinus virginianus), brown- headed nuthatch (Sitta pusilla), eastern meadowlark (Sturnella magna), pileated woodpecker (Dryocopus pileatus), pine warblers (Dendroica pinus), rufous-sided towhee (Pipilo erythrophthalmus), eastern diamondback rattlesnake (Crotalus adamanteus), oak toad (Bufo quercicus), and the pinewoods tree frog (Hyla femoralis). Introduced feral hogs are common in much of the community. The following endangered or threatened wildlife species may be found in or around this community: Florida panther (Felis concolor coryi), mangrove fox squirrel (Sciurus niger avicennia), crested caracara, Florida grasshopper sparrow (Ammodramus savannarum floridanus), southeastern kestrel (Falco sparverius paulus), red-cockaded woodpecker (Picoides borealis), bald eagle (Haliaeetus leucocephalus), sandhill crane (Grus canadensis pratensis), and the eastern indigo snake (Drymarchon corais couperi).

Environmental Value as a Natural System: Fire and water are the major stress conditions of this community. Fire controls hardwoods and promotes the natural regeneration of pine. Removal of fire will cause a successional move to a hardwood community. Flatwood communities are good cellulose producers and the original areas of predominantly longleaf pine have been logged. Areas in the northern part of the community are extensively used for timber production. Intensive management for pulp production can cause major changes in the vegetation. Without proper consideration this results in a low diversity of plants and an adverse change in some wildlife populations. This community has good wildlife values, especially with proper management. It is especially important as a wildlife buffer zone between urban areas occurring on better drained sites.

Rangeland: This ecological community has the potential for producing significant amounts of high quality native forage such as chalky bluestem, and indian grass (Sorghastrum spp.). It is Florida’s most important community for the production of cattle on native range. For sites in excellent condition, the average annual production of air dry plant material varies from 3,000 to 6,000 pounds per acre. The variation depends on plant growth conditions. From four to more than eighteen acres are usually needed per animal unit depending upon amount and type of forage available. There will be little forage available if the canopy cover exceeds 60 percent. The relative percentages of annual vegetative production by weight is 75 percent grasses and grass-like plants, 15 percent trees and shrubs, and 10 percent herbaceous plants.

Woodland: This community has a moderate potential productivity for commercial wood production. There are moderate equipment limitations and seedling mortality due to wet soil conditions. The commercial species suitable for planting is slash pine. Potential annual growth is 0.9 cords per acre. The potential annual growth for longleaf pine is 0.5 cords per acre. Potential productivity is 18 percent less for soils south of a line from Hernando County in the west to Orange County in the east.

Urbanland: This community is subject to high water tables during the rainy season and has limitations for urban development. Water management systems are required for urban uses. It is often difficult to establish vegetation on steep channel side slopes and infertile soil and special techniques may be required. Without vegetation,

D-6 Soil Classification Database Appendix D erosion and sedimentation is often a problem in some water management systems. Wind erosion is a problem in unvegetated areas. This is especially severe in the spring. Native plants can be used for beautification and require minimum establishment and maintenance. Some of the trees are: cabbage palm (Sabal palmetto), persimmon (Diospiros virginiana), live oak (Quercus virginiana), and slash pine (Pinus elliottii var. densa). Some of the shrubs are: American beauty berry (Callicarpa americana), coontie (Zamia pumila), coral bean (Erythrina herbaceae), partridge pea (Cassia spp.), pawpaw (Asimina reticulata), saw palmetto (Serenoa repens), shining sumac (Rhus copallinum), tarflower (Befaria racemosa), and wax myrtle (Myrica cerifera). Some of the herbaceous plants are: blazing star (Liatris spp.), pineland lily (Lilium catesbaei), asters, meadow beauty (Rhexia spp.), and zephyr lily (Zephyranthes spp.).

SCRUB CYPRESS (ECOLOGICAL COMMUNITY NO. 16)

Range: The Scrub Cypress ecological community occurs only in South Florida on marl and rock that is frequently flooded. Eastern Collier County and northern Monroe County have the largest areas of this community. This region is called “Big Cypress.” This community appears as a broad area of marshes with dwarf cypress (less than 20 feet tall) scattered throughout. It is stressed by the extreme seasonal change in water levels, and low level of plant nutrients. These factors cause poor growing conditions with a lack of plant diversity and small wildlife populations in comparison to the cypress swamp community.

Soils: The soils associated with this community are nearly level, poorly to very poorly drained, with coarse to medium textured surfaces underlain by finer textured material or fractured limestone. A representative soil is Margate.

Vegetation: The vegetation is much like that of the freshwater marsh community. Occasional air plants and orchids can be found in the scattered cypress trees. Plants which characterize this community are: bald cypress (Taxodium distichum), pond cypress (Taxodium distichum var. nutans), wax myrtle (Myrica cerifera), stiff-leafed wild pine (Tillandsia fasiculata), yellow-eyed grass (Xyris spp.), blue maidencane (Amphicarpum muhlenbergianum), bluejoint panicum (Panicum tenerum), chalky bluestem (Andropogon capillipes), cutgrass (Leersia hexandra), gulfdune paspalum (Paspalum monostachyum), and maidencane (Panicum hemitomon). The following protected plant species may be found in or around this community: Acuna’s epidendrum (Epidendrum acunae), auricled spleenwort (Asplenium auritum), bird’s nest spleenwort (Asplenium serratum), cow-horn orchid (Cyrtopodium punctatum), dwarf epidendrum (Encyclia pygmaea), hidden orchid (Maxillaria crassifolia), leafless orchid (Campylocentrum pachyrrhizum), night-scented orchid (Epidendrum nocturnum), and nodding catopsis (Catopsis nutans).

Wildlife: The poor soil and lack of plant nutrients that are responsible for the relatively sparse plant life also account for a fairly scattered wildlife population. This community is one of the least productive of wildlife. Deer (Odocoileus virginianus) will range through these areas, but the habitat is poor. The primary value is seasonal to frogs, turtles, snakes, and salamanders which can adjust to the short hydroperiod. It is also use

D-7 Appendix D Soil Classification Database by predators of these animals such as raccoons (Procyon lotor), mink (Mustela vison), and wading birds. Other wildlife species include bobcat (Lynx rufus), and herons. The following protected animal species may be found in or around this community: Florida panther (Felis concolor coryi), roseate spoonbill (Ajaja ajaja), wood stork (Mycteria americana), and American alligator (Alligator mississippiensis).

Environmental Value as a Natural System: The scrub cypress community occurs primarily in southwest Florida. Developments in and around the community cause changes in water quality and quantity which results in wide changes in portions of the plant community. The scrub cypress community is highly endangered. Scrub cypress swamps provide water storage areas by holding excess water and slowly releasing it into the water table. Water quality is enhanced by the community, which functions like a waste treatment plant by absorbing nutrients from the water.

Rangeland: This ecological community has the potential for producing significant amounts of high quality forage such as South Florida bluestem, gulfdune paspalum, chalky bluestem, and bluejoint panicum. For sites in excellent condition, the average annual production of air dry plant material varies from 1,500 to 4,500 pounds per acre. The variation depends on plant growth conditions. From nine to more than twenty- two acres are usually needed per animal unit depending upon amount and type of forage available. The relative percentages of annual vegetative production by weight is 75 percent grasses and grass-like plants, 15 percent trees and shrubs, and 10 percent herbaceous plants.

Woodland: These areas are not generally used for commercial woodland production. However, this community does have a moderate potential productivity for commercial woodland production on areas with adequate surface drainage. There are severe equipment limitations due to the poorly drained soil conditions. Slash pine is the species suitable for planting on areas with adequate surface drainage. Potential annual growth is 0.7 cords per acre.

Urbanland: This community is subject to periodic flooding and has severe limitations for urban development. Elaborate water management systems are required for urban uses. It is difficult to establish vegetation on steep channel side slopes and infertile spoil. Special techniques such as mulching, selected plants, and unusual seeding and plant management techniques may be required. Native plants can be used for beautification and require minimum establishment and maintenance. Some of the trees are: bald cypress, cabbage palm (Sabal palmetto), pond cypress, and slash pine (Pinus elliottii var. densa). Some of the shrubs are buttonbush (Cephalanthus occidentalis), dahoon holly (Ilex cassine), and wax myrtle.

CYPRESS SWAMP (ECOLOGICAL COMMUNITY NO. 17)

Range: The Cypress Swamp ecological community occurs along rivers, lake margins, slough and strands, or interspersed throughout other communities such as Flats (NSLP #7) and Flatwoods (NSLP#8). It occurs throughout Florida, but is the predominant

D-8 Soil Classification Database Appendix D swamp type in the area from Flagler County south through Polk County, and in southwest Florida. The “Big Cypress” area of Monroe and Collier counties is included in ecological community #16- Scrub Cypress.

Soils: This community is poorly drained and water is at or above ground level a good portion of the year. Soils commonly associated with this community are nearly level or depressional, poorly drained and have loamy subsoils and sandy surfaces.

Vegetation: Bald cypress (Taxodium distichum) is the dominant tree and is often the only plant which occurs in significant numbers. The diversity of tree species is low in cypress heads but increases in strands and along stream margins. The submergence or saturated condition of the soil and general absence of fire help reduce competition and keeps the community from a successional change to a swamp hardwood (bay head) community. Cypress swamps growing on sand, rock, and shallow mucky pond areas are not as productive as those found on alluvial flood plain soils. Plants which characterize this community are: bald cypress, pond cypress (Taxodium distichum var. nutans), coastal plain willow (Salix caroliniana), red maple (Acer rubrum), buttonbush (Cephalanthus occidentalis), wax myrtle (Myrica cerifera), cinnamon fern (Osmunda cinnamomea), royal fern (Osmunda regalis), Spanish moss (Tillandsia usneoides), giant wild pine (Tillandsia utriculata), and maidencane (Panicum hemitomon). Some of the protected plants that may be found in this ecological community include: the bird’s nest spleenwort (Asplenium serratum), climbing dayflower (Commelina gigas), fuzzy-wuzzy airplant (Tillandsia pruinosa), giant water dropwort (Oxypolis greenmanii), hidden orchid (Maxillaria crassifolia), nodding catopsis (Catopsis nutans), and grass-of-Parnassus (Parnassia graniflora).

Wildlife: This community is very important as a wildlife refuge and roosting area. It is well-suited for waterfowl and wading birds. Aquatic animals may be found in large numbers. The permanent residents of cypress heads are relatively few, but much of the wildlife of the flatwoods is dependent on these ponds for breeding purposes. The most common wildlife species include: deer (Odocoileus virginianus), raccoons (Procyon lotor), river otters (Lutra canadensis), Anhinga (Anhinga anhinga), barred owl (Strix varia), egrets, herons, limpkins (Aramus guarauna), pileated woodpecker (Drycopus pileatus), wood ducks (Aix sponsa), frogs, turtles, and a variety of water snakes. Some protected animal species that may be found in this ecological community include: Everglades mink (Mustela vison evergladensis), wood stork (Mycteria americana), American alligator (Alligator mississippiensis), bald eagle (Haliaeetus leucocephalus), and the Florida black bear (Ursus americanus floridanus).

Environmental Value as a Natural System: Cypress swamps are an extremely valuable resource. They can be used for environmental education study, scientific research, and recreation. They have a high value for use as wildlife habitat. This community has a relatively low diversity of plant species due to fluctuating water levels and low nutrient availability. Both drastic changes in mean water level and a stabilized water level may change the plant community. Often this will occur due to the effects of dams, dikes, or drainage channels. Stagnant water will result in slow tree growth especially if it occurs during the growing season. Natural regeneration of cypress requires

D-9 Appendix D Soil Classification Database fluctuation of the water and flooding during the dry season will prevent the cypress trees from reproduction.

Rangeland: This community has little or no value as rangeland.

Woodland: Extensive drainage would be required, thereby destroying this community.

Urbanland: This community is subject to periodic flooding and has severe limitations for urban development. Elaborate water management systems are required for urban uses. It is often difficult to establish vegetation on steep channel side slopes and infertile spoil. Special techniques such as mulching, special plants, and unusual maintenance techniques may be required. Without vegetation, erosion and sedimentation are a problem. Intensive management measures may also be necessary to maintain design capacity. Native plants can be used for beautification and require minimum establishment and maintenance. Some trees that can be used for this purpose are: bald cypress, button mangrove (buttonwood) (Conocarpus erectus), loblolly bay (Gordonia lasiathus), pond cypress, red maple, South Florida slash pine (Pinus elliottii var. densa), and sweet gum (Liquidambar styraciflua). Some of the shrubs are: buttonbush, coco plum (Chrysobalanus icaco), dahoon holly (Ilex cassine), and wax myrtle. Some herbs include asters, golden canna (Canna flaccida), cardinal flower (Lobelia cardinalis), pineland lily (Lilium catesbaei), ferns, coneflowers (Rudbeckia spp.), cattails (Typha spp.), rose mallow (Hibiscus spp.), and meadow beauty (Rhexia spp.).

SALT MARSH (ECOLOGICAL COMMUNITY NO. 18)

Range: The Salt Marsh community occurs along the Atlantic and Gulf Coasts, and inland along tidal rivers. An extensive area occurs along the Gulf of Mexico north of Tarpon Springs to St. Marks. Smaller isolated areas occur inland where salt springs rise near rivers. This community appears as an open expanse of grasses, sedges, and rushes. Usually there is a matrix of interconnected shallow natural channels that aid tidal influx.

Soils: Soils commonly associated with this community are nearly level and very poorly drained. They can be muck or sandy clay loams underlain by loamy sand, or organic soils underlain by clay or sand, or clayey throughout. Many of the soils have a high sulfur content. Some of the soils are soft and will not support the weight of a man or large animal. Tidal action causes saturation of the soil with salt water and inundation to a depth of a few inches. Representative soils include Estero and Wulfert.

Vegetation: Plant species often occur in distinct zones as a result of differing mean water levels and salinity concentrations. Some species, such as black needlerush (Juncus roemeiranus) and seashore saltgrass (Distichlis spicata), have a wide tolerance range and may be found throughout the grass marsh. Smooth cordgrass (Spartina alterniflora) is more indicative of low, regularly flooded marsh, while the high marsh supports: sea myrtle (Baccharis halimifolia), marsh hay cordgrass (Spartina patens), marsh elder (Iva spp.), saltwort (Batis maritima), and sea oxeye (Borrichia spp.). Along

D-10 Soil Classification Database Appendix D the Gulf Coast most marshes are dominated by black needlerush. Other plants that characterize the salt marsh community are: sea blite (Suaeda linearis), sea purslane (Sesuvium portulacastrum), and cordgrasses (Spartina spp.).

Wildlife: Salt marshes are good habitat for a variety of wildlife. The habitat type is usually maintained by natural forces such as tidal action and periodic hurricanes. Storms usually cause the creation of “open” water in salt and brackish marshes and also may change salinities. The resulting effect is that plant succession is set back and more favorable habitat may be created for waterfowl, furbearers, and some other forms of wildlife such as wading birds. Artificially created dikes to control salinity are used in managing marsh plants for wildlife. Prescribed burning is also a technique used in marsh management.

The salt marshes support a variety of wildlife. Some common species that occur are: white tail Deer (Odocoileus virginianus), raccoons (Procyon lotor), river otters (Lutra canadensis), pelicans, coots, egrets, gulls, terns, many forms of waterfowl. Protected species include: the West Indian manatee (Trichechus manatus latirostris), Cape Sable seaside sparrow (Ammodramus maritimus mirabilis, Collier, Monroe, and Miami- Dade Counties only), least tern (Sterna antillarum); peregrine falcon (Falco peregrinus tundrius), roseate tern (Sterna dougallii), bald eagle (Haliaeetus leucocephalus), wood stork (Mycteria americana), Atlantic green turtle (Chelonia mydas mydas), Atlantic hawksbill turtle (Eretmochelys imbricata imbricata), American alligator (Alligator mississippiensis), Florida ribbon snake (Thamnophis sauritus sackeni, Lower Keys population), and the Atlantic saltmarsh water snake (Nerodia fasciata taeniata).

Environmental Value as a Natural System: The functions of salt marshes are probably the most important and least understood of all ecological communities. On low energy coastlines and estuaries, the marsh functions as a transition zone from terrestrial to oceanic life. Salt marshes also perform an important function in the stabilization and protection of shorelines, especially during storm tides.

Nutrients, sediments and detritus from upland systems are redistributed by tidal action, making the marsh one of the most productive natural ecological systems. The area serves as a habitat for the early life stages of numerous ocean species as they feed on countless invertebrate organisms. Many wildlife forms overlap normal ranges at least seasonally to become harvesters and, in many cases, part of the natural food chain.

Rangeland: Salt marshes have a potential for producing significant amounts of cordgrass, saltgrass, and other grasses and forbs. For sites in excellent condition, the average annual production of air-dried plant materials varies from 4,000 to 8,000 pounds per acre, depending on plant growth conditions. From three to more than fifteen acres are usually needed per animal unit depending upon amount and type of forage available. The relative percentage of annual vegetative production by weight is 90 percent grasses, 5 percent shrubs and trees, and 5 percent herbaceous plants and vines.

Woodland: These soils are unsuitable for commercial wood production.

D-11 Appendix D Soil Classification Database

Urbanland: This community is subject to a high water table and periodic flooding. Therefore, it has very severe limitations for urban development. Very elaborate water management systems are required for urban uses. It is difficult to establish salt tolerant vegetation on steep channel side slopes and infertile spoil. Special techniques such as mulching, and unusual seeding and management techniques, will be required. Without vegetation, erosion and sedimentation become a problem. Intensive measures may also be required to maintain design capacity. Native plants can be used for beautification and require minimum establishment and maintenance. Some of the trees and shrubs are: black mangrove (Avicennia germinans), button mangrove (buttonwood) (Conocarpus erectus), necklace pod (Sophora tomentosa), sea oxeye, southern red cedar (Juniperus silicicola), and white mangrove (Laguncularia racemosa). Some of the herbaceous plants are: asters and goldenrod (Solidago spp.). Some of the grasses are: cordgrasses, seashore dropseed (Sporobolus virginicus), and seashore saltgrass.

SAWGRASS MARSH (ECOLOGICAL COMMUNITY NO. 24)

Range: The Sawgrass Marsh ecological community occurs south of Lake Okeechobee in the historic Everglades Basin. This community covers many thousands of acres. Smaller sawgrass marshes are found outside of this area, but they are included in the Freshwater Marsh and Ponds ecological community (#25).

Soils: Soils commonly associated with this community are nearly level and very poorly drained organic surfaces underlain by limestone. Representative soils are Torry and Terra Ceia.

Vegetation: The natural vegetation of this community is dominated by sawgrass. Muhly grass (Muhlenbergia capillaris) increases and becomes obvious when the sawgrass is repeatedly exposed to fire and the hydroperiod is shortened. With natural conditions, the vigorous sawgrass is 6 to 10 feet tall and of such density that few other plants can survive. Other marsh plants invade where marginal conditions occur for sawgrass growth, such as shallow organic soils and areas where the period of water submergence is short. Trees are not characteristic of this community, but a few may occur on the banks of gator holes. Plants that characterize this community are: sawgrass, gulf muhley (Muhlenbergia capillaris var. filipes), plume grass (Erianthus spp.), and pickerelweed (Pontederia cordata).

Wildlife: Numerous birds use this community year-round or for over-wintering. Frogs, snails, and crayfish are common and serve as food for larger animals. Animals that commonly occur in this community include: white tail (Odocoileus virginianus), red- winged blackbirds (Agelaius phoeniceus), egrets, herons, ibis, bitterns, and water snakes. Protected species that may be found in or around the sawgrass community include: Everglades mink (Mustela vison evergladensis), Florida panther (Felis concolor coryi), snail kite (Rostrhamus sociabilis), wood stork (Mycteria americana), and American alligator (Alligator mississippiensis).

D-12 Soil Classification Database Appendix D

Environmental Value as a Natural System: The sawgrass marshes serve as filter systems for water. They protect natural bodies of water from eutrophication. Marshes can help moderate drought and flood events. Their principal environmental values are related to water quality and quantity. Tall, dense sawgrass occurs in deep organic soils and requires water coverage of the rhizomes for most of the year. It also forms extensive, but shorter and less dense stands on marl soils in South Florida. Drainage, organic soil subsidence, and fires have reduced the amount of sawgrass and promoted the growth of other plants in many areas. Although the sawgrass community is one of the most resistant communities to change under natural conditions, severe fires and water quality reduction can completely alter the community’s characteristics within 10 to 20 years.

Rangeland: This site provides little to no native forage values.

Woodland: This community is not generally recommended for woodland.

Urbanland: This community is subject to very high water tables and has severe limitations for urban development. Intensive and complex water management systems are required for urban uses. It is often difficult to establish vegetation on steep channel side slopes and infertile spoil. Special techniques are usually required in these situations. Without vegetation, erosion and sedimentation can become a problem. Much of the sawgrass marsh is now included in public lands and is not available for urban uses.

FRESHWATER MARSH AND PONDS (ECOLOGICAL COMMUNITY NO. 25)

Range: The Freshwater Marsh and Ponds ecological community occurs throughout Florida. Individual communities vary widely in size. The largest communities, several thousand acres in size, generally occur in southeast Florida.

Soils: Soils commonly associated with this community are nearly level and very poorly drained with organic surfaces underlain by sand. Representative soils include Hontoon, Sanibel, and Okeelanta.

Vegetation: Within Florida, eight major different types of freshwater marshes have been described. Any one marsh may be composed of combinations of different major types. The types are: flag marshes, sawgrass marshes, arrowhead marshes, fire flag and other nongrass herbs marshes, cattail marsh, spike-rush marsh, bulrush marsh, and maidencane marsh. Plants that characterize this community may include: Beak rushes (Rhynchospora spp.), bulrushes (Scirpus spp.), maidencane (Panicum hemitomon), sawgrass (Cladium jamaicense), spike rushes (Eleocharis spp.), arrowhead (Sagittaria spp.), cattail (Typha spp.), pickerelweed (Pontederia cordata), and primrose willow (Ludwigia spp.).

Wildlife: Freshwater marshes and ponds provide excellent habitat for many wildlife species. Numerous birds and waterfowl use this community for over-wintering or year-round. Animals that commonly occur in this community are: river otters (Lutra

D-13 Appendix D Soil Classification Database canadensis), raccoon (Procyon lotor), marsh rabbits (Sylvilagus palustris), deer (Odocoileus virginianus), Florida water rat (Neofiber alleni), herons, egrets, bitterns, ibis, rails, limpkins (Aramus guarauna), snipes (Gallinago spp.), killdeer (Charadrius vociferus), ducks, hawks, frogs, turtles, and snakes. Some protected animal species that may be found in this ecological community include: Everglades mink (Mustela vison evergladensis), Key Vaca raccoon (Procyon lotor auspicatus, middle Florida Keys only), silver rice rat (Oryzomys agentatus), Cape Sable seaside sparrow (Ammodramus maritimus mirabilis), crested caracara (Polyborus plancus audubonii), Florida sandhill crane (Grus canadensis pratensis), snail kite (Rostrhamus sociabilis), wood stork (Mycteria americana), American alligator (Alligator mississippiensis), Florida ribbon snake (Thamnophis sauritis sackeni, Keys population only), and Keys mud turtle (Kinosternon bauri bauri, Keys population only).

Environmental Value as a Natural System: Freshwater marshes and ponds serve as filter systems for rivers and lakes. This protects these waterbodies from eutrophication and provides the marsh with nutrients that are used in vegetative growth. Marshes can reduce the impacts of drought and flooding. Fire and water level fluctuations are the major factors affecting these wetland areas. Variations in the water patterns on the marsh will change the plant diversity and productivity. Marsh-prairie systems will eventually move to a woody community with exclusion of fire or with permanent and lower water level changes. The freshwater marsh community is highly endangered. Many have been destroyed or at least degraded. Some examples of areas where drainage has occurred for reclamation of land and for agricultural interests are: The Everglades, Kissimmee River marshes, Lake Isotokpoga marsh, and the Upper St. Johns River marsh. Recreational uses of this community can cause much disturbance and may alter the plant community.

Rangeland: This ecological community has the potential for producing significant amounts of high-quality forage. For sites in excellent condition, the average annual production of air-dried plant materialvaries from 5,000 to 10,000 pounds per acre, depending on plant growth conditions. From three to more than thirteen acres are usually needed per animal unit depending upon amount and type of forages available. The relative percentage of annual vegetative production by weight is 80 percent grasses and grass-like plants, 5 percent trees and shrubs, and 15 percent herbs.

Woodland: This community is not generally recommended for woodland, unless drainage has been provided.

Urbanland: This community is subject to periodic flooding and has severe limitations for urban development. Intensive and complex water management systems are required for urban uses. It is often difficult to establish vegetation on steep channel side slopes and infertile spoil. Special techniques are usually required in these situations, such as mulching, special plants, and unusual management. Without vegetation, erosion and sedimentation can become a problem. Native plants can be used for beautification and require minimum establishment and maintenance. Some of the trees are: buttonbush (Cephalanthus occidentalis), coastal plain willow (Salix caroliniana), and persimmon (Diospiros virginiana). Some of the shrubs are elderberry (Sambucus canadense) and wax

D-14 Soil Classification Database Appendix D myrtle (Myrica cerifera). Some of the herbs are: golden canna (Canna flaccida), cardinal flower (Lobelia cardinalis), coneflowers (Rudbeckia spp.), marsh pink (Sabatia spp.), and meadow beauty (Rhexia spp.).

SLOUGH (ECOLOGICAL COMMUNITY NO. 26)

Range: The Slough ecological community occurs throughout central and southern Florida, but mostly in the latter. Individual communities vary widely in size. Most serve as drainage-ways between depressionsl soilsfor water during periods of heavy and prolonged rainfall. This slough community occurs in a slightly lower position adjacent to the South Florida Flatwoods ecological community (#6) and slightly higher positions adjacent to depressional communities.

Soils: Soils commonly associated with this community are nearly level and poorly drained with sandy marine sediments throughout the profile. Representative soils include Basinger, Malabar, and Riviera.

Vegetation: This community appears as an open expanse of grasses, sedges, and rushes with scattered pines and cypress in an area where the surface soil is saturated during the wet season. Surface water may move over this area for up to a few weeks during the rainy season. Most sloughs are relatively long and narrow and slightly lower in elevation than the surrounding flatwoods or hammocks. Grasses are the most common plants found in sloughs. Plants that characterize this community are: St. Peters wort (Ascyrum stans), pickerelweed (Pontederia cordata), sundew (Drosera spp.), marsh pink (Sabatia spp.), meadow beauty (Rhexia spp.), milkwort (Polygala spp.), beak rushes (Rhynchospora spp.), blue maidencane (Amphicarpum muhlenbergianum), and sloughgrass (Scleria spp.).

Wildlife: This community is productive in regards to food for bobwhite quail (Colinus virginianus), deer (Odocoileus virginianus), and wading birds. Its low-growing vegetative growth provides poor cover for most wildlife species, but this is often offset by the “edge effect” of this community when it is located with flatwoods. Sloughs are host to a diverse wildlife population. Many larger animals occur where sloughs join flatwoods and hammocks. Typical animals of the sloughs are: Bobcat (Lynx rufus), gray fox (Urocyon cinereoargenteus), marsh rabbit (Sylvilagus palustris), opossum (Didelphis virginiana), cotton rat (Sigmodon hispidus), raccoon (Procyon lotor), egrets, herons, ibis, meadowlark (Sturnella spp.), hawks, snipes (Gallinago spp.), snakes, and frogs. Some of the threatened or endangered animals include the Florida panther (Felis concolor coryi) and the Florida sandhill crane (Grus canadensis pratensis).

Environmental Value as a Natural System: Sloughs serve as natural drainageways during high water periods. They also retain water, help slow down water flows, and thereby increase water quantity and improve water quality. Fire and artificial water level fluctuations are the major factors affecting these areas. Variations in the natural sequences of either event will change the slough’s diversity and productivity. With

D-15 Appendix D Soil Classification Database the exclusion of fire or permanent water level reduction, the plant succession will be to a wooded community.

Rangeland: Native forage production is good with proper management. Use for rangeland has only a slight effect on the community if properly managed. The community has good wildlife values, especially with proper management. The installation of water control practices have facilitated the use of some sloughs for improved pasture, vegetables, and citrus. This ecological community has the potential for producing significant amounts of high quality forage such as: blue maidencane (Amphicarpum muhlenbergianum), chalky bluestem (Andropogon capillipes), and bluejoint panicum (Panicum tenerum). For sites in excellent condition, the average annual production of air- dried plant material varies from 4,000 to 8,000 pounds per acre. This variation depends on plant growth conditions. From three to more than 16 acres are usually needed per animal unit depending upon amount and type of forage available. The relative percentages of annual vegetative production by weight is 90 percent grasses and grass-like plants, 10 percent herbaceous plants.

Woodland: This community is not generally recommended for commercial woodland, unless drainage has been provided.

Urbanland: This community is subject to high water tables, especially during the rainy season. This causes limitations for urban development and water management systems are required. It is often difficult to establish vegetation on steep channel side slopes and infertile spoil. Special planting techniques are usually required. Without adequate vegetation, erosion and sedimentation is usually a problem. Severe wind erosion can also occur, especially in the spring. Native plants can be used for beautification and require minimum establishment and maintenance. Some of the shrubs are: saw palmetto (Serenoa repens) and wax myrtle (Myrica cerifera). Some of the herbs are: asters, coneflowers (Rudbeckia spp.), marsh pink (Sabatia spp.), and meadow beauty (Rhexia spp.).

D-16 Soil Classification Database Appendix E

Appendix E NATURAL SOIL LANDSCAPE POSITIONS CLASSIFICATION DATABASE

This database contains 35 soil data fields (1999 update). The data table contains fields from the SSURGO COMP table and the FOTG table, with one field added for the Natural Soil Landscape Position code. One notable change from the SSURGO COMP table is that only the Sequence Number 1 soils have been included in this table, since that component is most extensive and multiple per map unit are not user friendly. Within the table, an entry of "NA" (in text fields) or “-8” (in numeric fields) indicates that there is no data associated with this field for that entry ("not applicable"). An entry of "ND" (in text fields) or “-9” (in numeric fields) indicates that there is no data available for that entry, although there could be some available at a later update. The Soil Data Table elements are defined as follows.

MUID

This is the Map Unit Identification symbol, which uniquely identifies a map unit within a state. It is a six digit symbol derived from a concatenation of the three digit soil survey area symbol (SSAID) and the three digit map unit symbol (MUSYM). Thus the six digit code for Oldsmar sand (025 = soil survey code suffix for Oldsmar Sand) in Palm Beach County (611 = SSAID prefix code for Palm Beach County) is 611025. Note that some units may only have five digits. This occurs when a six-digit MUID, such as 061025, is truncated to 61025 when the first number is zero. A listing of three digit county codes used in SSURGO and in our Soil Classification Database is found in at the end of this section.

STSSAID

A concatenation of the alpha code for a state (FIPS) and the soil survey area symbol (SSAID).

MUSYM

This is the soil survey Map Unit Symbol. It is a three digit map unit code designated for each map unit name within a county.

CNTYABBR

This field contains a two-letter abbreviation for the county.

E-1 Appendix E Soil Classification Database

Table E-1. Three Digit Map Unit Symbols Used in the MUID.

Florida County Three Digit SSAID Symbol

Broward 716

Charlotte 015

Collier 021

Dade 025

De Soto 027

Glades 043

Hardee 049

Hendry 051

Highlands 055

Indian River 061

Lee 071

Martin 753

Monroe 087

Okeechobee 757

Orange 095

Osceola 610

Palm Beach 760

Polk 105

St. Lucie 766

LSPOS CODE

This is the NSLP position in which the MUID is found in Table E-2. Detailed descriptions of these categories can be found in the “Classification by NSLP Type” section of this document.

MAP UNIT NAME

This is the full name for the soil series which includes the soil series name(s), texture, percent slope, and phase (if noted).

S5ID 1

This is the Soil Interpretation Record Number for the Sequence Number 1 soil series found within the MUID. It is a six digit code and contains the two letter state code for the state responsible for the soil series phase (FL = Florida, GA = Georgia, etc) plus the four digit code for a particular soil (0059 = Myakka, flatwood). Thus the six digit code for Myakka is FL0059. The two letter state code is the same as used by the U.S. Postal Service for postal delivery.

E-2 Soil Classification Database Appendix E

Table E-2. LSPOS Codes.

LSPOS Code Description

1 Water

2 Tidal Soils

3 Marl & Rocky Soils

4 Everglades Peat

5 Muck Depressions

6 Sand Depressions

7 Flats Soils

8 Flatwood Soils

9 Knolls

10 Central Ridge & Dunes

11 Urban or Made Lands

12 No Data

COMPPCT 1

This field contains the percent of area of the Sequence Number 1 (first) soil series within the MUID.

SURFTEXT 1

This field contains the surface soil texture code for the Sequence Number 1 (first) soil series found within the map unit (Table E-3).

SHWT-HIGH

This is the high value for the average range of the depth to the seasonal high water table. Units are in feet. Negative values indicate a water table above the soil surface.

SHWT-LOW

This is the low value for the average range of the depth to the seasonal high water table. Units are in feet. Negative values indicate a water table above the soil surface.

SHWT-BEG

This is the average month in which the seasonal high water table begins.

SHWT-END

This is the average month in which the seasonal high water table ends.

E-3 Appendix E Soil Classification Database

Table E-3. Surface Soil Texture Codes.

Surface Soil Texture Code Description

Cclay

FS fine sand

FSL fine sany loam

GR-MUCK gravelly muck

GRV-L very gravelly loam

LFS loamy fine sand

LS loamy sand

MARL marl

MUCK muck

MK-FS mucky fine sand

MK-LFS mucky loamy fine sand

MK-S mucky sand

ROCK rock

S sand

SCL sandy clay loam

SICL silty clay loam

SIL silt loam

SHWT-DUR

This is the duration of the SHWT in months.

HYDRIC

This indicates if a MAP UNIT NAME is defined as a Hydric soil. If the MAP UNIT NAME is hydric the entry is "Y". If the MAP UNIT NAME is not hydric the entry is "N".

HYDROGRP

This is the Hydrologic Group for a particular MAP UNIT NAME. Table E-4 contains the codes used with a general description of the soil conditions associated with them.

DRAINAGE

This is the soil drainage class code, which identifies natural drainage condition of the soil. The code refers to the frequency and duration of periods when the soil is free of saturation (Table E-5).

E-4 Soil Classification Database Appendix E

Table E-4. Hydrological Group Codes.

Hydrological Group Code Description

High infiltration rates. Soils are deep, well drained to excessively drained sands and A gravels

Moderate infiltration rates. Deep and moderately deep, moderately well and well B drained soils that have moderatly coarse textures

Slow infiltration rates. Soils with layers impeding downward movement of water, or C soils that have moderately fine or fine textures

Very slow infiltration rates. Soils are clayey, have a high water table, or are shallow to D an impervious layer

Table E-5. Soil Drainage Class Codes.

Soil Drainage Class Code Description

E excessively

SE somewhat excessively

Wwell

MW moderately well

SP somewhat poorly

P poorly

VP very poorly

ECOLCOMM

This indicates the Ecological Community code of a MAP UNIT NAME. These codes correspond to the ecological communities as defined by the Soil Conservation Society's document “The 26 Ecological Communities of Florida”.

MLRA

This is the Major Land Resource Area. It is a three digit numeric code or four digit numeric and alpha code that indicates the Major Land Resource Area code of a MAP UNIT NAME. MLRAs are areas that have similar land use, topography, climate, precipitation, and soils.

MUKIND

This is the code identifying the kind of map unit, for example: Consociation (C); Association (A); Undifferentiated Group (U); Complex (X).

E-5 Appendix E Soil Classification Database

ANFLOOD FREQ

Descriptive term used to describe the frequency of annual flooding (flooding likely to occur during the year) that is likely to occur. Frequent (FREQ) ->50% chance of flooding; Occasional (OCCAS) - 5 to 50% chance of flooding; Rare (RARE) - 0 to 5% chance of flooding.

ANFLOOD BEG

Month in which the annual flooding (flooding likely to occur during the year) begins in a normal year.

ANFLOOD END

Month in which the annual flooding (flooding likely to occur during the year) ends in a normal year.

ROCKDEPTH HIGH

The maximum value for the range in depth to the bedrock, expressed in inches.

ROCKDEPTH LOW

The maximum value for the range in depth to the bedrock, expressed in inches.

SLOPE LOW

This is the lower end of the slope range for a MAP UNIT NAME. It is a one or two digit numeric value expressed in percent. A difference in elevation of one foot over a horizontal distance of one hundred feet is one percent. Additional Information can be found in the National Soils Handbook.

SLOPE HIGH

This is the upper end of the slope range for a MAP UNIT NAME. It is a one or two digit numeric value expressed in percent. A difference in elevation of five feet over a horizontal distance of one hundred feet is five percent.

PANDEPTHHIGH

Maximum value for the range in depth to the upper boundary of a cemented pan, expressed in inches.

E-6 Soil Classification Database Appendix E

PANDEPTHLOW

Minimum value for the range in depth to the upper boundary of a cemented pan, expressed in inches.

PANHARD

The degree of induration and thickness of the cemented pan. A pan is rated as "THICK" if it is more than 3 inches thick and continually indurated or more than 18 inches thick and discontinuous or fractured. Pans not meeting these criteria are rated THIN.

OTHERPH

This is Soil Series Phase Criteria that is used in conjunction with the Soil Interpretation Record (S5ID) to provide the correct interpretations for a particular MAP UNIT NAME. Additional Information concerning OTHERPH is in the National Soils Handbook.

LEACH

This indicates the potential of a MAP UNIT NAME to allow chemicals to leave the application site by leaching through the soil. Possible entries are LOW, MEDIUM, or HIGH. Additional information concerning soileach and other types of Water Quality Interpretations is in Section II-iii-L of the FOTG.

RUNOFF

This indicates the potential of a MAP UNIT NAME to allow chemicals to leave the application site with runoff water and/or detached soil particles. Possible entries are LOW, MEDIUM, or HIGH. Additional information concerning soilrun and other types of Water Quality Interpretations is in Section II-iii-L of the FOTG.

CORCON

An interpretation of the rating of the susceptibility of concrete to corrosion when in contact with the soil.

CORSTEEL

An interpretation of the rating of the susceptibility of uncoated steel to corrosion when in contact with the soil.

E-7 Appendix E Soil Classification Database

E-8 Soil Classification Database Appendix E 15008 FL015 8 ch 2 FINE HALLANDALE SAND, TIDAL FL0389 95 FS 0.0 0.5 JAN DEC 12 Y D P 18 155 S FREQ JAN DEC 20 7 0 2 -9 -9 NA NA MED HIGH MED HIGH 15007 FL015 7 ch 11 -URBAN MATLACHA COMPLEX LAND FL0386 60 GR-FS 2.0 3.0 JUN OCT 5 N NA SP NA 155 C NONE NA NA -8 -8 0 2 -9 -9 NA NA MED MED LOW HIGH 15006 FL015 6 ch 8 HALLANDALE SAND FINE FL0065 95 FS 0.5 1.5 JUN SEP 4 N D P 6 155 S NONE NA NA 20 7 0 2 -9 -9 NA NA MED HIGH LOW HIGH 15005 FL015 5 ch 7 FINECAPTIVA SAND FL0273 95 FS 0.0 0.5 JUN OCT 5 Y D P 26 155 S NONE NA NA -8 -8 0 1 -9 -9 NA NA HIGH HIGH LOW LOW 15004 FL015 4 ch 11 - URBAN CANAVERAL LAND COMPLEX FL0060 70 FS 1.5 3.5 JUN NOV 6 N NA SP 2 155 C NONE NA NA -8 -8 0 2 -9 -9 NA NA HIGH MED LOW MED 15002 FL015 2 ch 9 CANAVERAL SAND FINE FL0060 95 FS 1.5 3.5 JUN NOV 6 N C SP 2 155 S NONE NA NA -8 -8 0 2 -9 -9 NA NA HIGH MED LOW MED MUID STSSAID MUSYM CNTYABBR LSPOSCODE MAPUNIT NAME 1 S5ID COMPPCT 1 1 SURFTEXT HIGH SHWT LOW SHWT BEG SHWT END SHWT DUR SHWT HYDRIC HYDROGRP DRAINAGE ECOLCOMM MLRA MUKIND ANFLOOD FREQ ANFLOOD BEG ANFLOOD END HIGHROCKDEPTH LOW ROCKDEPTH SLOPE LOW HIGHSLOPE LOW PANDEPTH HIGH PANDEPTH PANHARD OTHERPH LEACH RUNOFF CORCON CORSTEEL

E-9 Appendix E Soil Classification Database PECKISH MUCKY PECKISH MUCKY FINE SAND ESTERO MUCK VALKARIA VALKARIA FINE SAND BOCA FINE SAND FELDA FINE FELDA SAND MYAKKA MYAKKA SAND FINE POMPANO POMPANO SAND FINE SAND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL015 15009 ch EAUGALLIE 8 9 FL015 15010 ch 7 10 FL015 15011 FL015 ch 15012 11 8 FL015 15013 ch 12 7 FL015 15014 ch FL015 13 15015 8 FL015 15016 ch 14 7 ch 15 2 ch 16 2 COMPPCT 19595959595959595 LOW-9-9-9-9-9-9-9-9 ENDNANANANANANADECDEC DUR4549941212 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG ENDSHWT SSHWT FL0154 0.5HYDRIC 1.5HYDROGRPDRAINAGEPPPPPPVPVP JUNECOLCOMM6266266261819 SEP FL0032MLRA FSMUKINDSSSSSSSS D 0.0ANFLOOD FREQ N 1.0ANFLOOD BEG FL0059 JUNANFLOOD OCT NONE HIGHROCKDEPTH LOWROCKDEPTH NA FL0127 -8SLOPE LOW FS 155 0.5 HIGHSLOPE -8 D 1.5 YPANDEPTH JUN NONE SEP HIGHPANDEPTH FL0054PANHARD 0OTHERPHNANANANANANANANA FS NA 2 -9 0.0LEACH 155 -8 JUL 1.0RUNOFF NONE MAR FL0126 -8 DCORCON NCORSTEEL NA FL0301 NONE FS NA 0 0.5 155 -9 JUN 2 FEB FL0272 -8 1.5 LOW HIGH D -8 MED HIGH Y NONE NA NA 155 FS JUN 0.0 SEP -8 0 1.0 HIGH HIGH -9 2 HIGH MED -8 NONE D N NA JAN MUCK DEC 0.0 NA 155 FREQ 0.5 MED HIGH 0 -9 HIGH MK-FS 40 HIGH 2 JAN DEC 24 FREQ D 0.0 NA Y 0.5 HIGH MED 155 NA HIGH MED -8 -9 0 2 -8 D HIGH 155 NA Y LOW JAN HIGH MED -8 155 -9 D JAN HIGH 0 -8 Y HIGH HIGH 2 NA MED -8 HIGH LOW -8 HIGH -9 0 HIGH NA 1 HIGH HIGH HIGH HIGH -9 NA 0 1

E-10 Soil Classification Database Appendix E KESSON FINE SAND MUCK BEACHES WULFERT MUCK GATOR MUCKGATOR TERRA CEIA MATLACHA GRAVELLY FINE SAND, FINE SAND, GRAVELLY MATLACHA SUBSTRATUM LIMESTONE SAND S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT S DURSHWT FL0230 2.0HYDRIC 3.5HYDROGRP FL0387DRAINAGE JUL 95ECOLCOMM NOV GR-FSMLRA 1.5 5MUKIND 2.5 BANFLOOD FREQ JUN N OCTANFLOOD BEG MW 3ANFLOOD END NONE HIGHROCKDEPTH 5 LOWROCKDEPTH NA NA -8SLOPE LOW SP N S 155 NA NONE HIGHSLOPE -8 NA LOWPANDEPTH HIGHPANDEPTH NAPANHARD FL0415 155 60 0 NA -9OTHERPH S 5 -9 40LEACH MUCKRUNOFF 95CORCON -2.0CORSTEEL FL0031 -9 NA 0 0.0 JUN -9 2 NA APR MUCK LOW DC0002 LOW 95 NA HIGH MED 11 -2.0 NA NONE D FL0276 VP S JUN 0.0 LOW APR Y MED LOW 25 HIGH FL0274 NA 155 95 NONE NA 0.0 -8 MUCK 11 S JAN -8 DEC 6.0 VP D Y 25 FS 95 FREQ 0.0 -9 JAN DEC NA 155 0 -9 0.5 NA 1 -8 12 FREQ P -8 S D NA 0.0 95 DEC JAN NA Y UNDRAINED LOW 0.5 HIGH FREQ 155 JAN 12 HIGH HIGH -9 DEC UNDRAINED 0 -9 VP -8 D 1 18 NA -8 M Y JAN 155 NA DEC LOW HIGH 12 MED MED VP -8 -9 NA D -9 18 -8 1 JAN S 155 2 DEC Y NA HIGH HIGH HIGH HIGH -9 -8 NA -9 0 -8 HIGH LOW S 1 HIGH NA HIGH -9 HIGH LOW -9 LOW HIGH 0 NA 1 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL015 15017 ch DAYTONA 9 17 FL015 15018 ch 18 11 FL015 15019 ch 19 5 FL015 15020 FL015 15022 ch 20 5 FL015 15023 FL015 ch 15024 22 2 ch 23 2 ch 24 2

E-11 Appendix E Soil Classification Database OLDSMAR SAND PUNTA PUNTA FINE SAND IMMOKALEE IMMOKALEE SAND POMPANO FINE SAND, FINE POMPANO DEPRESSIONAL PINEDA SAND FINE SUBTR. - URBAN LAND COMPLEXSUBTR. COMPPCT 160 959595 9595 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG ENDSHWT S DURSHWT FL0321 2.0HYDRIC 4.0HYDROGRPDRAINAGE JULECOLCOMM OCTMLRA 4MUKIND NAANFLOOD FREQ NANFLOOD BEG SP NAANFLOOD END RARE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C 155 NA HIGHSLOPE -8 LOWPANDEPTH HIGH FL0080PANDEPTH PANHARD 0 FS -9OTHERPH 2 0.0 -9LEACH FL0285 1.0RUNOFF JUNCORCON NOVCORSTEEL NA FS -2.0 6 NA D 0.0 JUN MAR Y P HIGH LOW NONE 26 HIGH HIGH FL0058 NA 10 NONE 155 -8 D NA S -8 Y 25 VP FL0393 S NA 0.5 155 -9 NA 0 -8 JUN FL0067 1.5 SEP -9 2 S -8 NA NONE 0.5 NA -9 FS 4 0 JUN SEP -9 1.5 2 D LOW HIGH P LOW HIGH 6 N NONE NA NA 0.5 NA JUN SEP 155 S MED HIGH NA 1.5 HIGH MED -8 4 NONE S -8 D P 6 N NA 155 -9 NA 0 -9 4 -8 2 D -8 S P N 6 NA 155 NA HIGH MED NA HIGH NA HIGH -9 -8 -9 0 -8 2 S HIGH NA MED HIGH HIGH NA -9 -9 0 HIGH LOW MED 2 HIGH NA NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL015 15025ORGANIC AUGUSTINE SAND, ch ST. 11 25 FL015 15026 ch 7 26 FL015 15027 ch 27 6 FL015 15028 FL015 15029 ch 28 8 FL015 15033 ch 29 8 ch 33 8

E-12 Soil Classification Database Appendix E ANCLOTE SAND, ANCLOTE SAND, DEPRESSIONAL ISLES FINE SAND, FINE SAND, ISLES DEPRESSIONAL ISLES FINE ISLES SAND, SLOUGH SATELLITE SATELLITE SAND FINE IMMOKALEE - URBAN IMMOKALEE LAND COMPLEX WABASS O SAND FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0123 0.0HYDRIC 1.0HYDROGRPDRAINAGE FL0075 JUN 95ECOLCOMM NOV SMLRA 6 0.5 FL0058MUKIND 1.5 DANFLOOD FREQ JUN YANFLOOD BEG SEP P 70 26ANFLOOD END S 0.5 NONE HIGHROCKDEPTH 4 1.5 LOWROCKDEPTH JUN NA -8 SEPSLOPE LOW D S 155 NA N -8 HIGHSLOPE NONE FL0102 P 6 LOWPANDEPTH HIGHPANDEPTH 4PANHARD NA NONE FL0395 0 -9 155 NA -8OTHERPH NA 2 -9 N SLEACH -8 95 P 6RUNOFF 1.5 FSCORCON NA JUN 3.5 155CORSTEEL NOV NA NA -8 FL0396 -9 0 NA C -9 2 -8 95 0.0 FS NONE JUN LOW HIGH OCT 1.0 LOW HIGH 6 NA -9 C 0 NA -9 2 NONE N FL0315 LOW HIGH SP 3 MED HIGH NA NA 155 95 NA JUN -2.0 NA 5 MAR FS -8 D HIGH MED 0.0 S HIGH -8 HIGH Y P NONE 26 NA 155 NA -9 72 0 -9 40 2 S 95 JUN MAR 10 -2.0 D S NA NONE 0.0 LOW Y NA HIGH VP 155 MED 25 NA -9 LOW -9 NA 0 1 72 HIGH NA MED 40 LOW NA HIGH S 10 D -9 VP 155 Y -9 NA 25 0 HIGH MED NA 1 NA HIGH LOW -8 NA -8 S HIGH -9 HIGH -9 HIGH MED 0 NA 2 NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL015 15034 ch MALABAR 7 34 FL015 15035 ch FL015 35 8 15036 ch 36 11 FL015 15037 FL015 15038 ch 37 9 FL015 15039 ch 38 7 FL015 15040 ch 39 6 ch 40 6

E-13 Appendix E Soil Classification Database COPELAND SANDY DEPRESSIONAL LOAM, MALABAR FINE SAND, FINE MALABAR DEPRESSIONAL SMYRNA SMYRNA SAND FINE WABASSO SAND, WABASSO SUBSTR. LIMESTONE DEPRESSIONAL MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL015 15041FINE SAND, ch VALKARIA 6 41 FL015 15042 ch 42 8 FL015 15043 FL015 ch 43 15044 8 ch 44 6 FL015 15045 ch 45 6 COMPPCT 19595959595 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG ENDSHWT FS DURSHWT FL0267 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKINDSSSSS DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END FL0419 NONE HIGHROCKDEPTH S LOWROCKDEPTH NA 0.5 -8SLOPE LOW 155 NA 1.5 HIGHSLOPE -8 JUN LOWPANDEPTH SEP HIGHPANDEPTH PANHARD 4 0 -9OTHERPH 2 -9LEACH D FL0091RUNOFF N P NONE 6CORCONCORSTEEL NA FL0286 FS NA 0.5 NA 155 80 NA 1.5 JUN 40 SEP HIGH HIGH MED HIGH FS -2.0 4 -9 0 -9 JUN 2 NONE 0.0 MAR D N FL0265 P 6 NA NONE NA NA 155 10 NA -8 LOW HIGH -8 D MED MED Y VP 25 -2.0 LS NA 155 JUN MAR -9 0.0 NA 0 -8 -9 2 -8 NONE NA NA 10 HIGH MED -9 0 -9 HIGH HIGH D 2 VP Y 21 NA 155 NA HIGH LOW NA NA HIGH LOW 50 20 -9 -9 0 1 HIGH NA MED HIGH NA LOW

E-14 Soil Classification Database Appendix E MYAKKA FINE SAND, MYAKKA DEPRESSIONAL FLORIDANA SAND, FLORIDANA DEPRESSIONAL OLDSMAR FINE SAND, OLDSMAR FINE SAND, SUBSTR. LIMESTONE FELDA FINE SAND, SAND, FINE FELDA DEPRESSIONAL SAND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL015 15048 AUGUSTINE ch ST. 9 48 FL015 15049 ch 49 6 FL015 15050 ch 50 8 FL015 15051 ch 51 6 FL015 15053 ch 53 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT S DURSHWT FL0320 2.0HYDRIC 3.0HYDROGRPDRAINAGE JULECOLCOMM OCTMLRA 4MUKIND FL0298 CANFLOOD FREQ 95 NANFLOOD BEG FS SP NAANFLOOD END -2.0 RARE HIGHROCKDEPTH 1.0 JUN LOWROCKDEPTH NA DEC -8SLOPE LOW S 155 NA HIGHSLOPE -8 LOW 7PANDEPTH FL0391 HIGHPANDEPTH DPANHARD Y VP 0 -9 NONE 95 25OTHERPH 2 -9 FSLEACH 0.5RUNOFF 1.5 NA JUNCORCON 155 -8 SEP NACORSTEEL S NA -8 NA FL0262 4 NONE HIGH MED -9 D 0 HIGH P HIGH -9 N 2 6 95 NA FS 155 -2.0 NA NA 72 NA JUN 0.0 MAR S FL0307 40 MED HIGH HIGH HIGH NONE -9 0 -9 10 2 D VP 95 Y 25 FS -2.0 NA JUN MAR NA 0.0 NA 155 LOW HIGH NA LOW HIGH -8 NONE -8 S 10 -9 VP D 0 -9 25 Y 2 155 NA NA NA LOW HIGH NA -8 MED LOW -8 S -9 -9 0 2 HIGH NA MED HIGH HIGH NA

E-15 Appendix E Soil Classification Database MALABAR FINE FINE MALABAR SAND, HIGH WINDER SAND, SAND, WINDER DEPRESSIONAL ORSINO FINE SAND URBAN LAND SAND, TIDAL ISLES MUCKISLES BOCA FINE SAND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL015 15055 ch FINE COCOA 9 55 FL015 15056 ch 56 2 FL015 15057 ch 57 2 FL015 15059 FL015 15061 ch 59 11 FL015 15062 ch 61 9 FL015 15063 ch 62 6 ch 63 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0061 5.0HYDRIC 6.0HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4 FL0394MUKIND 95 MUCK AANFLOOD FREQ N 0.0ANFLOOD BEG W 4ANFLOOD END 0.5 FL0384 JAN NONE HIGHROCKDEPTH DEC FS LOWROCKDEPTH NA 40 95SLOPE LOW S 155 NA 12 HIGHSLOPE 20 0.0 LOWPANDEPTH D 0.5 HIGH JAN DC0035PANDEPTH Y FREQ VP DECPANHARD 18 0 -9OTHERPH 2 -9LEACH FL0103 VAR JAN 12RUNOFF 72 155 DEC 95CORCON FREQ S 40 DCORSTEEL 2.0 P Y NA NA 2.0 FL0283 18 NA NA FS JAN -9 0 DEC 155 HIGH -9 40 95 LOW 1 LOW LOW 3.5 24 NONE S -9 JUN 5.0 DEC FL0390 NA NA S NA NA N NONE NA -9 NA 0 MED -9 95 NA HIGH 1 155 7 -2.0 HIGH HIGH JUN -8 MAR 0.0 A -8 NA M MW NONE 3 NA N LOW NA HIGH NA 155 HIGH HIGH FS -9 -8 10 0 -9 -8 95 0.5 2 JUN S SEP VP D 1.5 NONE NA Y NA 25 155 NA MED HIGH NA ND ND -9 -9 -8 0 5 -8 LOW NA S HIGH 4 NA P MED LOW D NA 155 6 -9 NA N -9 0 HIGH LOW 2 NA -8 LOW HIGH NA -8 S -9 HIGH LOW -9 0 HIGH NA LOW 2 NA

E-16 Soil Classification Database Appendix E BRADENTON BRADENTON FINE SAND HEIGHTS FINE SAND MATLACHA MATLACHA FINE SAND GRAVELLY SMYRNA - URBAN SMYRNA COMPLEX LAND CALOOSA SAND FINE LAND COMPLEX S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 70 ENDSHWT FS DURSHWT FL0065 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4MUKIND NAANFLOOD FREQ NANFLOOD BEG P NAANFLOOD END FL0420 NONE HIGHROCKDEPTH 95 FS LOWROCKDEPTH NA 20SLOPE LOW 2.5 C 155 NA HIGHSLOPE 7 FL0091 3.5 LOWPANDEPTH JUL HIGHPANDEPTH OCT 65PANHARD FS 0 -9OTHERPH 4 2 0.5 -9LEACH NA 1.5RUNOFF JUN N SEP NONECORCON NA FL0386 MWCORSTEEL NA NA NA 4 -8 NA 155 NA NONE S 95 MED GR-FS HIGH -8 P 6 N LOW HIGH 2.0 JUN 3.0 OCT NA -9 155 0 FL0365 NA -8 -9 2 C -8 NONE NA FL0232 5 NA NA FS -9 SP N NA 0 -9 LOW MED 95 2 HIGH HIGH 0.5 NA 155 JUN SEP 1.5 NA NA -8 NA FS S -8 MED HIGH NONE HIGH HIGH 95 0.5 JUN SEP D 1.5 -9 4 0 -9 NONE 2 P 6 N NA 155 NA MED NA MED NA HIGH LOW D -8 4 S -8 P 8 N 155 NA NA -9 -8 -9 0 1 S -8 NA HIGH LOW HIGH LOW NA -9 -9 0 HIGH LOW HIGH 2 NA LOW NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL015 15064 chURBAN HALLANDALE - 11 64 FL015 15066 ch 11 66 FL015 15067 ch 11 67 FL015 15069 ch 11 69 FL015 15070 FL015 15072 ch 8 70 ch 72 8

E-17 Appendix E Soil Classification Database CHOBEE MUCK PINEDA FINE SAND, PINEDA FINE SUBSTR. LIMESTONE ELECTRA ELECTRA SAND FINE HALLANDALE FINE HALLANDALE FINE SAND, SLOUGH BOCA FINE SAND, BOCA FINE SLOUGH DEPRESSIONAL S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0411 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP FL0383 25ANFLOOD END 95 FS NONE HIGHROCKDEPTH 0.0 LOWROCKDEPTH NA -8SLOPE LOW 1.0 S 155 NA JUN HIGHSLOPE -8 OCT LOWPANDEPTH FL0388 HIGHPANDEPTH 5PANHARD 0 -9OTHERPH 95 1 D -9 FSLEACH Y P 0.0 NONERUNOFF 26 1.0CORCON JUN OCTCORSTEEL NA NA 155 FL0010 40 NA NA S 24 5 LOW NONE HIGH FL0414 D LOW HIGH Y P 95 26 FS -9 0 -9 2.0 1 JUL NA 3.5 OCT 155 NA 20 S 7 NA 95 FS NA 0.0 NONE JUN NOV LOW FL0412 HIGH 4 1.0 HIGH MED -9 0 C -9 1 N 6 NONE SP NA 155 NA NA 6 -8 NA HIGH HIGH D S HIGH -8 P LOW Y 26 MUCK 95 155 -2.0 MAR NA JUN NA 0.0 -9 80 NONE 0 -9 2 40 S NA MED LOW NA LOW -9 HIGH 10 -9 0 D 1 VP 25 Y HIGH NA LOW 155 NA HIGH NA LOW NA -8 -8 S -9 -9 0 HIGH LOW 1 HIGH NA HIGH NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL015 15073 chFINE SAND, PINEDA 6 73 FL015 15074 ch 74 7 FL015 15075 ch 75 7 FL015 15076 FL015 15077 ch 76 9 ch 77 FL015 7 15078 ch 78 5

E-18 Soil Classification Database Appendix E CHOBEE, LIMESTONE SUBSTR. AND CHOBEE, LIMESTONE DEPRESSIONAL DANIA MUCKS, FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL015 15099 ch WATER 1 99 FL021 SUBSTR.LIMESTONE FINE SAND, HOLOPAW 21002 co 2 MALABAR 7 FL021 21003 FL021 co 21004 3 7 co 4 5 S5ID 1S5ID 1COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 100 ENDSHWT NA DURSHWT DC0038 -9HYDRIC FL0453 95 -9HYDROGRP FSDRAINAGE NAECOLCOMM NA 0.0MLRA -9 1.0MUKIND JUN NAANFLOOD FREQ NOV NAANFLOOD BEG NA NA 6ANFLOOD END NA HIGHROCKDEPTH D Y LOWROCKDEPTH NA P -9 26SLOPE LOW M NA NA HIGHSLOPE -9 NONE LOWPANDEPTH NA HIGHPANDEPTH 80 155 NAPANHARD S -9 50 -9OTHERPH -9 -9LEACHRUNOFFCORCON 0 -9 FL0123CORSTEEL 2 -9 NA NA 95 FL0450 FS NA NA NA 0.0 NA NA NA 1.0 JUN NOV LOW 55 HIGH MUCK MED HIGH -2.0 6 JUN D 1.0 MAR Y NONE P 26 NA 10 NONE 155 NA -8 D S -8 Y 25 VP NA 155 NA -9 0 60 -9 2 8 U NA NA -9 0 -9 LOW HIGH 1 HIGH LOW NA NA HIGH LOW HIGH LOW

E-19 Appendix E Soil Classification Database HALLANDALE FINE FINE HALLANDALE SAND OLDSMAR FINE SAND, OLDSMAR FINE SAND, SUBSTR. LIMESTONE MYAKKA MYAKKA SAND FINE IMMOKALEE IMMOKALEE SAND FINE COPELAND FINE SAND COPELAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL021 21006SUBSTR. - LIMESTONE co RIVIERA, 7 6 FL021 21007 co 8 7 FL021 21008 FL021 co 21010 8 8 co 8 10 FL021 21011 co 11 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 65 ENDSHWT FS DURSHWT FL0421 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND DANFLOOD FREQ YANFLOOD BEG P 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA 70SLOPE LOW C 155 NA HIGHSLOPE 20 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 -9OTHERPH FL0058 2 -9 95LEACH FSRUNOFF 0.5CORCON 1.5CORSTEEL FL0059 NA JUN SEP NA 95 FS FL0391 4 LOW HIGH 0.5 MED HIGH D 1.5 JUN N NONE SEP 6 P 95 FS NA 0.5 -8 155 4 NA JUN 1.5 S NONE SEP -8 D FL0065 N P 6 NONE -9 NA 0 155 -9 4 2 NA -8 D S -8 N P 95 6 FS NA NA 0.5 NA 156A JUN SEP NA 1.5 -9 72 0 MED HIGH -9 2 40 HIGH S HIGH NONE NA NA -9 HIGH MED 4 0 -9 HIGH HIGH 2 D N P NA 155 6 NA HIGH NA MED NA HIGH LOW 20 7 S -9 -9 0 2 HIGH NA MED HIGH LOW NA

E-20 Soil Classification Database Appendix E FT. DRUM AND MALABAR, AND MALABAR, DRUM FT. SANDS HIGH, FINE RIVIERA FINE SAND, SUBSTR. LIMESTONE BASINGER SAND FINE OLDSMAR SAND FINE POMELLA POMELLA SAND FINE LIMESTONE SUBSTR. LIMESTONE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL021 21014 coFINE SAND, PINEDA 7 14 FL021 21015 co 15 9 FL021 21016 FL021 co 21017 16 8 FL021 21018 co 17 7 co 18 FL021 21020 7 co 20 8 UID SSSS U 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0414 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM266626268 NOVMLRA 6MUKINDS DANFLOOD FREQ YANFLOOD BEG P FL0078ANFLOOD END 95 NONE FS HIGHROCKDEPTH LOWROCKDEPTH 2.0 NA 80 FL0067SLOPE LOW 3.5 NA 156A HIGHSLOPE 40 JUL NOV LOWPANDEPTH 95 HIGH FSPANDEPTH FL0063PANHARD 0.5 5 0 -9OTHERPH 1.5 1 -9 JUN CLEACH SEP FL0421 N NONERUNOFF MW 95CORCON FSCORSTEEL 0.0 NA NA 4 155 JUN 1.0 -8 NA NONE FEB NA D -8 P N LOW 95 HIGH FS LOW HIGH 0.0 NONE FL0225 JUN 155 NA NOV 1.0 -9 9 0 NA -8 -9 2 D -8 P Y NONE 155 NA NA NA NA -9 -8 6 0 -9 2 MED -8 MED D P FS Y 55 LOW HIGH 0.5 JUN 156A SEP NA NA 1.5 NA NA -9 NONE LOW HIGH 70 0 -9 HIGH MED 2 40 NA HIGH NA HIGH MED HIGH -9 4 -9 0 C 156A 2 P N HIGH NA NA LOW MED NA NA HIGH -8 -8 -9 -9 0 HIGH MED 2 NA HIGH LOW NA

E-21 Appendix E Soil Classification Database HOLOPAW AND OKEELANTA SOILS, AND OKEELANTA HOLOPAW DEPRESSIONAL CHOBEE, WINDER AND GATOR SOILS, SOILS, AND GATOR CHOBEE, WINDER DEPRESSIONAL FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT ENDSHWT DURSHWT HYDRIC 95 FSHYDROGRP FL0054DRAINAGE 0.5ECOLCOMM 1.5MLRA JUNMUKIND FEBANFLOOD FREQ 9ANFLOOD BEG FL0412ANFLOOD END 40 D FSL N HIGHROCKDEPTH P -2.0 6 LOWROCKDEPTH SLOPE LOW 1.0 NONE JUN HIGHSLOPE MAR NA LOWPANDEPTH 40 S 155 NA HIGHPANDEPTH 24 10PANHARDOTHERPH DLEACH Y NONE VPRUNOFF 0 -9 25 2 -9CORCONCORSTEEL NA -8 155 NA U -8 NA NA -9 MED 0 HIGH FL0264 -9 1 MED HIGH FS 75 NA -2.0 NA 0.0 JUN MAR LOW HIGH HIGH HIGH 10 NONE D Y VP 25 NA 155 NA -8 U -8 -9 0 -9 1 NA NA HIGH LOW HIGH MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL021 21021 co BOCA 8 21 FL021 21022 co 22 6 FL021 21023 co 23 6

E-22 Soil Classification Database Appendix E WABASSO WABASSO FINE SAND PINEDA AND RIVIERA PINEDA AND RIVIERA SAND FINE HOLOPAW HOLOPAW SAND FINE COPELAND FINE SAND, DEPRESSIONAL COPELAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL021 21025SUBSTR. AND LIMESTONE co BOCA, RIVIERA, 6 25 FL021 21027 co 27 7 FL021 21028 co 28 7 FL021 21029 co 29 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 40 ENDSHWT FS DURSHWT FL0268 -2.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM FEBMLRA 9MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA 70SLOPE LOW U 155 NA HIGHSLOPE 20 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 -9OTHERPH 1 -9LEACH FL0027RUNOFF 95CORCON FS 0.0CORSTEEL NA FL0080 1.0 NA JUN NOV 55 MED FS HIGH MED 0.0 HIGH 6 1.0 JUN D NOV Y P NONE 26 FL0075 NA 6 -8 NONE 155 NA D S -8 Y P 26 95 FS 0.5 NA JUN 155 1.5 -9 0 NA SEP -8 -9 2 U -8 NONE NA NA 4 -9 0 -9 D 2 LOW HIGH 6 N P HIGH MED NA NA 155 NA NA -8 HIGH LOW HIGH -8 LOW S -9 0 -9 2 NA HIGH NA LOW MED HIGH

E-23 Appendix E Soil Classification Database URBAN LAND - HOLOPAW - - HOLOPAW URBAN LAND BASINGER COMPLEX 32co11 33 LAND co 11 95VAR2.02.0 45 NA VAR NA 2.0 -9 2.0 NN NA NA NA NA -9 NA NA MC NA NA NANA-8-8 NA 00 NA 22 -8 -9 -8 -9NANA -9 HIGH -9 NA NA HIGH CNTYABBRLSPOSCODE NAMEMAPUNIT SOILS AND MARGATE JUPITER SUBSTR., LIMESTONE co HILOLO 7 URBAN MUIDSTSSAIDMUSYM FL021 21031 31 FL021 21032 FL021 21033 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 40 ENDSHWT FS DURSHWT FL0543 0.0 HYDRIC 1.0 HYDROGRPDRAINAGE JUN ECOLCOMM NOV MLRA 6 MUKIND D ANFLOOD FREQ Y ANFLOOD BEG P 11 ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA 70 SLOPE LOW U 156A NA HIGHSLOPE 8 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 -9 OTHERPH 2 -9 LEACHRUNOFFCORCONCORSTEEL NA NA MED HIGH LOW HIGH DC0035 DC0035 NONE NONE 155 155 HIGH ND ND HIGH ND ND

E-24 Soil Classification Database Appendix E TUSCAWILLA TUSCAWILLA FINE SAND UDORTHENTS UDORTHENTS SHAPED URBAN LAND - AQUENTS COMPLEX, ORGANIC SUBSTR. LIMESTONE SUBSTR., COMPLEX SUBSTR., LIMESTONE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL021 21034 co - OLDSMAR,- IMMOKALEE URBAN LAND 11 34 FL021 21035 co 11 35 FL021 21036 co 11 36 FL021 21037 co 8 37 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 45 ENDSHWT VAR DURSHWT DC0035 2.0HYDRIC 2.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND NAANFLOOD FREQ NANFLOOD BEG NA NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C 155 NA HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 -9OTHERPH 2 -9LEACHRUNOFF FL0392CORCON VAR 60CORSTEEL NA 0.5 NA 1.5 NA HIGH HIGH NA ND ND -9 NA N NA NONE NA NA FL0089 155 -8 NA M -8 CB-S 95 2.0 FL0219 -9 0 4.0 -9 2 JAN FS DEC NA 12 95 NA NA NONE 0.5 HIGH SP HIGH NA N 1.5 JUN ND SEP ND NA 155 NA NONE 72 4 M D 40 P 12 N -9 2 NA -9 156A 5 NA -8 S -8 NA NA HIGH HIGH -9 0 -9 MED HIGH 2 NA LOW HIGH NA HIGH LOW

E-25 Appendix E Soil Classification Database URBAN LAND - URBAN LAND COMPLEX SATELLITE DURBIN AND WULFERT MUCKS, MUCKS, DURBIN AND WULFERT FLOODED FREQUENTLY FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL021 21038 - BOCA COMPLEX co- MATLACHA URBAN LAND 11 38 SATELLITE FL021 21039 co 9 39 FL021 21040 co 40 2 FL021 21041 co 41 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 45 ENDSHWT VAR DURSHWT DC0035 2.0HYDRIC 2.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND NAANFLOOD FREQ NANFLOOD BEG NA NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA 60SLOPE LOW C 155 NA HIGHSLOPE 20 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 -9OTHERPH 2 -9 FL0102LEACH FS 95RUNOFFCORCON 1.5 FL0356CORSTEEL 3.5 NA NA JUN MUCK NOV 55 HIGH 6 HIGH 0.0 ND ND C 0.5 JAN N SP NONE DEC 3 12 NA -8 155 FREQ NA D S -8 VP Y 19 DC0035 JAN 156A -9 0 DEC -8 VAR -9 2 U -8 65 2.0 NA 2.0 NA NA -9 NA 0 -9 HIGH 1 LOW MED LOW NONE NA -9 NA LOW NA HIGH NA N NA HIGH HIGH NA 155 NA -8 -8 C -9 0 -9 2 NA HIGH HIGH NA ND ND

E-26 Soil Classification Database Appendix E PENNSUCCO LOAM SILT PAOLA FINE SAND, FINE PAOLA 8 PCT 1 TO SLOPES WINDER, RIVIERA, LIMESTONE SUBSTR., AND SUBSTR., RIVIERA, LIMESTONE WINDER, DEPRESSIONAL CHOBEE SOILS, BEACHES ASSOCIATION S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 70 ENDSHWT FS DURSHWT FL0060 1.5HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND CANFLOOD FREQ NANFLOOD BEG SP-MW 2ANFLOOD END NONE FL0283 HIGHROCKDEPTH 45 LOWROCKDEPTH FS NA -8SLOPE LOW -2.0 A 155 NA HIGHSLOPE -8 1.0 LOWPANDEPTH JUN HIGH MARPANDEPTH PANHARD 0 -9OTHERPH 10 2 -9 VPLEACH DRUNOFF YCORCON NONE 25CORSTEEL NA NA NA 155 70 NA U HIGH 40 LOW LOW MED -9 0 -9 1 FL0056 NA 95 NA FS 6.0 LOW HIGH 6.0 LOW NA HIGH NA FL0352 -9 E NONE A 95 N SIL 3 0.0 1.0 JUN NA 155 NOV NA -8 S -8 NONE 6 P -9 D 1 -9 Y 8 26 NA 156A NA NA 72 NA HIGH LOW 40 S LOW HIGH -9 0 -9 1 NA MED UNDRAINED HIGH LOW HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL021 21042 - co CANAVERAL 9 42 FL021 21043 co 43 6 FL021 21045 co 45 10 FL021 21048 co 48 3

E-27 Appendix E Soil Classification Database KESSON MUCK, KESSON MUCK, FLOODED FREQUENTLY OCHOPEE FINE OCHOPEE SANDY LOAM SANDY LOAM, LOW SANDY LOAM, MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL021 21049 co SANDS HALLANDALE AND BOCA FINE 7 49 FINE OCHOPEE FL021 21050 co 50 3 FL021 21051 co 51 3 FL021 21052 co 52 2 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 60 ENDSHWT FS DURSHWT FL0388 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKIND DANFLOOD FREQ YANFLOOD BEG P 26ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA 40SLOPE LOW U 156A NA HIGHSLOPE 7 LOWPANDEPTH HIGHPANDEPTH PANHARD FL0488 0 -9 95OTHERPH FSL 2 -9LEACH 0.0RUNOFF 1.0CORCON JUNCORSTEEL OCT NA NA FL0488 5 MED D HIGH LOW Y FSL 95 HIGH NONE 24 P 0.0 1.0 JUN FL0274 NA 156A OCT 20 NA S 6 MUCK 5 95 NONE D -9 0.0 0 Y -9 JAN 24 1 0.5 P DEC 156A NA 20 NA NA FREQ NA S 6 12 LOW HIGH D HIGH LOW 18 Y 156A VP -9 0 -9 JAN 2 DEC -8 NA S NA -8 MED MED HIGH LOW -9 0 -9 1 NA HIGH NA LOW HIGH LOW

E-28 Soil Classification Database Appendix E NO DATA WATER BASINGER FINE SAND, BASINGER FINE FLOODED OCCASIONALLY JUPITER - BOCA JUPITER COMPLEX FREQUENTLY FLOODED FREQUENTLY MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL021 21053 SOILS, co ESTERO AND PECKISH 2 53 FL021 21054 co 54 7 FL021 21056 co 56 7 FL021 21098 FL021 21099 co 98 12 co 99 1 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 60 ENDSHWT MUCK DURSHWT FL0301 0.0HYDRIC 0.5HYDROGRPDRAINAGE JANECOLCOMM DECMLRA 12MUKIND DANFLOOD FREQ YANFLOOD BEG VP 18ANFLOOD END FREQ HIGHROCKDEPTH LOWROCKDEPTH JAN -8 LOWSLOPE U 156A DEC HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH MK-FS FL0556PANHARD 90 0 -9OTHERPH 1 -9LEACH 0.0RUNOFF 0.5 JUNCORCON NOVCORSTEEL NA NA 6 FS FL0423 D LOW HIGH Y P 95 NONE HIGH HIGH 9 0.0 NA 1.0 JUN 156A NA FEB 40 S 8 9 OCCAS D -9 0 Y -9 P 1 14 NA 156A JUL NA SEP NA -8 NA S DC0038 -8 0 MED HIGH NA LOW -9 HIGH NA -9 NA -9 0 -9 2 100 -9 NA NA NA -9 NA -9 NA HIGH HIGH NA HIGH MED NA NA NA NA NA NA NA -9 NA -9 NA NA NA NA NA -9 NA NA -9 -9 M -9 -9 -9 -9 NA NA NA NA -9 NA -9 -9 NA -9 NA NA NA NA NA NA

E-29 Appendix E Soil Classification Database KROME VERY KROME VERY LOAM GRAVELLY PERRINE MARL, DRAINED PENNSUCO MARL PENNSUCO MARL, PENNSUCO MARL, DRAINED LAUDERHILL MUCK MARL, DRAINED S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT GR-MARL DURSHWT FL0546 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4MUKIND DANFLOOD FREQ YANFLOOD BEG MUCK P 24ANFLOOD END NONE HIGH FL0069ROCKDEPTH 95 LOWROCKDEPTH NA 20SLOPE LOW S 156A NA -2.0 SIL HIGHSLOPE 1 0.0 FL0352 LOWPANDEPTH JUN HIGHPANDEPTH APRPANHARD 95 0 -9OTHERPH 1 11 -9 0.0LEACH DRUNOFF 1.0 JUN YCORCON NONE NOV 25 VP FL0352CORSTEEL SIL NA DRAINED NA 156A 6 40 NA FL0373 NONE S MED MED D 20 95 LOW HIGH Y P 24 SIL 0.0 JUN 1.0 156A NOV NA -9 0 -9 72 NA 1 FL0549 S 95 40 UNDRAINED NONE -1.0 JUN 6 DRAINED NA NOV 1.0 D GRV-L -9 25 Y 0 P -9 156A LOW NONE HIGH 1 HIGH MED NA NA 72 NA UNDRAINED 6 95 4.0 40 S DRAINED JUN 156A NOV D LOW HIGH 24 HIGH Y 5.0 LOW VP NONE NA NA -9 40 0 -9 1 NA 20 S NA 156A 6 HIGH LOW HIGH A 9 LOW MW -9 N -9 NA 0 1 NA 10 HIGH NA LOW HIGH LOW 2 S -9 -9 0 LOW MED LOW 2 NA LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL025 25002 GRAVELLY da BISCAYNE 3 2 FL025 25003 da 4 3 FL025 25004 da 3 4 FL025 25005 FL025 25006 da 3 5 FL025 da 25007 3 6 da 9 7

E-30 Soil Classification Database Appendix E PERRINE MARL UDORTHENTS, MARLY SUBSTR. - SUBSTR. MARLY UDORTHENTS, COMPLEX LAND URBAN UDORTHENTS, LIMESTONE SUBSTR. - SUBSTR. LIMESTONE UDORTHENTS, COMPLEXURBAN LAND WATER COMPLEX WATER S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 50 ENDSHWT CB-S DURSHWT FL0089 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND NA FL0376ANFLOOD FREQ CB-S N 60ANFLOOD BEG W NAANFLOOD END 2.0 NONE HIGHROCKDEPTH 4.0 LOWROCKDEPTH NA JAN 80SLOPE LOW C 156A NA DEC HIGHSLOPE 40 LOWPANDEPTH 12 HIGHPANDEPTH NAPANHARD 15 N -9OTHERPH NONE SP NA 40 -9LEACHRUNOFFCORCON NA 156A 72CORSTEEL NA NA C 40 NA FL0377 HIGH HIGH CB-S 0 -9 LOW LOW 2 -9 60 2.0 4.0 NA JAN NA DEC HIGH LOW 12 MED HIGH NA NONE NA N SP 156A NA FL0373 90 NA 10 SIL C 95 -1.0 0 -9 2 -9 1.0 JUN NOV NA NA NONE 6 MED MED D MED LOW 25 VP Y 156A NA NA 40 20 S -9 0 -9 1 NA LOW UNDRAINED HIGH HIGH LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL025 25009- da UDORTHENTS 11 9 FL025 25010 da 11 10 FL025 25011 da 11 11 FL025 25012 da 3 12

E-31 Appendix E Soil Classification Database CARDSOUND SILTY CLAY LOAM - CLAY SILTY CARDSOUND COMPLEXROCK OUTCROP TAMIAMI MUCK, TAMIAMI DEPRESSIONAL BISCAYNE MARL, MARL, BISCAYNE DRAINED URBAN LAND MUCK S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT MARL DURSHWT FL0546 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4 MUCK FL0055MUKIND 95 DANFLOOD FREQ YANFLOOD BEG -2.0 P 25ANFLOOD END 0.0 DC0035 VAR NONE JUN HIGHROCKDEPTH FL0546 APR LOWROCKDEPTH NA 20SLOPE LOW 95 S 156A NA MARL HIGHSLOPE 1 11 2.0 LOWPANDEPTH D 2.0 HIGH NAPANDEPTH Y 95 NONE NAPANHARD VP 24 0 -9 0.0OTHERPH FL0552 1 -9LEACH 1.0 JUN NA 156A -9RUNOFF SEP 20 MUCK NACORCON NONE S NACORSTEEL 8 NA N NA NA NONE UNDRAINED 4 FL0548 156A 95 D NA -9 0 MED -1.0 -8 MED P -9 NA 1 24 SICL Y UNDRAINED LOW HIGH 156A JAN 1.0 M DEC NA -8 NA NA NA NONE 20 S -9 DRAINED 0 1 -9 MED HIGH 12 2 60 5.0 HIGH MED D JAN 156A DEC 6.0 25 VP -9 NA Y 0 -9 NONE NA 1 NA HIGH HIGH NA ND ND 51 NA MED MED S 12 156A 20 HIGH LOW A W 9 N -9 NA NA -9 0 NA 2 9 NA MED HIGH C HIGH 2 MED -9 -9 0 HIGH LOW 2 NA LOW LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL025 25013 MARL da BISCAYNE 3 13 DANIA FL025 25014 da 14 4 FL025 25015 FL025 25016 da 15 11 da 16 FL025 3 25018 FL025 25020 da 18 5 da 20 9

E-32 Soil Classification Database Appendix E PERRINE MARL, PERRINE MARL, TIDAL BISCAYNE MARL - ROCK BISCAYNE OUTCROP COMPLEX MATACUMBE MATACUMBE MUCK CHEKIKA VERY CHEKIKA VERY LOAM GRAVELLY OUTCROP COMPLEX S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 55 ENDSHWT S DURSHWT FL0551 5.0HYDRIC 6.0HYDROGRPDRAINAGE JANECOLCOMM DECMLRA 12MUKIND AANFLOOD FREQ NANFLOOD BEG W 9ANFLOOD END NONE HIGHROCKDEPTH FL0547 LOWROCKDEPTH 95 NA 9SLOPE LOW GRV-L C 156A NA 1.0 HIGHSLOPE 2 LOWPANDEPTH 3.0 JUN HIGHPANDEPTH NOVPANHARD 0 FL0519 -9OTHERPH 2 6 -9LEACH MUCKRUNOFF 95 CCORCON N NONE SP 1.5CORSTEEL FL0546 NA 24 3.0 JUL NA DEC NA MARL 156A NA 10 HIGH S HIGH 60 2 MED LOW 6 0.0 OCCAS C JUN 1.0 SEP N MW -9 0 14 -9 1 156A JUL NONE DEC FL0554 9 4 NA S 2 NA P D Y MARL HIGH 156A 25 HIGH LOW HIGH NA -9 NA 0 -9 2 95 20 1.0 C JAN DEC NA 0 1.0 NA MED HIGH FREQ MED -9 LOW 0 -9 1 12 NA MED HIGH 156A VP UNDRAINED D Y HIGH LOW 19 JAN DEC 40 S 20 NA -9 -9 0 1 HIGH LOW NA HIGH LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL025 25022 SAND - ROCK da OPALOCKA 9 22 FL025 25023 da 23 9 FL025 25024 da 24 FL025 9 25025 da 25 3 FL025 25026 da 26 2

E-33 Appendix E Soil Classification Database HALLANDALE FINE SAND PLANTATION PLANTATION MUCK TERRA CEIA TERRA CEIA MUCK, TIDAL PENNSUCO MARL, TIDAL PAHOKEE PAHOKEE MUCK ROCK OUTCROP COMPLEXROCK OUTCROP S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 75 ENDSHWT SCL DURSHWT FL0535 0.0HYDRIC 1.0HYDROGRPDRAINAGE APRECOLCOMM SEPMLRA 6MUKIND DANFLOOD FREQ YANFLOOD BEG P 25ANFLOOD END RARE HIGHROCKDEPTH LOWROCKDEPTH NA 51SLOPE LOW C 156A NA HIGHSLOPE 0 LOWPANDEPTH HIGHPANDEPTH PANHARD FL0072 0 -9 MUCK 95OTHERPH 2 -9LEACH -1.0RUNOFF 0.0 FL0353CORCON JUNCORSTEEL SIL NA FEB NA 95 9 FL0374 0.0 LOW HIGH D 0.5 JAN LOW HIGH Y DEC NONE MUCK 25 VP FL0095 95 NA 156A 0.0 12 51 NA FREQ JAN S 0.5 MUCK D DEC 36 Y FL0065 VP 19 156A 95 JAN -9 FREQ 0 72 -2.0 FS DEC -9 12 1 JUN APR 0.0 S 40 D VP 19 Y 156A NA NONE JAN UNDRAINED DEC -9 95 0.5 0 JUN -8 -9 NA LOW HIGH 11 SEP 1 HIGH 1.5 MED -8 S 156A VP D NONE 25 NA Y NA NA HIGH MED -9 HIGH NA LOW 0 -9 40 4 1 156A 20 S P NA D 9 HIGH NA LOW Y NA HIGH HIGH DRAINED -9 20 -9 0 1 7 HIGH NA S NA LOW HIGH MED -9 -9 HIGH 0 HIGH HIGH 2 NA LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL025 25028 da LOAM - DEMROY MUCKY SANDY CLAY 7 28 FL025 25030 da 30 4 FL025 25031 da FL025 31 25032 2 FL025 25033 da 32 2 FL025 25034 da 33 5 da 34 8

E-34 Soil Classification Database Appendix E DADE FINE SAND SAND BEACHES POMELLO ROCK OUTCROP - VIZCAYA - - VIZCAYA ROCK OUTCROP COMPLEX BISCAYNE BASINGER SAND FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL025 25035 da MARGATE 7 35 FL025 25037 da 37 7 FL025 25038 da 38 3 FL025 25039 FL025 25040 da 39 FL025 25041 2 da 40 9 da 41 9 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0094 -1.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0063 95ECOLCOMM FEB FSMLRA 9 0.0MUKIND DC0015 D 1.0ANFLOOD FREQ Y JUNANFLOOD BEG P FEB 9ANFLOOD END 55 ROCK NONE HIGHROCKDEPTH -1.0 9 LOWROCKDEPTH NA 40 1.0SLOPE LOW JUN D S 156A NA HIGHSLOPE 20 Y DEC NONE P LOWPANDEPTH 26 HIGHPANDEPTH PANHARD NA 156A 7 0 -9OTHERPH -8 NONE 2 NA -9 DLEACH S -8 DC0002 NRUNOFF P 25CORCON FL0078 156ACORSTEEL NA NA S -9 0 NA NA 20 -9 1 95 FL0351 C 0 0.0 HIGH HIGH JAN 6.0 MED HIGH DEC NA S NA -9 95 0 -9 2.0 HIGH 2 HIGH JUL FREQ HIGH NOV MED 3.5 12 NA D FS NA NONE 95 HIGH Y HIGH 5.0 156A NA JUN P SEP HIGH LOW 6.0 JAN 5 NONE DEC -8 156A C M 3 N -8 MW NA NA 156A 4 -8 -9 A 1 -9 S -8 W 2 N 9 NA NA NA HIGH HIGH NA 40 -9 HIGH HIGH -9 0 20 S 2 MED MED NA LOW NA HIGH -9 -9 HIGH 0 LOW 2 LOW NA MED NA

E-35 Appendix E Soil Classification Database WATER KESSON MUCK, TIDAL ST. AUGUSTINE ST. SAND CANAVERAL CANAVERAL SAND SUBSTRATUM, 2 TO 5 PCT SLOPES 5 TO 2 SUBSTRATUM, COMPPCT 195 959595100 SPSPVPNA 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT ENDSHWT CB-S DURSHWT FL0376 2.0HYDRIC 4.0HYDROGRPDRAINAGESP JANECOLCOMM DECMLRA 12MUKIND NAANFLOOD FREQ NANFLOOD BEG NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA 72SLOPE LOW M 156A NA HIGHSLOPE 40 LOWPANDEPTH HIGH FL0060PANDEPTH SPANHARD 0 -9OTHERPH 5 1.5 -9LEACH 3.0RUNOFF FL0320 JUNCORCON NOVCORSTEEL NA S 6 NA C 1.5 3.0 N JUL FL0274 HIGH NONE LOW 2 OCT MED HIGH NA 156A 4 -8 DC0038 NA S NONE MUCK -8 C 0.0 N JAN NA 0.5 DEC 156A -9 NA 0 NA -9 2 NA -8 FREQ S -8 12 -9 NA NA -9 D NA NA Y 19 156A -9 HIGH NA 0 -9 LOW 2 JAN MED LOW DEC -8 -9 NA -8 S NA NA NA HIGH NA NA MED HIGH HIGH NA NA -9 0 -9 -9 1 -9 M NA LOW NA HIGH HIGH LOW -9 -9 -9 -9 NA NA NA NA NA NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL025 25042 LIMESTONE da UDORTHENTS, 11 42 FL025 25045 da 9 45 FL025 25047 da 47 9 FL025 25048 FL025 25099 da 48 2 da 99 1

E-36 Soil Classification Database Appendix E BRADENTON BRADENTON FINE SAND BASINGER FINE SAND, BASINGER FINE DEPRESSIONAL BASINGER FINE SAND, BASINGER FINE FLOODED FREQUENTLY BASINGER SAND FINE DEPRESSIONAL S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT MK-FS DURSHWT FL0315 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW S 155 NA HIGHSLOPE -8 FS LOW FL0063PANDEPTH 95 HIGHPANDEPTH PANHARD 0.0 0 -9OTHERPH FL0423 1 -9 1.0LEACH JUN FS FEBRUNOFF 95CORCON 9CORSTEEL 0.0 NA NA 1.0 JUN D FEB Y P NONE 26 HIGH HIGH MED HIGH 9 FL0261 NA 155 FREQ -8 NA D S -8 Y P 21 FS 95 JUL -2.0 155 -9 0 SEP -8 -9 2 JUN 0.0 S MAR -8 FL0232 NA NONE NA -9 0 10 -9 HIGH 2 HIGH D HIGH MED FS 25 Y VP NA 95 0.5 NA NA HIGH HIGH 155 JUN NA SEP 1.5 HIGH MED -8 S -8 NONE 4 -9 0 -9 2 D 8 P N NA NA HIGH 155 HIGH NA NA HIGH MED -8 -8 S -9 -9 0 1 LOW HIGH NA HIGH NA LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL027 27002 deMUCKY SAND, FINE ANCLOTE 6 2 FL027 27003 de 7 3 FL027 27004 de 6 4 FL027 27005 de 6 5 FL027 27006 de 8 6

E-37 Appendix E Soil Classification Database CHOBEE MUCK, CHOBEE MUCK, DEPRESSIONAL CASSIA FINE SAND BRADENTON - FELDA - CHOBEE FELDA - - BRADENTON FLOODED COMPLEX, FREQUENTLY OCCASIONALLY FLOODED OCCASIONALLY S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 40 ENDSHWT FS DURSHWT FL0348 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4MUKIND DANFLOOD FREQ YANFLOOD BEG P 21ANFLOOD END OCCAS HIGHROCKDEPTH LOWROCKDEPTH JUN -8SLOPE LOW C 155 NOV HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 -9OTHERPH 2 -9LEACHRUNOFF FL0348 35CORCON FSCORSTEEL 0.0 NA NA 1.0 JUN SEP LOW HIGH LOW HIGH 4 D FREQ Y 21 P JUN NOV 155 -8 C FL0100 -8 95 FS FL0412 -9 0 1.5 -9 2 3.5 JUL JAN 95 NA MUCK NA -2.0 7 NONE JUN 0.0 LOW HIGH MAR C HIGH LOW N 3 SP NONE NA NA 155 10 -8 D S -8 Y VP 25 NA NA 155 -9 0 -8 -9 2 S -8 NA NA -9 MED LOW 0 -9 MED HIGH 1 NA HIGH LOW NA HIGH HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL027 27007 COMPLEX, - CHOBEE - FELDA de BRADENTON 6 7 FL027 27008 de 6 8 FL027 27009 FL027 de 27010 9 9 de 5 10

E-38 Soil Classification Database Appendix E FELDA FELDA FINE SAND FARMTON FARMTON FINE SAND EAUGALLIE EAUGALLIE FINE SAND DURBIN AND WULFERT MUCKS, MUCKS, DURBIN AND WULFERT FLOODED FREQUENTLY DEPRESSIONAL S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT MK-FS DURSHWT FL0299 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW S 155 NA HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH PANHARD MUCK FL0356 0 -9OTHERPH 60 1 -9LEACH 0.0RUNOFFCORCON 0.5 JANCORSTEEL NA DEC NA 12 LOW HIGH D HIGH HIGH Y VP FREQ 18 JAN FS FL0154 155 -8 DEC U -8 95 FL0214 0.5 -9 1.5 FS 0 JUN -9 SEP 1 FL0127 95 4 0.5 NA FS JUN NA NONE 1.5 SEP D P N HIGH HIGH 6 HIGH HIGH 95 0.0 NA NONE JUL 4 NA 155 MAR 1.0 -8 S -8 D P N NONE 6 NA 155 NA 9 -9 0 -9 -8 2 D S -8 P Y 26 NA NA 155 NA NA LOW HIGH -9 MED -8 HIGH 0 -9 2 -8 S NA HIGH LOW NA HIGH MED -9 -9 0 2 HIGH NA LOW HIGH MED NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL027 27011SAND, MUCKY FINE de DELRAY 6 11 FL027 27012 de 12 2 FL027 27013 de FL027 13 27014 8 FL027 27015 de 14 8 de 15 7

E-39 Appendix E Soil Classification Database IMMOKALEE IMMOKALEE FINE SAND GATOR MUCK, GATOR DEPRESSIONAL FLORIDANA MUCKYFLORIDANA FINE SAND, DEPRESSIONAL FELDA FINE SAND, FINE SAND, FELDA DEPRESSIONAL FREQUENTLY FLOODED FREQUENTLY S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0329 0.0HYDRIC 1.0HYDROGRPDRAINAGE JULECOLCOMM MARMLRA 9MUKIND DANFLOOD FREQ YANFLOOD BEG P 12ANFLOOD END FREQ HIGHROCKDEPTH LOWROCKDEPTH JUL -8SLOPE LOW FL0298 S 155 FEB 95 HIGHSLOPE -8 FS LOWPANDEPTH -2.0 HIGHPANDEPTH 1.0PANHARD JUN 0 -9OTHERPH DEC 2 -9LEACHRUNOFF 7CORCON FL0262CORSTEEL D NA Y NONE NA 25 VP 95 MK-FS -2.0 NA LOW HIGH 0.0 NA JUN MED 155 -8 HIGH MAR S -8 10 FL0415 NONE -9 0 D -9 1 Y VP 25 MUCK NA 95 NA NA 155 FL0058 -2.0 NA -8 S JUN -8 0.0 APR LOW HIGH HIGH HIGH FS -9 NONE 0 -9 11 2 95 0.5 D JUN SEP VP 1.5 25 Y NA NA NA HIGH LOW 155 NONE NA MED LOW -8 S -8 4 P D 6 N -9 NA 0 -9 155 NA 1 -8 NA -8 HIGH S DRAINED LOW HIGH HIGH -9 -9 0 NA 2 HIGH NA MED HIGH HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL027 27016SAND, de FINE FELDA 6 16 FL027 27017 de 17 6 FL027 27018 de 18 6 FL027 27019 de FL027 19 27020 5 de 20 8

E-40 Soil Classification Database Appendix E ONA FINE SANDONA FINE SAND PINEDA FINE MYAKKA MYAKKA SAND FINE MALABAR FINE SAND, FINE MALABAR DEPRESSIONAL MALABAR FINE FINE MALABAR SAND, HIGH FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL027 27021 de MALABAR 7 21 FL027 27022 de 22 8 FL027 27023 de 23 6 FL027 27024 FL027 27025 de 24 8 FL027 27026 de 25 8 de 26 7 HTDR41044 6 DUR64 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FSSHWT FL0123 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0390 95ECOLCOMM NOV FSMLRA 0.5MUKIND D 1.5ANFLOOD FREQ Y JUNANFLOOD BEG P SEP 26 FL0286ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH 95 NA -8 FSSLOPE LOW D S 155 NA -2.0 HIGHSLOPE -8 Y NONE 6 P LOWPANDEPTH 0.0 JUN HIGHPANDEPTH MARPANHARD NA 0 -9OTHERPH 155 -8 2 FL0059 NA -9LEACH S -8RUNOFF NONECORCON D FL0124 YCORSTEEL NA VP 25 95 -9 0 FS NA -9 2 0.5 NA 155 JUN NA 1.5 SEP -8 LOW HIGH S LOW HIGH -8 FL0080 NA 95 NA FS 0.5 NONE JUN LOW HIGH SEP 1.5 -9 HIGH LOW 0 -9 1 D N NONE P 6 NA NA 155 NA FS 95 NA HIGH 0.0 LOW JUN -8 NOV HIGH LOW D 1.0 S -8 N P NONE 6 155 NA NA -9 -8 0 -9 2 -8 S NA D HIGH NA MED Y HIGH P 155 -9 HIGH 26 NA -9 0 NA 1 HIGH -8 NA MED HIGH NA HIGH -8 S -9 -9 HIGH 0 LOW HIGH 2 NA LOW NA

E-41 Appendix E Soil Classification Database POMPANO POMPANO FINE SAND POMELLO FINE SAND PINEDA AND PINELLAS PINEDA AND PINELLAS FINE SANDS PINEDA FINE SAND, PINEDA FINE DEPRESSIONAL FLOODED S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0479 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND DANFLOOD FREQ YANFLOOD BEG P 26ANFLOOD END FREQ HIGHROCKDEPTH LOWROCKDEPTH JUL -8SLOPE LOW S 155 SEP HIGHSLOPE -8 LOWPANDEPTH FL0411 95 HIGHPANDEPTH FSPANHARD 0 -9 -2.0OTHERPH 1 -9 0.0LEACH JUNRUNOFF MARCORCONCORSTEEL NA 10 NA D Y FL0080 NONE 25 VP LOW HIGH LOW HIGH NA 60 FS NA 155 -8 0.0 S -8 1.0 JUN NOV -9 0 FL0078 -9 6 1 NONE D Y FL0032 P 26 NA 95 NA FS NA 2.0 NA 155 LOW HIGH JUL -8 3.5 NOV HIGH LOW U -8 95 FS 0.0 NONE OCT JUN -9 5 0.5 0 -9 2 C 3 N MW NONE NA NA NA 155 NA HIGH LOW 5 HIGH -8 LOW D P S -8 Y 26 NA 155 NA -9 -8 0 -9 2 -8 S NA MED NA MED LOW -9 HIGH -9 0 2 HIGH NA HIGH HIGH NA MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL027 27027 deFINE SAND, FREQUENTLY PINEDA 6 27 FL027 27028 de 28 6 FL027 27029 de 29 7 FL027 27030 FL027 27031 de 30 9 de 31 7

E-42 Soil Classification Database Appendix E TAVARES FINE SAND, FINE TAVARES 5 PCT 0 TO SLOPES SMYRNA SMYRNA FINE SAND SATELLITE SATELLITE SAND FINE SAMSULA MUCK, MUCK, SAMSULA DEPRESSIONAL QUARTZIPSAMMENTS, QUARTZIPSAMMENTS, LEVEL NEARLY FINE SAND FINE CLOMN 5 64 253 47 116 DUR4-9 S S SS 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FSSHWT FL0393 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUN FL0437 95ECOLCOMM6NA SEP FSMLRA 2.0MUKINDSM D 8.0ANFLOOD FREQ N NAANFLOOD BEG P NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW NA 155 NA HIGHSLOPE -8 N NONE MW LOWPANDEPTH FL0092 HIGHPANDEPTH PANHARD NA 0 -9 95OTHERPH 155 -8 MUCK 2 NA -9LEACH -8 -2.0RUNOFF 0.0CORCON JUNCORSTEEL APR NA FL0102 -9 0 NA -9 3 NONE LOW D HIGH FL0091 FS HIGH HIGH VP Y NA 95 NA 1.5 FL0021 HIGH NA LOW 3.5 JUN 155 HIGH HIGH NA NOV -8 FS -8 95 0.5 NONE JUN 1.5 SEP C -9 FS SP 0 -9 N 1 NONE 95 3.5 JUN NA 155 DEC NA 6.0 NA UNDRAINED -8 NONE MED D P HIGH -8 HIGH HIGH N 155 NA NA -9 NA -8 0 -9 A MW 2 -8 N 155 NA NA HIGH MED NA MED LOW NA -9 -8 -9 0 -8 2 MED NA HIGH HIGH HIGH NA -9 -9 0 HIGH LOW 5 HIGH LOW NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL027 27032 de PUNTA 8 32 FL027 27033 de 33 11 FL027 27034 de 34 5 FL027 27035 FL027 27036 de 35 9 FL027 27037 de 36 8 de 37 9

E-43 Appendix E Soil Classification Database WATER ZOLFO ZOLFO FINE SAND WABASSO WABASSO FINE SAND VALKARIA VALKARIA SAND FINE FREQUENTLY FLOODED FREQUENTLY COMPPCT 195 -9 95 NANANANA -9-9-9-9 959595100 JUN LOW-9 11 446-9 BEGNA D DUR11 1 DDCNA 0 LOW0 HIGH1 222-9 000-9 S 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT SSSM SHWT BEG ENDSHWT MUCKSHWT FL0031 -2.0HYDRIC 0.0HYDROGRPD DRAINAGE JUNECOLCOMM APRMLRAMUKINDS ANFLOOD FREQ YANFLOOD VP 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH -8SLOPE 155 NASLOPE 88PANDEPTH HIGHPANDEPTH MUCK FL0305PANHARDOTHERPH -9 0.0LEACHRUNOFF 0.5 JUNCORCON APRCORSTEEL NA UNDRAINED MED FL0126 HIGH FS Y VP FREQ MED 21 MED FL0075 0.0 155 -8 NOV FS 88 1.0 JUN FL0288 SEP 0.5 DC0038 -9 JUN FS 1.5 NA NONE SEP P Y 26 NA 2.0 NONE JUN NA NOV 3.5 NA 155 88 MED HIGH 88 MED MED P 6 N NONE -9 NA NA NA 155 -9 88 NA -9 NA 88 SP N 4 155 NA NA 88 HIGH HIGH NA -9 88 MED HIGH NA NA NA NA NA NA HIGH LOW -9 NA MED HIGH -9 -9 MED NA HIGH MED LOW NA -9 NA NA NA NA NA SOCD55 7891 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE5 NAMEMAPUNIT FL027 27038 DEPRESSIONAL MUCK, CEIA de TERRA 38 MUCK, TERRA CEIA FL027 27039 de 39 FL027 27040 FL027 de 27041 40 FL027 27042 de 41 FL027 27099 de 42 de 99

E-44 Soil Classification Database Appendix E FELDA FELDA FINE SAND SANIBEL SANIBEL MUCK GATOR GATOR MUCK POPLE SAND FINE MALABAR MALABAR SAND FINE SMYRNA SMYRNA SAND FINE VALKARIA VALKARIA SAND FINE FINE SAND FINE SOCD888 5 7 45678 9 10 MUIDSTSSAIDMUSYM2 CNTYABBRLSPOSCODE878785 MAPUNIT NAME FL043 43002 gl HALLANDALE FL043 43004 gl FL043 43005 FL043 43006 gl FL043 43007 gl FL043 43008 FL043 gl 43009 FL043 43010 gl gl gl COMPPCT 19595959595959595 DDDDD 266266252526 D PPPPVPVPP D 445411119 2 2 LOW-9-9-9-9-9-9-9-9 00000 0 0 ENDNANANANANANANANA DUR4 SSSSS S S LOW0 HIGH222221 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG ENDSHWT FSSHWT FL0065 0.5HYDRIC 1.5HYDROGRPD DRAINAGEP JUNECOLCOMM6 SEP FL0126MLRA FSMUKINDS ANFLOOD FREQ 0.0 N FL0091ANFLOOD BEG 1.0 JUNANFLOOD NONE SEP HIGHROCKDEPTH FS LOWROCKDEPTH FL0123 NA 20SLOPE 0.5 155SLOPE 7 1.5 JUNPANDEPTH FL0241 SEP Y NONE HIGHPANDEPTH PANHARD FSOTHERPH 0.0 FL0415 -9 NALEACH JUN 0.5 -8 NONE 155 OCTRUNOFFCORCON N -8CORSTEEL FS FL0073 NA 0.5 NONE JUN NA NA SEP 1.5 155 -8 -9 HIGH FL0127 HIGH -8 Y NONE LOW HIGH MUCK JUN -2.0 APR NA NA 155 0.0 NA -8 NONE -9 HIGH MUCK HIGH -8 N HIGH MED JUN -1.0 APR NA 155 NA NONE 0.0 NA MED HIGH FS -8 -9 HIGH HIGH -8 Y JUL 0.0 MAR 155 NA NA NONE LOW HIGH NA 1.0 HIGH LOW -8 -9 -8 HIGH LOW NA 155 Y NA HIGH NA LOW -9 -8 HIGH LOW HIGH NA -8 HIGH 155 UNDRAINED NA Y UNDRAINED HIGH LOW NA HIGH -9 88 LOW NA -8 HIGH LOW HIGH MED -9 NA

E-45 Appendix E Soil Classification Database FLORIDANA FINE FLORIDANA SAND, DEPRESSIONAL PINEDA SAND FINE BASINGER SAND FINE BOCA SAND FINE CHOBEE LOAMY FINE CHOBEE LOAMY SAND, DEPRESSIONAL MUCK OPC 99 95959595 19595 S SSSS 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG ENDSHWT MUCKSHWT DUR FL0077 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JAN MK-LFS FL0412ECOLCOMM DECMLRA 12 -2.0MUKINDS DANFLOOD FREQ 0.0 Y JUNANFLOOD BEG VP 25 MARANFLOOD END NONE HIGHROCKDEPTH 10 LOWROCKDEPTH NA -8 FSSLOPE LOW 155 NA FL0054 D HIGHSLOPE -8 Y VP NONE LOWPANDEPTH 25 HIGHPANDEPTH FL0063PANHARD 0.5 0 NA -9OTHERPH FS 155 2 -8 -9 NA 1.5LEACH JUN FEB -8 FL0080RUNOFFCORCONCORSTEEL 0.0 NA 9 FL0262 FS -9 DRAINED 0 JUN 1.0 NONE FEB -9 1 D P N LOW NA HIGH 6 LOW MED 0.0 NA NONE JUN FS 9 NA NOV 155 1.0 NA 40 LOW HIGH D 24 P Y HIGH NONE HIGH 26 -2.0 JUN MAR NA 155 0.0 6 NA -9 -8 0 NONE -9 2 -8 D P NA Y 26 155 NA NA NA 10 -9 HIGH MED -8 0 -9 MED HIGH 2 -8 NA D VP 25 Y 155 NA NA HIGH NA HIGH HIGH MED -9 -8 -9 0 NA -8 2 HIGH NA LOW HIGH LOW -9 NA -9 HIGH 0 LOW 1 MED NA LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL043 43011 gl TEQUESTA 5 11 FL043 43012 gl 12 6 FL043 43013 FL043 43014 13 gl 8 FL043 43015 14 gl FL043 7 43016 15 gl 7 16 gl 6

E-46 Soil Classification Database Appendix E FT. DRUM FT. FINE SAND IMMOKALEE IMMOKALEE SAND HALLANDALE - POPLE COMPLEX ASTOR FINE ASTOR SAND, DEPRESSIONAL EAUGALLIE EAUGALLIE SAND FINE TERRA CEIA MUCK MUCK HTDR14 4 44 DUR81148 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT MUCKSHWT FL0071 -1.0HYDRIC 0.0HYDROGRPDRAINAGE JUN MUCKECOLCOMM JAN FL0031 95MLRAMUKIND -2.0 DANFLOOD FREQ Y FL0154 FS 0.0ANFLOOD BEG VP JUN 25ANFLOOD END APR NONE HIGHROCKDEPTH 95 LOWROCKDEPTH FL0231 0.5 NA -8SLOPE LOW S 155 NA HIGHSLOPE 1.5 -8 D JUN FS LOW YPANDEPTH VP SEP NONE 25 HIGHPANDEPTH 95PANHARD 0 -2.0 -9OTHERPH NA 1 -9LEACH 155 -8 JUN NONE NA 0.0 FL0065 S DRUNOFF JAN 52 P NCORCON 6CORSTEEL NA NONE NA UNDRAINED FS -9 155 0 NA -8 -9 1 DRAINED S -8 FL0058 LOW D HIGH 60 VP 0.5 Y MED HIGH 25 NA JUN NA 1.5 SEP NA 155 -9 FL0225 NA 0 -9 -8 LOW 2 HIGH NONE -8 S S MED MED NA NA 0.5 95 HIGH LOW JUN -9 P D SEP 0 -9 HIGH MED 1.5 N 6 1 NONE NA FS 155 NA NA HIGH MED 20 0.5 HIGH 95 JUN LOW 7 SEP C NA NONE 1.5 P D -9 N 6 -9 155 NA 0 2 NA HIGH NA HIGH -8 HIGH LOW -8 S NA P D 155 N NA 6 NA -9 -9 -8 HIGH 0 MED 2 HIGH NA NA -8 S HIGH HIGH -9 LOW -9 HIGH 0 LOW NA 2 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL043 43017 gl OKEELANTA 5 17 FL043 43019 gl 19 4 FL043 43020 FL043 20 gl 43022 8 22 gl 6 FL043 43024 FL043 43026 24 gl 8 FL043 43027 26 gl 8 27 gl 8

E-47 Appendix E Soil Classification Database LAUDERHILL MUCK MALABAR FINE FINE MALABAR SAND, HIGH ARENTS, STEEP VERY BASINGER FINE SAND, BASINGER FINE DEPRESSIONAL OLDSMAR SAND FINE MYAKKA MYAKKA SAND FINE FINE SAND FINE SOCD98 1 4 118 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE9886 MAPUNIT NAME FL043 43028 gl POMELLO 28 FL043 43029 gl 29 FL043 43023 FL043 43034 23 gl 34 gl FL043 43035 FL043 43036 35 gl FL043 43037 36 gl 37 gl OPC 9999 959595 NANANA 195959595 25 11 D NAD 2 LOW-9-9-9-9-9-9-9 602 0 ENDNANANANA 450 DUR54410-94 N N Y LOW0000 M HIGH2221 S S 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT ENDSHWT FSSHWT FL0078 2.0HYDRICNNNY 3.5HYDROGRPCDDD DRAINAGE JUL FL0059ECOLCOMM36625NA6 NOV FSMLRA 0.5MUKINDSSSS FL0067 1.5ANFLOOD FREQ JUNANFLOOD BEG MW SEPANFLOOD S FL0261 NONE HIGHROCKDEPTH 0.5 LOWROCKDEPTH NA -8 1.5SLOPE JUN 155 SEP PSLOPE -8 NONEPANDEPTH HIGHPANDEPTH FS -2.0PANHARD NA JUN 0.0OTHERPH NONE 155 -8 MAR -9LEACH FL0085 -8 PRUNOFFCORCON NONECORSTEEL NA NA 155 FL0390 NA -8 -9 -8 VP MED HIGH VAR HIGH 6.0 LOW NA NA NA 155 NA 6.0 FL0069 NA -8 -9 MED HIGH -8 HIGH NONE HIGH FS NA 0.5 NA JUN SEP HIGH 1.5 LOW -9 HIGH MED NONE W NA NA 155 HIGH NA HIGH MED MUCK HIGH -2.0 -8 JUN APR NONE 0.0 -8 P 155 NA -9 -8 -8 LOW NA LOW LOW NA LOW VP 155 NA -9 HIGH LOW 40 LOW NA HIGH NA 20 HIGH LOW -9 MED HIGH NA DRAINED

E-48 Soil Classification Database Appendix E SAND WATER FINE ADAMSVILLE SANIBEL MUCK, MUCK, SANIBEL DEPRESSIONAL OKEELANTA AND DANIA OKEELANTA DEPRESSIONAL MUCKS, DANIA MUCK PLANTATION PLANTATION MUCK MUCK S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT MUCK DURSHWT FL0072 -1.0HYDRIC 0.0HYDROGRP MUCKDRAINAGE FL0095 JUN 95ECOLCOMM FEBMLRA 9 -2.0MUKIND 0.0 DANFLOOD FREQ JUN FL0055 Y MUCKANFLOOD BEG VP APR 25ANFLOOD END FL0431 NONE HIGHROCKDEPTH 95 MUCK 11 LOWROCKDEPTH -2.0 NA 51 LOWSLOPE D S 155 NA 0.0 Y VP HIGHSLOPE JUN 36 NONE 25 APR LOWPANDEPTH 50 -2.0 HIGHPANDEPTH PANHARD NA 0 JUN -9 40 0.0 11 155OTHERPH NA APR 1 -9 S 20LEACH NONE DRUNOFF VP FL0073 YCORCON 25 MUCK NONECORSTEEL 11 NA -9 0 NA DRAINED -9 155 1 20 NA VP D 8 Y 25 DRAINED S LOW HIGH DC0038 MED HIGH -1.0 NA 95 NA FL0036 NA 155 NA 70 JUN DRAINED APR -9 0.0 LOW HIGH 0 NA 8 -9 U 1 HIGH MED FS NONE NA -9 11 -9 0 -9 HIGH 100 LOW 1 NA HIGH VP MED NA D -9 25 NA Y 95 2.0 HIGH NA LOW NA HIGH 155 JUN NOV HIGH NA -8 3.5 NONE DRAINED -9 S -8 NA NA NA 6 NA -9 NA NA NA -9 SP 0 NA 1 C -9 6 HIGH NA N LOW HIGH 155 NA NA LOW -9 M NA -8 -9 -8 S -9 NA -9 NA NA -9 NA NA -9 MED -9 HIGH 0 LOW NA 2 MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL043 43038 gl PAHOKEE 4 38 FL043 43040 gl 40 5 FL043 43041 FL043 43042 gl 41 4 42 gl 5 FL043 43043 FL043 43099 43 FL049 gl 49001 5 99 gl 1 1 ha 9

E-49 Appendix E Soil Classification Database CANDLER FINE SAND, CANDLER FINE 5 PCT 0 TO SLOPES TAVARES FINE SAND, FINE TAVARES 5 PCT 0 TO SLOPES APOPKA FINE SAND, APOPKA FINE PCT SLOPES 5 TO 0 FT. GREEN FINE SAND, GREEN FINE FT. PCT SLOPES 5 TO 2 FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL049 49002 ha ZOLFO 9 2 FL049 49003 ha 8 3 FL049 49004 ha 10 4 FL049 49005 ha 9 5 FL049 49006 ha 10 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0288 2.0HYDRIC 3.5HYDROGRPDRAINAGE JUN FL0362 95ECOLCOMM NOV FSMLRA 6 0.5MUKIND C 1.5ANFLOOD FREQ N JUNANFLOOD BEG SP SEP 6ANFLOOD END NONE HIGHROCKDEPTH 4 LOWROCKDEPTH NA -8SLOPE LOW D S 155 NA FL0024 HIGHSLOPE -8 N P NONE LOWPANDEPTH 6 HIGHPANDEPTH 95 FSPANHARD NA 0 -9 6.0OTHERPH 155 -8 2 NA -9LEACH 6.0 S NA -8 NARUNOFFCORCON FL0021CORSTEEL NA -9 2 NA -9 -9 5 NONE A N MED W MED 95 FS MED LOW 4 NA 3.5 NA NA 6.0 155 JUN NA -8 DEC LOW FL0003 HIGH S -8 LOW HIGH NONE 7 -9 0 -9 A 5 N MW 95 FS 4 6.0 NA 155 NA NA 6.0 NA NA NA -8 LOW LOW S -8 MED HIGH NONE -9 -9 0 -9 E 5 A N NA 155 NA 4 NA HIGH LOW NA HIGH LOW -8 -8 S -9 -9 0 5 NA HIGH LOW HIGH NA LOW

E-50 Soil Classification Database Appendix E FELDA FELDA FINE SAND POMONA FINE SAND POPASH MUCKY POPASH SAND FINE BRADENTON LOAMY FINE SAND, FINE LOAMY BRADENTON FLOODED FREQUENTLY FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL049 49007 ha BASINGER 7 7 FL049 49008 ha 6 8 FL049 49009 ha 6 9 FL049 49010 FL049 49011 ha 8 10 ha 11 7 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0063 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0348ECOLCOMM 95 FEB LFSMLRA 9 0.0MUKIND DANFLOOD FREQ 1.0 Y JUNANFLOOD BEG P 26 SEPANFLOOD END NONE HIGHROCKDEPTH 4 LOWROCKDEPTH NA -8SLOPE LOW S 155 D NA HIGHSLOPE -8 Y FREQ LOW P 12PANDEPTH HIGHPANDEPTH PANHARD JUN 0 -9OTHERPH 155 -8 FL0361 2 NOV -9LEACH S -8RUNOFF MK-FSCORCON 95CORSTEEL NA -2.0 -9 0 NA 0.0 JUN -9 2 FL0007 MAR HIGH HIGH MED HIGH FS NA FL0127 10 NA NONE 95 D LOW 0.5 HIGH Y 25 HIGH LOW VP JUN 1.5 SEP FS NA NA 155 95 -8 0.0 S NONE -8 JUL MAR 4 1.0 D N 6 P NONE -9 0 -9 NA 2 155 NA 9 -8 NA D S -8 NA Y LOW 26 P HIGH NA HIGH 155 HIGH NA -9 -8 0 -9 2 -8 S NA HIGH LOW NA HIGH HIGH -9 -9 0 2 HIGH LOW NA HIGH MED NA

E-51 Appendix E Soil Classification Database SMYRNA SMYRNA SAND MYAKKA MYAKKA FINE SAND IMMOKALEE IMMOKALEE FINE SAND FLORIDANA MUCKYFLORIDANA FINE SAND, DEPRESSIONAL FELDA FINE SAND, FREQUENTLY SAND, FREQUENTLY FINE FELDA FLOODED FINE SAND FINE UIDSS 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT S LOWSHWT SS SHWT BEG 95 ENDSHWT FS DURSHWT FL0127 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUL FL0329 95ECOLCOMM MAR FSMLRA 9 0.0MUKINDSS D 1.0ANFLOOD FREQ Y JULANFLOOD BEG P MAR 26ANFLOOD END NONE HIGHROCKDEPTH 9 LOWROCKDEPTH NA -8SLOPE LOW D 155 NA HIGHSLOPE -8 Y FREQ P 21 LOWPANDEPTH HIGHPANDEPTH PANHARD JUL 0 -9OTHERPH 155 -8 FL0262 2 FEB -9LEACH -8RUNOFF 95CORCON MK-FSCORSTEEL -2.0 NA -9 0 NA 0.0 -9 2 JUN MAR LOW HIGH MED HIGH NA 10 FL0058 NA NONE D LOW HIGH Y 25 HIGH MED VP FS FL0059 NA 95 155 NA 0.5 -8 SEP -8 FL0091 1.5 JUN FS 95 -9 NONE 0 0.5 -9 4 1 SEP JUN 1.5 D S N 6 NA P NONE NA 95 NA HIGH 0.5 LOW 155 SEP JUN NA MED LOW 1.5 -8 4 NONE -8 D N 6 P NA 155 NA -9 0 -9 4 -8 2 D -8 N NA P 6 155 NA HIGH NA MED NA HIGH HIGH -9 -8 -9 0 -8 2 HIGH NA MED HIGH NA HIGH -9 -9 HIGH 0 MED 2 HIGH NA HIGH NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL049 49011 ha FELDA 7 11 FL049 49012 ha 12 6 FL049 49013 ha 13 6 FL049 49015 FL049 49016 ha 15 8 FL049 49017 ha 16 8 ha 17 8

E-52 Soil Classification Database Appendix E JONATHAN JONATHAN SAND SPARRFINE SPARRFINE SAND POMELLO POMELLO SAND FINE PLACID FINE SAND, PLACID DEPRESSIONAL SAMSULA SAMSULA MUCK ONA FIND SAND FINE SAND FINE CLOM65533 5 DUR74111054 S SS S 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FSSHWT FL0100 1.5HYDRIC 3.5HYDROGRPDRAINAGE JUL FL0124 95ECOLCOMM36252533 JAN FSMLRA 0.5MUKINDSSS FL0092 C 1.5ANFLOOD FREQ N JUNANFLOOD BEG SP SEP 95ANFLOOD END MUCK NONE FL0287 HIGHROCKDEPTH -2.0 LOWROCKDEPTH NA 0.0 -8 JUNSLOPE LOW D 155 NA APR HIGHSLOPE -8 N P FS NONE LOWPANDEPTH 95 HIGHPANDEPTH -2.0PANHARD NA 0 -9 NONEOTHERPH JUN 1.0 155 -8 2 NA FL0078 -9 D MARLEACH Y -8 VPRUNOFFCORCON FL0008CORSTEEL NONE NA NA 155 NA -9 -8 0 NA FS -9 2 -8 D VP 95 FL0159 Y 2.0 LOW MED JUL HIGH MED NOV 3.5 NA NA 155 -9 NA NA 0 FS -9 -8 1 NONE MED HIGH 95 -8 1.5 HIGH HIGH JUL OCT NA 3.5 UNDRAINED NONE MED HIGH -9 HIGH MW S NA C HIGH 0 -9 N 2 3.0 95 OCT JUN NA 155 NA NONE NA 5.0 HIGH HIGH LOW -8 SP HIGH C -8 N 155 NA NA NA -9 -8 MW -9 0 -8 2 B MED NA 155 MED N NA HIGH LOW NA NA -9 -9 -8 0 MED MED 2 HIGH -8 HIGH NA NA -9 LOW LOW HIGH -9 LOW 0 NA 2 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL049 49018 ha CASSIA 9 18 FL049 49019 ha 19 FL049 8 49020 ha FL049 20 49021 5 ha 21 6 FL049 49022 FL049 49023 ha 22 FL049 49024 9 ha 23 9 ha 24 9

E-53 Appendix E Soil Classification Database MUCK PITS HONTOON HOLOPAW HOLOPAW FINE SAND BRADENTON - FELDA - CHOBEE FELDA - - BRADENTON FLOODED FREQUENTLY ASSOCIATION, ELECTRA ELECTRA SAND FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0075 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUN FL0010 95ECOLCOMM SEP SMLRA 4 2.0 FL0348MUKIND D 3.5ANFLOOD FREQ N JULANFLOOD BEG P OCT 6 40ANFLOOD END LFS NONE HIGHROCKDEPTH 0.0 4 LOWROCKDEPTH 1.0 NA JUN -8SLOPE LOW C S SEP 155 NA HIGHSLOPE -8 N NONE SP LOWPANDEPTH 3 HIGHPANDEPTH PANHARD 4 NA 0 FREQ -9OTHERPH 155 -8 D 2 NA -9LEACH S Y P -8RUNOFF 21CORCON JUNCORSTEEL 155 NA NOV -8 -9 0 NA FL0027 -9 2 A -8 LOW HIGH HIGH MED DC0028 NA -9 FL0090 NA 0 95 -9 FS 2 LOW 0.0 MED HIGH JUN 1.0 LOW NOV NA NA LOW HIGH 95 VAR LOW HIGH 0.0 NONE NA NA 6.0 6 MUCK 95 D -2.0 Y JUN P NA APR 0.0 26 NA NA 155 NONE -9 -8 NA S -8 NA NA NA NA 155 NA 11 D -9 Y VP -8 0 -9 25 NA 155 2 -8 M NA NA -8 HIGH NA LOW MED -8 -9 HIGH S -9 0 8 NA NA NA -9 ND NA ND -9 0 2 HIGH NA MED HIGH HIGH UNDRAINED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL049 49025 ha WABASSO 8 25 FL049 49026 ha 26 FL049 9 49027 ha 27 6 FL049 49028 FL049 49029 ha FL049 28 49030 7 ha 29 11 ha 30 5

E-54 Soil Classification Database Appendix E KALIGA KALIGA MUCK FARMTON FARMTON FINE SAND WAUCHULA WAUCHULA FINE SAND MANATEE MUCKY FINE MANATEE SAND, DEPRESSIONAL FELDA FINE SAND, FINE SAND, FELDA DEPRESSIONAL FREQUENTLY FLOODED FREQUENTLY MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL049 49031SAND, FINE ha POMPANO 6 31 FL049 49032 ha 32 6 FL049 49033 ha 33 6 FL049 49034 FL049 49035 ha 34 8 FL049 49036 ha 35 8 ha 36 5 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0235 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND DANFLOOD FREQ YANFLOOD BEG P 21ANFLOOD END FREQ HIGHROCKDEPTH FL0298 95 LOWROCKDEPTH FS JUN -8SLOPE LOW S 155 NOV -2.0 HIGHSLOPE -8 1.0 LOWPANDEPTH JUN HIGHPANDEPTH DECPANHARD 0 -9OTHERPH FL0322 2 -9 7LEACHRUNOFF D Y 95CORCON NONE MK-FS VP 25CORSTEEL -2.0 NA NA NA 0.0 JUN NA MAR 155 -8 S HIGH HIGH -8 MED HIGH FL0153 10 NONE D -9 0 Y VP -9 2 25 FS FL0214 95 NA 0.5 NA 155 NA -8 FL0209 JUN 1.5 SEP NA S -8 FS LOW HIGH HIGH HIGH 95 0.5 NONE -9 JUN 4 0 SEP -9 1.5 2 D MUCK P N 6 NONE NA 95 -2.0 NA JUN NA APR 155 NA LOW HIGH 0.0 HIGH HIGH 4 -8 NONE S -8 D P N 6 NA 155 NA -9 11 0 -9 -8 2 D -8 S VP Y NA 25 NA 155 HIGH LOW NA NA HIGH HIGH -9 -8 -9 0 -8 2 S HIGH LOW NA HIGH MED NA -9 -9 HIGH 0 LOW HIGH 1 HIGH NA UNDRAINED

E-55 Appendix E Soil Classification Database SAND FL049 FL051 WATER BOCA 9 NO DATA UNKNOWN CODE BRADENTON BRADENTON SAND FINE LOAMY ST. LUCIE LUCIE ST. SAND FINE SAND, DEPRESSIONAL S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0261 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END FL0057 95 NONE HIGHROCKDEPTH FS LOWROCKDEPTH 6.0 NA -8 LOWSLOPE FL0232 S 155 NA 6.0 HIGHSLOPE -8 NA LOWPANDEPTH NA 95 HIGHPANDEPTH LFSPANHARD -9 0.5 0 -9OTHERPH 2 -9 1.5LEACH A JUN NRUNOFF E SEP NA NONE 3CORCONCORSTEEL 4 NA NA NA 155 NONE -8 NA NA D S 0 -8 NA N P -9 HIGH HIGH 13 MED HIGH -9 NA DC0038 NA NA 155 -9 FL0054 0 NA -8 -9 NA 2 S -8 0 NA -9 -9 NA NA -9 NA NA 100 NA NA -9 -9 NA 0 NA -9 NA NA S 2 HIGH NA -9 LOW NA LOW NA MED 95 NA -9 NA 0.5 NA JUN -9 NA NA FEB NA 1.5 LOW NA -9 NA HIGH NA NA -9 HIGH LOW NA NA NA NONE NA NA NA NA -9 -9 9 -9 -9 NA NA NA D -9 -9 NA N P 6 NA -9 M NA NA NA 155 NA -9 NA NA NA -9 -9 -9 -9 40 S 24 -9 NA NA -9 -9 NA NA -9 NA NA NA NA NA NA -9 NA 0 -9 NA 2 NA MED HIGH NA HIGH MED MUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT ha BASINGER FINE 6 37 ha 38 10 ha 39 8 ha 45 12 ha 98 12 ha 99 1 he 1 8 MUIDSTSSAID FL049 49037 FL049 49038 FL049 49039 FL049 49045 FL04 49098 49099 51001

E-56 Soil Classification Database Appendix E PINEDA FINE SAND RIVIERA FINE SAND MALABAR MALABAR SAND IMMOKALEE IMMOKALEE SAND WABASSO WABASSO SAND OLDSMAR SAND LIMESTONE SUBSTR. LIMESTONE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL051 51002 heSAND, PINEDA 7 2 FL051 51004 he 8 FL051 4 51006 FL051 he 51007 8 6 FL051 51008 he 8 7 FL051 51009 FL051 he 51010 7 8 he 7 9 he 7 10 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0414 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND DANFLOOD FREQ YANFLOOD BEG P FL0067 26 95ANFLOOD END S NONE HIGHROCKDEPTH 0.5 LOWROCKDEPTH FL0075 NA 80 1.5SLOPE LOW S 155 NA JUN HIGHSLOPE 40 SEP LOWPANDEPTH 95 FL0058 HIGHPANDEPTH S 0.5 4PANHARD 0 -9 1.5OTHERPH JUN D 1 -9 SEPLEACH N NONE FL0123 6 PRUNOFF 95CORCON 0.5 SCORSTEEL FL0064 4 NA JUN NA 1.5 NONE -8 SEP 155 NA NA D S -8 N P 6 FL0080 LOW HIGH 95 NONE LOW HIGH NA 0.0 155 JUN S 4 -9 NA -8 0 NOV 1.0 -9 2 D S -8 N P NONE 6 95 JUN 0.0 NA DEC 155 NA 1.0 NA FS -9 NA -8 0 -9 NONE 6 2 -8 S LOW HIGH D MED HIGH 95 JUN Y NOV 0.0 NA P 26 155 NA NONE 1.0 NA FS -9 HIGH NA LOW 0 -9 HIGH -8 7 MED 2 D -8 S Y NA 155 26 NA P HIGH NA MED NA HIGH HIGH -8 -9 6 -9 0 -8 D S 2 155 Y NA HIGH 26 NA P LOW NA LOW NA HIGH -9 -8 -9 HIGH 0 -8 LOW 2 S HIGH NA HIGH NA HIGH -9 -9 LOW LOW HIGH 0 NA 2 NA

E-57 Appendix E Soil Classification Database GATOR GATOR MUCK POMPANO POMPANO SAND BASINGER SAND MYAKKA MYAKKA SAND WABASSO SAND, WABASSO SUBSTR. LIMESTONE GENTRY FINE SAND, GENTRY DEPRESSIONAL FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL051 51012 he WINDER 7 12 FL051 51013 he 13 6 FL051 51014 he 14 8 FL051 51015 FL051 51017 he 15 FL051 51018 8 he FL051 17 51019 7 he 18 7 he 19 5 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0076 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0207 95ECOLCOMM DEC FSMLRA 7 -2.0MUKIND D 0.0ANFLOOD FREQ Y JUNANFLOOD BEG P JAN 26ANFLOOD END NONE HIGHROCKDEPTH 8 LOWROCKDEPTH NA -8SLOPE LOW D S 155 NA HIGHSLOPE -8 Y FL0419 NONE 25 VP LOWPANDEPTH HIGHPANDEPTH PANHARD 95 NA S 0 -9OTHERPH 155 -8 0.5 2 NA -9LEACH S -8 1.5RUNOFF JUN SEPCORCONCORSTEEL NA FL0059 -9 0 NA -9 2 4 FL0063 NONE D LOW HIGH N P LOW 6 HIGH 95 NA FL0032 S 0.5 UNDRAINED NA JUN 155 1.5 LOW HIGH NA SEP 80 HIGH MED FL0415 S 95 40 0.0 S JUN NONE 1.0 FEB 4 -9 0 -9 NA D NONE 2 95 N 0.0 P JUN 6 OCT S 1.0 NA NA 155 9 NONE NA -8 HIGH D MED Y MED -8 P 95 JUN S MED -2.0 26 APR 155 NA NONE 0.0 MUCK NA -8 5 -9 NA -8 D 0 -9 S 2 Y 26 P 155 NA NA NA HIGH NA MED -9 -8 HIGH -9 HIGH 11 0 -8 D 2 S 155 25 HIGH Y NA NA VP HIGH HIGH NA MED NA -9 -8 -9 MED 0 -8 HIGH 2 S HIGH NA MED UNDRAINED -9 HIGH LOW -9 HIGH 0 HIGH NA 1

E-58 Soil Classification Database Appendix E RIVIERA SAND, SUBSTR. LIMESTONE HOLOPAW SAND, HOLOPAW SUBSTR. LIMESTONE POMELLO FINE SAND, POMELLO FINE PCT SLOPES 5 TO 0 VALKARIA VALKARIA SAND HOLOPAW HOLOPAW SAND MUCK S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 90 ENDSHWT MUCK DURSHWT FL0071 -1.0HYDRIC 0.0HYDROGRPDRAINAGE JUN SECOLCOMM JAN FL0027 95MLRA 8MUKIND 0.0 DANFLOOD FREQ FL0126 Y 1.0ANFLOOD BEG VP JUN 25ANFLOOD END S NOV NONE HIGHROCKDEPTH 95 FL0078 LOWROCKDEPTH 0.0 NA 6 -8SLOPE LOW S 155 NA 1.0 HIGHSLOPE JUN -8 D SEP LOW YPANDEPTH P NONE 26 HIGH FSPANDEPTH 95PANHARD 2.0 0 -9OTHERPH NA JUL 4 2 -9 3.5LEACH NONE NOV 155 -8 NA D SRUNOFF FL0453 -8 Y PCORCON 26CORSTEEL NONE NA NA DRAINED 155 5 -9 0 NA -8 -9 2 C S -8 LOW N 3 HIGH MW NA S 95 MED HIGH 0.0 NA FL0421 NA 155 JUN NOV NA 1.0 -9 -8 0 -9 2 S LOW -8 HIGH NA NONE HIGH MED NA -9 HIGH HIGH 6 0 -9 HIGH 5 MED D NA P 95 Y S 26 0.0 JUN NA NOV NA 155 HIGH MED 1.0 NA LOW HIGH NONE 80 50 S -9 6 -9 0 D NA P 2 26 Y HIGH 155 NA NA LOW HIGH NA MED 70 40 S -9 NA -9 HIGH 0 LOW 2 HIGH NA MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL051 51020 he OKEELANTA 5 20 FL051 51021 he 21 7 FL051 51022 FL051 he 51024 22 7 he 24 9 FL051 51026 he 26 FL051 51027 7 he 27 7

E-59 Appendix E Soil Classification Database CHOBEE FINE SANDY LOAM, DEPRESSIONAL SUBSTR., LIMESTONE HOLOPAW SAND, HOLOPAW DEPRESSIONAL HALLANDALE SAND OLDSMAR SAND, SUBSTR. LIMESTONE DEPRESSIONAL S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT S DUR FL0268SHWT -2.0HYDRIC 0.0HYDROGRP JUNDRAINAGE FEBECOLCOMM 9MLRA FL0391 95MUKIND D SANFLOOD FREQ Y 0.5ANFLOOD BEG VP 25 1.5ANFLOOD END JUN NONE HIGHROCKDEPTH SEP LOWROCKDEPTH NA 40SLOPE LOW S 155 NA 4 24 HIGHSLOPE FL0065 LOWPANDEPTH D HIGH NPANDEPTH P NONE 6 95PANHARD 0 -9OTHERPH 0.5 2 S FL0264 -9LEACH NA 1.5 JUN 72 155RUNOFF NA SEP SCORCON 40CORSTEEL NA 95 NA -2.0 4 FL0450 NONE S -9 0 JUN D 0.0 MED -9 HIGH 2 MAR N P MED HIGH 9 NA NA 155 NONE 20 NA NA 10 7 S 95 -2.0 LOW HIGH D JUN HIGH Y LOW VP MAR 0.0 FSL 25 NA -9 155 0 -9 NONE NA -8 2 -8 S NA 10 NA D HIGH MED VP Y HIGH -9 LOW 25 0 -9 155 NA 2 NA 79 NA HIGH NA LOW 40 S HIGH MED -9 -9 0 2 HIGH NA LOW HIGH NA LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL051 51028 he BOCA SAND, 6 28 FL051 51029 he 29 8 FL051 51023 he 23 FL051 8 51033 he 33 FL051 51034 6 he 34 6

E-60 Soil Classification Database Appendix E UDORTHENTS PAHOKEE PAHOKEE MUCK JUPITER SAND FINE SUBSTR., DEPRESSIONAL SUBSTR., UDIFLUVENTS SAND, RIVIERA LIMESTONE FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0219 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEP FL0420MLRA 4 95 FSMUKIND DANFLOOD FREQ 2.5 NANFLOOD BEG P 3.5 12 JULANFLOOD END FL0422 NONE OCT HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW 95 4 S 155 NA S HIGHSLOPE -8 -2.0 NA LOWPANDEPTH N NONE 0.0 HIGHPANDEPTH NA JUN MW MARPANHARD 0 -9OTHERPH 2 -9 NALEACH 155 -8 NARUNOFF M 10 -8CORCON NONE D FL0053CORSTEEL VP Y NA 25 NA -9 0 FL0072 -9 NA 2 155 LOW HIGH NA 95 80 LOW HIGH FS S 0.5 40 FL0089 NA JUN 1.5 NOV NA MED MED -9 95 0 -9 HIGH HIGH MUCK -1.0 2 NONE JUN FEB 6 0.0 D NA P GR-S 12 NA N NONE 95 2.0 LOW HIGH NA NA HIGH HIGH NA 155 3.0 NA 9 NONE 20 D 8 S VP 25 Y 155 NA NA -9 -9 51 NA 0 -9 W NA 1 S 36 N 155 NA NA NA HIGH NA MED HIGH -8 LOW -9 -9 0 -8 M 1 HIGH NA LOW HIGH MED DRAINED -9 NA -9 0 MED LOW MED 2 NA LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL051 51037 he TUSCAWILLA 8 37 FL051 51039 he 39 11 FL051 51042 he 42 6 FL051 51044 FL051 51045 he 44 8 FL051 51047 he 45 4 he 47 11

E-61 Appendix E Soil Classification Database CHOBEE FINE SANDY CHOBEE FINE SANDY DEPRESSIONAL LOAM, TERRA CEIA TERRA CEIA MUCK ADAMSVILLE ADAMSVILLE SAND FINE MALABAR FINE FINE MALABAR SAND, HIGH DELRAY SAND, DELRAY DEPRESSIONAL SUBSTR. MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL051 51049 he AQUENTS, ORGANIC 11 49 FL051 51050 he 6 50 FL051 51051 he 51 8 FL051 51053 FL051 51056 he 53 9 FL051 51057 he 56 4 he 57 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT ND 1.0HYDRIC 3.5HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND NAANFLOOD FREQ NANFLOOD BEG 95 SP NA SANFLOOD END FL0299 NONE -2.0 HIGHROCKDEPTH LOWROCKDEPTH 0.0 NA -8SLOPE LOW JUN M 155 NA HIGHSLOPE -8 MAR LOWPANDEPTH 10 HIGHPANDEPTH DPANHARD FL0390 0 -9OTHERPH 95 Y 2 VP -9 NONE 25LEACH FS 0.5RUNOFF 1.5CORCON JUN NACORSTEEL SEP 155 -8 NA FL0036 NA S NA -8 4 95 LOW NONE HIGH D FS 1.5 FL0031 HIGH HIGH P -9 0 N 6 3.5 -9 JUN 2 NOV NA FL0040 155 NA -8 NA 95 NONE MUCK S -2.0 6 NA -8 JUN 0.0 C APR LOW HIGH SP LOW MED N 6 NONE -9 FSL 0 -9 NA 155 2 90 -2.0 NA JUN -8 11 MAR 0.0 S NA -8 D NONE VP NA Y HIGH LOW 24 LOW HIGH 155 NA -9 NA 0 -9 10 -8 2 52 S VP D NA MED Y 25 NA HIGH 155 NA MED LOW NA -9 -9 0 -8 1 -8 S HIGH NA LOW DRAINED MED MED -9 NA -9 0 HIGH LOW 1 NA HIGH HIGH

E-62 Soil Classification Database Appendix E PINEDA SAND, DEPRESSIONAL MALABAR SAND, MALABAR DEPRESSIONAL MYAKKA SAND, MYAKKA DEPRESSIONAL DEPRESSIONAL MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL051 51058 he SAND, DEPRESSIONAL OLDSMAR 6 58FINE SAND, WINDER FL051 51059 he 59 6 FL051 51060 he 60 6 FL051 51061 he 61 FL051 51062 6 he 62 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT S DURSHWT FL0282 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW S 155 NA HIGHSLOPE -8 LOWPANDEPTH FL0283 95 HIGHPANDEPTH FSPANHARD -2.0 0 -9OTHERPH 2 -9 0.0LEACH JUNRUNOFF MARCORCONCORSTEEL 10 NA FL0307 NA D Y VP NONE 25 95 LOW HIGH S -2.0 HIGH MED NA 0.0 FL0286 JUN 155 -8 MAR NA S -8 10 95 NONE -2.0 -9 0 D S -9 FL0411 VP 2 Y JUN 25 MAR 0.0 NA NA 155 NA -8 NA 10 NONE S -8 LOW HIGH -2.0 95 LOW HIGH VP D MAR JUN 25 Y S 0.0 -9 0 -9 NA 2 155 NA NONE -8 10 NA S -8 NA HIGH MED VP HIGH HIGH D 25 Y -9 0 -9 NA 155 2 NA NA -8 HIGH NA LOW -8 S LOW HIGH -9 -9 0 2 HIGH NA LOW HIGH LOW NA

E-63 Appendix E Soil Classification Database DANIA MUCK LAUDERHILL MUCK MARGATE MARGATE SAND PLANTATION PLANTATION MUCK HALLANDALE SAND, DEPRESSIONAL OUTCROP COMPLEX S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 50 ENDSHWT FSSHWT FL0053 DUR 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND DANFLOOD FREQ YANFLOOD BEG P 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA 20SLOPE LOW C 155 NA HIGHSLOPE 0 FL0417 95 LOWPANDEPTH S HIGHPANDEPTH -2.0PANHARD 0 -9 0.0OTHERPH 1 -9 JUNLEACH APRRUNOFFCORCONCORSTEEL 11 NA FL0095 D NA Y NONE 25 VP 90 LOW HIGH MUCK -2.0 LOW FL0094 HIGH NA 20 0.0 155 JUN NA S APR 7 FL0069 S 95 -1.0 11 -9 0 NONE -9 JUN D 2 1.0 FL0055 FEB Y VP 24 MUCK 95 -2.0 NA NA NONE 155 JUN 40 NA NA APR 0.0 9 S HIGH HIGH 20 D HIGH LOW MUCK P 16 NONE Y -2.0 95 NA -9 JUN 155 0 APR -9 NA 40 1 11 0.0 D NONE S 24 VP 20 Y NA NA 155 DRAINED LOW HIGH NA 40 HIGH -9 MED 0 -9 11 2 NA S 20 VP D 25 NA Y HIGH 155 MED NA HIGH NA -9 MED 20 -9 0 DRAINED 2 HIGH 8 NA LOW S HIGH MED UNDRAINED -9 -9 HIGH 0 LOW HIGH 1 NA MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL051 51063OCHOPEE - ROCK he - JUPITER 7 63 FL051 51064 he 64 6 FL051 51065 he 65 FL051 5 51066 FL051 51067 he 66 7 FL051 51068 he 67 4 he 68 4

E-64 Soil Classification Database Appendix E ST. LUCIE SAND, LUCIE ST. 8 PCT 0 TO SLOPES 8 PCT SLOPES WATER TO SAND, 0 PAOLA ADAMSVILLE ADAMSVILLE SAND VARIANT MUCK S5ID 1S5ID 1COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 60 ENDSHWT MUCKSHWT FL0458 DUR -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM APRMLRA 11MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END MUCK NONE FL0458 HIGHROCKDEPTH 90 LOWROCKDEPTH NA -8 LOWSLOPE -2.0 FL0082 FS C 155 NA HIGHSLOPE -8 0.0 LOWPANDEPTH JUN 95 HIGHPANDEPTH APR 2.5PANHARD 0 -9OTHERPH 1 DC0038 11 -9 3.5 JUNLEACH FL0056 NOV DRUNOFF NA Y VPCORCON NONE 25CORSTEEL NA 6 100 DRAINED S -9 NONE NA C 155 -8 NA SP NA N S -9 11 LOW NA -8 95 HIGH FL0057 LOW HIGH 6.0 NA 155 NA NA NA 6.0 -8 NA -9 0 S -9 -8 1 -9 NA NA DRAINED NONE NA NA S NA NA -9 -9 0 -9 NA NA 95 E A 5 NA N 3 6.0 LOW HIGH -9 NA HIGH LOW M -9 NA NA 6.0 NA 154 NA MED LOW NONE -8 NA HIGH MED S -8 -9 -9 -9 -9 NA -9 E A NA -9 N NA 3 NA 0 -9 NA 8 NA 154 NA NA NA LOW HIGH -8 LOW HIGH -8 S NA -9 -9 0 8 NA HIGH LOW LOW MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL051 51069 MUCKS he DENAUD-GATOR 5 69 DENAUD FL051 51070 he FL051 70 5 51073 he 73 9 FL051 51099 FL055 55001 he 99 1 hi FL055 1 55002 10 hi 2 10

E-65 Appendix E Soil Classification Database PLACID FINE SAND, PLACID DEPRESSIONAL TAVARES SAND, TAVARES 5 PCT 0 TO SLOPES DAYTONA SAND, DAYTONA 5 PCT 0 TO SLOPES DUETTE SAND, DUETTE PCT SLOPES 5 TO 0 DEPRESSIONAL MUIDSTSSAIDMUSYM34567 CNTYABBRLSPOSCODE69996 NAMEMAPUNIT FL055 55003 SAND, hi BASINGER FINE FL055 55004 hi FL055 55005 hi FL055 55006 hi FL055 55007 hi COMPPCT 19595959595 LOW-9-9-9-9-9 ENDNANANANANA HIGH-2.04.03.53.5-2.0 DUR1055710 LOW00000 HIGH25552 1S5ID COMPPCT 1SURFTEXT SHWT LOWSHWT SHWT BEG ENDSHWT FSSHWT FL0261HYDRICYNNNY 0.0HYDROGRPDABAD DRAINAGEVPMWMWMWVP JUNECOLCOMM2533425 MARMLRAMUKINDSSSSS ANFLOOD FREQANFLOOD BEGANFLOOD NONE HIGHROCKDEPTH FL0323 LOWROCKDEPTH FS NA -8SLOPE 154SLOPE -8 6.0PANDEPTH JUN HIGHPANDEPTH OCTPANHARDOTHERPHNANANANANA -9 FL0230LEACHRUNOFFCORCON NONE SCORSTEEL NA 5.0 JUL NA NOV 155 -8 HIGH FL0021 HIGH -8 MED HIGH NONE -9 S JUN 6.0 DEC FL0287 NA 155 NA -8 -8 MED LOW NONE LOW HIGH -9 FS JUN MAR 0.0 NA 155 NA -8 NONE MED LOW -8 HIGH MED -9 155 NA NA HIGH LOW -8 HIGH LOW -8 -9 LOW NA HIGH HIGH HIGH

E-66 Soil Classification Database Appendix E SATELLITE SATELLITE SAND FELDA FELDA FINE SAND BASINGER FINE SAND ORSINO SAND, 5 PCT 0 TO SLOPES MYAKKA MYAKKA SAND FINE ASTATULA SAND, 0 TO 8 0 TO SAND, ASTATULA PCT SLOPES SAND OPC 99 9595959595 19595 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG ENDSHWT S DURSHWT FL0058 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEP FL0019MLRA 4 SMUKIND 6.0 DANFLOOD FREQ N 6.0ANFLOOD BEG P NA 6ANFLOOD END NA NONE HIGHROCKDEPTH LOWROCKDEPTH NA -9 -8SLOPE LOW S 154 NA HIGHSLOPE -8 A FL0059 N LOWPANDEPTH NONE E HIGHPANDEPTH 2PANHARD 0 -9 FL0103OTHERPH NA 2 -9 S 0.5 154LEACH -8 NA SRUNOFF 1.5 -8 JUNCORCON SEPCORSTEEL NA NA 4.0 -9 0 4 S -9 8 5.0 FL0063 JUN NONE MED D HIGH DEC N HIGH HIGH P 6 NA FL0127 NONE NA NA 155 7 NA -8 LOW HIGH FL0102 A HIGH S LOW -8 N 0.0 MW 1 JUN 1.0 FS NA FEB 155 NA -9 0 -8 -9 NONE 2 S -8 0.0 JUL MAR 1.0 FS NA 9 NONE NA -9 MED HIGH D 0 -9 HIGH P Y HIGH 5 1.5 JUN NOV 154 NA 26 NONE 3.5 S NA NA LOW HIGH NA 9 -8 MED LOW -8 D S P Y 154 NA 26 NA -9 -8 6 -9 0 -8 2 C S 154 SP N HIGH NA NA HIGH 3 MED NA HIGH NA -9 -8 -9 0 LOW HIGH -8 1 S MED HIGH NA NA -9 LOW HIGH -9 LOW MED 0 NA 2 NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL055 55008 hi IMMOKALEE 8 8 FL055 55009 hi 10 9 FL055 55010 FL055 55011 hi 8 10 hi 9 11 FL055 55012 FL055 55013 FL055 55014 hi 12 7 hi 13 7 14 hi 9

E-67 Appendix E Soil Classification Database PINEDA SAND GATOR GATOR MUCK BRIGHTON BRIGHTON MUCK HONTOON HONTOON MUCK SAMSULA SAMSULA MUCK KALIGA KALIGA MUCK MALABAR MALABAR SAND FINE VALKARIA VALKARIA SAND FINE FINE SAND FINE COMPPCT 1959595959090909095 P P VPVPVPVPVPP LOW-9-9-9-9-9-9-9-9-9 ENDNANANANANANANANANA S S SSSSSS 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG ENDSHWT FS DURSHWT FL0232 0.5HYDRIC 1.5HYDROGRPDRAINAGEP JUNECOLCOMM SEP FL0126MLRA 4 FSMUKINDS D 0.0ANFLOOD FREQ N FL0123ANFLOOD BEG 1.0 12 JUNANFLOOD SEP NONE HIGHROCKDEPTH FS FL0209 LOWROCKDEPTH NA -8 4SLOPE LOW 0.0 155 HIGHSLOPE -8 1.0 FL0092 JUN DPANDEPTH NOV Y NONE HIGH 26PANDEPTH MUCK FL0090PANHARD 0OTHERPH -2.0 2 -9 NA 6 JUNLEACH 0.0 NONE 155 -8 APR MUCKRUNOFF D FL0257 -8 YCORCON 26 -2.0CORSTEEL JUN NA MUCK NONE APR 0.0 FL0415 NA NA 154 11 0 -8 -9 2 D NONE LOW -8 HIGH -2.0 25 MUCK Y JUN FL0080 LOW APR HIGH 0.0 NA NA 11 155 NONE NA MUCK 0 -8 D -9 25 -1.0 2 JAN Y HIGH HIGH DEC -8 HIGH MED NA NONE 1.0 155 NA 11 S NA -8 LOW HIGH D 25 JUN -2.0 APR 0 -9 -8 HIGH NONE LOW Y 1 155 NA 0.0 NA 12 HIGH LOW DRAINED -8 HIGH NONE JUN NOV -9 0.0 HIGH 0 25 DRAINED -8 D 1 155 Y NA HIGH NA DRAINED MED 1.0 HIGH HIGH 11 DRAINED -8 -9 HIGH 0 25 -8 LOW 155 D HIGH 1 DRAINED NA NA HIGH Y 6 NA HIGH LOW -8 HIGH -9 HIGH 8 155 0 -8 NA NA D 1 Y HIGH HIGH LOW HIGH -8 -9 NA -8 0 HIGH 1 HIGH LOW LOW -9 NA 0 2 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL055 55015 hi BRADENTON 8 15 FL055 55016 hi 16 7 FL055 55017 FL055 55018 17 hi 7 FL055 55020 FL055 18 hi 55021 5 FL055 20 55022 hi 5 FL055 55023 21 hi FL055 5 55024 22 hi 5 23 hi 5 24 hi 7

E-68 Soil Classification Database Appendix E FELDA FINE SAND, FELDA DEPRESSIONAL OLDSMAR FINE SAND POMONA SAND ARCHBOLD SAND, PCT SLOPES 5 TO 0 TEQUESTA TEQUESTA MUCK DEPRESSIONAL S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT MK-SSHWT DUR FL0494 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 21ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH FL0077 NA MUCK -8SLOPE LOW 90 S 154 NA HIGHSLOPE -8 -2.0 LOWPANDEPTH HIGHPANDEPTH 0.0 JAN FL0434PANHARD S DEC 0 -9OTHERPH 2 -9LEACH 12 95RUNOFF 3.5CORCON DCORSTEEL Y 6.0 VP NA JUN NONE 25 NOV NA FL0007 NA LOW 6 HIGH 155 -8 NA HIGH HIGH S FL0067 S NONE -8 A MW 95 N 3 0.5 FL0298 JUN -9 0 1.5 SEP NA -9 154 2 S NA -8 S 95 -8 0.5 NONE JUN NA SEP 4 1.5 DRAINED P -9 D LOW HIGH FS 0 -9 NONE N LOW MED 5 95 -2.0 6 JUN NA DEC NA 155 1.0 4 NA NA NONE -8 P D LOW HIGH S -8 N MED LOW 6 155 NA NA 7 -9 -8 0 -9 VP D -8 2 NA S Y 154 NA 25 NA NA LOW HIGH -9 HIGH HIGH -8 -9 0 NA -8 2 S HIGH NA LOW HIGH MED -9 NA -9 0 HIGH LOW 2 HIGH NA HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL055 55019 hi HICORIA MUCKY SAND, 6 19 FL055 55026 hi 26 5 FL055 55028 28 hi 9 FL055 55029 FL055 55030 29 hi FL055 8 55031 30 hi 8 31 hi 6

E-69 Appendix E Soil Classification Database POMELLO SAND, 5 PCT 0 TO SLOPES SANIBEL SANIBEL MUCK TAVARES-BASINGER-SANIBEL TAVARES-BASINGER-SANIBEL COMPLEX, ROLLING BASINGER, ST. JOHNS AND JOHNS BASINGER, ST. SOILS PLACID VERY STEEP VERY MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL055 55032 hi ARENTS, 11 32 FL055 55033 hi 7 33 FL055 55034 34 hi 9 FL055 55035 FL055 55036 35 hi 5 36 hi 9 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT VAR DURSHWT FL0085 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NA FL0063 FS 60MLRA -9MUKIND 0.0 NAANFLOOD FREQ N 1.0ANFLOOD BEG W NAANFLOOD END JUN NONE HIGHROCKDEPTH FEB LOWROCKDEPTH NA 9 -8SLOPE LOW M 155 NA D HIGHSLOPE -8 LOW YPANDEPTH NONE P 10 HIGHPANDEPTH FL0021PANHARD 45 -9OTHERPH NA 65 S -9 60LEACH 154 -8 NA URUNOFF 0.0 -8CORCON 6.0CORSTEEL JUN NA DEC NA 0 -9 2 -9 7 MED HIGH NONE C LOW LOW N 4 NA MW-P NA FL0073 NA HIGH HIGH 154 NA MED HIGH -8 C -8-8 FL0078 90 MUCK -1.0 0.0 5 -9 JUN 8 -9 APR S 90 NONE NA 2.0 NA 11 JUN 3.5 HIGH LOW D FEB VP LOW HIGH Y 25 NONE NA 155 NA 9 -8 -8 SP S C 3 N 154 NA NA -9 0 -9 -8 2 -8 S NA LOW HIGH UNDRAINED LOW HIGH NA -9 0 -9 5 MED MED NA LOW HIGH

E-70 Soil Classification Database Appendix E ANCLOTE - BASINGER FINE SANDS, - BASINGER FINE SANDS, ANCLOTE FLOODED FREQUENTLY ARENTS, ARENTS, ORGANIC SUBSTR. SMYRNA SMYRNA SAND EAUGALLIE EAUGALLIE SAND FINE DEPRESSIONAL S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT S DURSHWT FL0286 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP FL0154 25ANFLOOD END 95 NONE HIGHROCKDEPTH FS 0.5 LOWROCKDEPTH NA -8SLOPE LOW FL0091 1.5 S 154 NA JUN HIGHSLOPE -8 SEP LOWPANDEPTH FL0083 95 HIGHPANDEPTH 4 SPANHARD 0.5 0 -9OTHERPH 2 -9 D 1.5 JUNLEACH N SEP P NONERUNOFF 6 95CORCON 2.0 FSCORSTEEL NA JUN FL0316 NA 3.0 4 NOV 154 NA -8 NA NONE S D -8 N P LOW HIGH 6 NONE LOW HIGH 6 NA -9 155 0 NA -9 NA 55 -8 2 N 0.0 S SP FS -8 JUN NA OCT 0.5 NA 155 NA NA NA -8 FREQ -9 0 -9 M -8 LOW HIGH 2 HIGH MED 5 NA D -9 NA VP Y 0 -9 HIGH MED 21 2 HIGH 154 HIGH JUN NOV NA LOW -8 NA HIGH HIGH HIGH -8 C -9 -9 0 2 HIGH NA HIGH HIGH MED NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL055 55037 SAND, hi MALABAR 6 37 FL055 55038 hi 38 8 FL055 55039 FL055 55040 39 hi 8 40 hi 11 FL055 55041 41 hi 6

E-71 Appendix E Soil Classification Database PAOLA-BASINGER PAOLA-BASINGER SANDS, ROLLING SATELLITE-BASINGER- COMPLEXURBAN LAND URBAN LAND COMPLEX, 0 TO 8 PCT SLOPES 8 TO 0 COMPLEX, MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL055 55042 LAND hi ASTATULA-URBAN 11 42 FL055 55043 FL055 hi 11 55044 43 11 44 hi FL055 55045 10 45 hi S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 70 ENDSHWT S DURSHWT FL0019 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND NAANFLOOD FREQ NANFLOOD BEG E NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C 154 NA HIGHSLOPE DC0035 -8 95 LOWPANDEPTH FL0102 VAR HIGHPANDEPTH 2.0PANHARD 2.0 0 -9OTHERPH 50 8 -9 S NALEACH NA 1.0RUNOFFCORCON 3.5 -9CORSTEEL JUN NA NA NOV NA N NONE NA NA FL0056 6 NA HIGH LOW NONE HIGH LOW NA NA N 154 -8 SP NA M -8 65 S NA 154 0.0 NA -8 6.0 C -9 JUN -8 0 -9 OCT 8 NONE -9 5 A NA 0 -9 2 NA 3 E-P N MED HIGH ND NA ND NA NA 154 HIGH LOW NA -8 MED LOW C -8 -9 8 -9 12 NA HIGH NA MED HIGH LOW

E-72 Soil Classification Database Appendix E OPC 9 000 0 195 -9-9-9-9-9-9 1000000 HIGH0.0 DUR9 NANANANANANA -9-9-9-9-9-9 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT 1S5ID COMPPCT FL055 55046 FLOODED 1SURFTEXT FREQUENTLY MUCK, hi KALIGA 5 46SHWT LOWSHWT WATER BEGSHWT ENDSHWT ARENTS MUCK NANANANANANA SHWT FL0486 SAMSULAHYDRIC CANDLER 1.0HYDROGRPDRAINAGEVP JUN MEADE FORT ECOLCOMM FEB IMMOKALEE MLRA155 MUKIND DANFLOOD FREQ YANFLOOD BEG 25ANFLOOD END FREQ HIGHROCKDEPTH LOWROCKDEPTH JUN FL055 -8 LOWSLOPE 55099 S NOV HIGHSLOPE -8 FL057 LOWPANDEPTH 57004 hi 99 1 HIGHPANDEPTH FL057PANHARD 57005 0 -9 NAOTHERPH DC0038 1 -9LEACH 4 hl OUT 0 FL057RUNOFF 57007CORCON NA -9CORSTEEL NA OUT NA FL057 hl NA NA 5 57018 0 NA -9 NA LOW HIGH OUT NA HIGH HIGH NA NA FL057 hl NA NA 7 57021 NA NA 0 -9 OUT NA NA NA NA NA NA NA -9 M -9 hl NA NA 18 NA NA -9 0 NA NA NA NA OUT NA -9 NA -9 -9 -9 NA -9 -9 NA NA NA NA NA -9 NA NA -9 hl NA 21 NA -9 -9 -9 NA -9 0 -9 NA NA NA NA NA NA NA NA NA NA NA NA NA -9 -9 NA -9 NA NA -9 -9 -9 -9 NA NA NA NA NA NA NA NA NA NA -9 -9 NA -9 NA -9 NA -9 -9 NA NA NA NA NA NA NA NA -9 -9 NA NA NA -9 -9 NA -9 NA NA -9 NA NA NA NA NA -9 -9 -9 -9 NA NA NA NA NA NA

E-73 Appendix E Soil Classification Database FL057 FL057 FL057 FL057 FL057 7 FL057 FL057 FL05 7 MUIDSTSSAID FL05 57025 57027 57029 57033 57039 57041 57046 57047 57050 SHWT LOW-9-9-9-9-9-9-9-9-9 NANANANANANANANANA MUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT 1S5ID COMPPCT 1 1SURFTEXT hl LAKE 0 25 HIGHSHWT MALABARSHWT MYAKKA BEGSHWT hl 27 0 0 ENDSHWT ONA NA DURSHWT OUT -9 ARENTSHYDRIC NA 0HYDROGRP OUT POMELLO 29DRAINAGE hl NA JOHNS ST. -9 0ECOLCOMM NAMLRA SEFFNER -9 NA OUTMUKIND NA SLICKENS NA NA 33ANFLOOD FREQ 0 hl NAANFLOOD BEG -9 0 -9 NA OUTANFLOOD END NA 39 NA NA HIGHROCKDEPTH NA NA hl OUT LOWROCKDEPTH NA NA NA 0 0 -9SLOPE LOW NA NA NA NA NANANANANANANANANA NA -9 -9 HIGHSLOPE -9 41 NA NA OUT NA LOWPANDEPTH NA hl -9 NA 0 NA NA NA HIGHPANDEPTH NA -9 0 -9PANHARD NA NA -9 -9 NAOTHERPH -9 NA -9 NA -9 OUTLEACH NA NA 46RUNOFF NA 0 NA NA NA -9 -9 hl -9 -9 NA NACORCON -9 -9 -9 NA NA NA -9 NACORSTEEL 0 NA NA OUT NA NA NA NA NA NA 47 NA -9 NA -9 NA -9 NA 0 -9 NA -9 NA hl -9 NA -9 -9 NA OUT NA NA NA NA NA NA NA NA -9 0 NA 50 -9 NA NA NA NA NA -9 -9 NA -9 NA NA NA NA NA -9 -9 hl NA NA -9 0 NA -9 NA -9 -9 0 NA -9 NA -9 -9 NA NA NA NA NA NA NA NA NA NA -9 NA NA -9 NA 0 NA -9 -9 NA -9 NA -9 NA -9 NA -9 NA NA NA NA NA NA NA NA NA -9 NA NA NA NA -9 -9 -9 -9 -9 NA NA -9 NA NA NA NA NA NA NA -9 -9 -9 NA -9 -9 -9 NA NA NA NA -9 -9 NA -9 -9 NA NA NA NA NA NA NA

E-74 Soil Classification Database Appendix E FINE SAND HTLW99999. 0.5 VP LOW-9-9-9-9-93.0 LOW 1S5ID 1COMPPCT 1SURFTEXT HIGHSHWT SHWT BEGSHWT 0 ENDSHWT NA DURSHWT OUT -9HYDRICHYDROGRPDRAINAGENANANANANASP NA 0 NA OUTECOLCOMM NAMLRA -9 -9MUKIND NAANFLOOD FREQ NA NA OUTANFLOOD BEG NA NA NA 0ANFLOOD END -9 NA HIGHROCKDEPTH -9 OUT NA LOWROCKDEPTH NA NA NA NA -9SLOPE LOW NA NA NA NA NA HIGHSLOPE -9 0 OUT NA LOWPANDEPTH -9 -9 HIGHPANDEPTH NA NA NA NA FL0060PANHARD NA -9 NA NA NA NA -9 -9OTHERPH NA -9 -9 -9 0LEACHNANANANANAHIGH FS NA -9 -9RUNOFF NA NA NACORCON NA NA NA -9CORSTEEL NA NA NA -9 -9 90 NA -9 -9 1.5 JUN NA NA -9 NA -9 NOV NA NA NA NA NA NA NA NA -9 C NA NA NA -9 -9 6 NA N -9 -9 -9 NA 2 NA NA NA NONE NA -9 NA NA NA -9 -9 NA -9 -9 NA -9 S 155 NA -8 NA NA FL0062 -8 -9 NA -9 NA NA -9 -9 NA NA 0 -9 LFS NA NA NA 5 -9 NA NA 90 JUN NA 0.0 NA NA OCT MED LOW MED D 5 Y NONE 26 NA 155 NA S -8 -8 -9 0 -9 2 NA NA HIGH HIGH HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL057 57052 hl SMYRNA 0 52 WABASSO FL057 57057 WINDER WINDER hl 57 0 FL057 ZOLFO 57059PCT SLOPES 5 TO SAND, 0 FINE CANAVERAL FL057 CHOBEE LOAMY 57060 hl 59 FL057 0 57061 FL061 61001 60 hl 0 61 hl 0 1 ir 9 FL061 61002 2 ir 6

E-75 Appendix E Soil Classification Database PEPPER SAND PAOLA SAND, 0 TO TO SAND, 0 PAOLA 5 PCT SLOPES PALM BEACH SAND, PALM 5 PCT 0 TO SLOPES OLDSMAR SAND FINE MYAKKA MYAKKA SAND FINE IMMOKALEE IMMOKALEE SAND FINE FINE SAND FINE CLOM6662 3 6 S SSS S S 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 90 ENDSHWT FS DURSHWT FL0154 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUN FL0058ECOLCOMM66 SEP 90 FSMLRA 4MUKINDS 0.5 DANFLOOD FREQ 1.5 N FL0059ANFLOOD BEG JUN P SEPANFLOOD END NONE HIGHROCKDEPTH 90 FS FL0067 LOWROCKDEPTH 4 NA -8SLOPE LOW 0.5 155 NA D HIGHSLOPE -8 1.5 JUN N LOW NONEPANDEPTH FL0066 SEP P HIGHPANDEPTH 90 FSPANHARD 0 -9 NAOTHERPH 0.5 2 -9 155 -8 4 NA JUNLEACH 1.5 NONE SEP -8RUNOFF D NCORCON P 90CORSTEEL S NA FL0056 NONE 6.0 NA NA -9 NA 0 6.0 NA 155 -9 4 2 NA -8 D LOW HIGH -8 N NONE MED HIGH P NA NA NA 155 NA -9 FL0227 -9 0 -8 MED HIGH -9 2 A HIGH HIGH -8 90 N S 6.0 NA E NA 155 NA 6.0 NA NA NA NONE -9 HIGH MED -8 0 -9 HIGH HIGH 2 -8 NA HIGH NA LOW MED -9 HIGH -9 90 -9 A 0 0.5 S JUN N 5 NONE 1.5 SEP 155 NA E LOW NA HIGH NA LOW LOW NA -8 -8 4 -9 D -9 N 155 0 LOW NA HIGH P 5 HIGH NA NA LOW NA -8 -8 15 HIGH LOW 30 MED HIGH 0 THIN 2 NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL061 61003 ir EAUGALLIE 8 3 FL061 61004 ir 8 4 FL061 61005 FL061 61006 ir 8 5 FL061 61007 ir 8 6 FL061 61008 ir 10 7 FL061 61009 10 ir 8 8 ir 9

E-76 Soil Classification Database Appendix E PINEDA FINE SAND MANATEE LOAMY MANATEE FINE SAND WINDER WINDER FINE SAND WABASSO WABASSO SAND FINE ARCHBOLD SAND, PCT SLOPES 5 TO 0 ST. LUCIE SAND, 0 LUCIE ST. 8 PCT SLOPES TO FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL061 61010 ir RIVIERA 7 10 FL061 61011 ir 11 10 FL061 61012 12 9 ir FL061 61013 FL061 61014 13 8 ir FL061 61015 14 7 ir FL061 61016 15 6 ir 16 7 ir SURFTEXT 1FSSS 190909090909090 FSFSLFSFS 475 6 LOW-9-9-9-9-9-9-9 ENDNANANANANANANA DUR7-96 S SSS S 1S5ID COMPPCT SURFTEXT HIGHSHWT LOWSHWT SHWT BEG ENDSHWT SHWT FL0064 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0057ECOLCOMM DECMLRA 6.0MUKINDSS D 6.0ANFLOOD FREQ Y NAANFLOOD BEG P NA 8ANFLOOD NONE HIGHROCKDEPTH FL0434 LOWROCKDEPTH NA -8SLOPE LOW A 155 HIGHSLOPE -8 N NONE EPANDEPTH 3 3.5 HIGHPANDEPTH 6.0PANHARD NA JUN 0OTHERPHNANANANANANANA 155 -8 NOV 2 -9 FL0075LEACH -8RUNOFFCORCON FL0076 NONECORSTEEL NA A 0 N -9 8 MW 0.5 3 FL0157 LOW 1.5 HIGH JUN NA 155 SEP HIGH HIGH -8 NA -8 0.0 NONE HIGH LOW JUN 1.0 MED LOW DEC FL0080 D 0 P -9 N NONE 5 0.0 6 JUN NA OCT 155 0.5 NA -8 NONE HIGH LOW D -8 P Y MED LOW 155 NA 12 -8 0 -9 JUN 0.0 NOV 2 -8 D NONE 1.0 VP Y 155 NA NA 26 LOW HIGH HIGH MED -8 -9 0 -8 2 LOW NA HIGH LOW HIGH D P 155 Y NA -9 26 0 MED HIGH 2 NA LOW HIGH -8 -8 HIGH LOW -9 HIGH LOW 0 NA 2

E-77 Appendix E Soil Classification Database ST. AUGUSTINE ST. SAND FLORIDANA FLORIDANA SAND ARENTS, 0 TO ARENTS, 0 TO 5 PCT SLOPES URBAN LAND POMELLO SAND, 0 SAND, 0 POMELLO 5 PCT SLOPES TO CAPTIVA CAPTIVA SAND FINE TO 5 PCT SLOPES 5 PCT TO S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 90 ENDSHWT FS DURSHWT FL0437 2.0HYDRIC 8.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND BANFLOOD FREQ NANFLOOD BEG MW NA FL0273ANFLOOD END 90 NONE FS HIGHROCKDEPTH LOWROCKDEPTH 0.0 NA FL0078 -8SLOPE LOW 0.5 M 155 NA HIGHSLOPE -8 JUN OCT LOWPANDEPTH 90 S HIGHPANDEPTH 2.0PANHARD 5 0 -9OTHERPH 3.5 JUL 5 -9 D NOVLEACH P Y DC0035 NONERUNOFF 2CORCON FL0097CORSTEEL NA 5 NA NONE NA 155 -8 NA C S 90 MW -8 N VAR 3 2.0 FL0068 MED LOW NA HIGH 2.0 LOW NA NA FS 90 155 -9 NA 0 -8 1.5 -9 FL0320 1 S -8 JUN 3.0 NOV NONE -9 NA NONE NA NA -9 NA 0 N -9 S 90 5 NA HIGH HIGH 0.0 6 LOW JUN NA OCT SP LOW 155 0.5 NA NA NA -8 NONE N NA NA M MED -8 MED NA 155 HIGH 90 LOW S NA 1.5 OCT JUL -8 RARE 3.0 -9 M -8 VP 5 D 0 -9 5 NA Y 156B NA NA -9 MED NA NA HIGH -9 0 ND SP ND 5 -8 C 4 NA MED HIGH S -8 NA 155 NA N MED NA HIGH NA -9 -8 -9 0 LOW HIGH -8 S 2 NA MED NA HIGH -9 MED MED -9 0 NA HIGH HIGH 2 NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL061 61017 ir QUARTZIPSAMMENTS0 9 17 FL061 61018 ir 18 7 FL061 61021 21 ir 9 FL061 61022 FL061 61023 22 ir FL061 11 61024 23 11 ir FL061 61025 24 7 ir 25 9 ir

E-78 Soil Classification Database Appendix E JONATHAN SAND, JONATHAN 5 PCT 0 TO SLOPES JUPITER FINE SAND IMMOKALEE - URBAN LAND URBAN LAND - IMMOKALEE COMPLEX EAUGALLIE - URBAN EAUGALLIE COMPLEX LAND LAND COMPLEX OPC 955 50 9090 1955050 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG ENDSHWT FS DURSHWT DC0002 0.0HYDRIC 6.0HYDROGRP FL0054DRAINAGE JAN FSECOLCOMM DECMLRA 12 0.5MUKIND 1.5 DANFLOOD FREQ JUN Y FEBANFLOOD BEG FL0154 P NAANFLOOD END 9 FREQ HIGHROCKDEPTH LOWROCKDEPTH JAN FS NA -8SLOPE LOW M 155 DEC N 0.5 HIGHSLOPE -8 NONE NA P 1.5 LOWPANDEPTH JUN SEP HIGHPANDEPTH NAPANHARD FL0058 NA 155 1 40 -9OTHERPH C 3 -9 24 4LEACHRUNOFF NONE NACORCON NA NCORSTEEL FS P NA -9 0 -9 NA 0.5 2 NA JUN 1.5 NA 155 SEP -8 HIGH HIGH C -8 HIGH NA HIGH FL0053 NA NONE MED 4 HIGH NA FL0159 MED -9 HIGH 0 -9 NA 2 N P NA FS NA 155 NA NA 0.5 -8 JUN LOW HIGH NOV 1.5 C -8 HIGH HIGH NONE S JUN 3.0 OCT -9 5.0 0 -9 D 6 2 NONE 12 NA N HIGH MED NA P NA HIGH HIGH 155 NA B 5 20 3 8 S N NA 155 MW NA -9 -8 -9 0 S -8 1 HIGH NA HIGH HIGH LOW NA 50 72 LOW 0 LOW LOW 5 HIGH THIN NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL061 61020 ir BEACHES 20 2 BOCA - URBAN FL061 61027 ir 27 11 FL061 61028 28 ir 11 FL061 61029 29 ir 11 FL061 61031 FL061 61032 31 8 ir 32 9 ir

E-79 Appendix E Soil Classification Database CANOVA CANOVA MUCK GATOR GATOR MUCK MALABAR MALABAR SAND FINE BOCA SAND FINE MCKEE MUCKY MUCKY MCKEE LOAM CLAY SATELLITE SATELLITE SAND FINE TO 5 PCT SLOPES 5 PCT TO COMPPCT 190909090909090 3 19662525 S S SSS S 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT ENDSHWT S DURSHWT FL0019 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM3 NAMLRA -9MUKINDS AANFLOOD FREQ FL0102 NANFLOOD BEG E SANFLOOD END 1.5 NONE HIGHROCKDEPTH FL0432 3.5 LOWROCKDEPTH NA -8SLOPE LOW JUN 155 NA HIGHSLOPE -8 NOV LOWPANDEPTH 6 MK-CL 0.0 HIGHPANDEPTH PANHARD 0.5 FL0054 C 0 JAN -9 NOTHERPH 5 NONE DEC -9 SPLEACHRUNOFF FLO390CORCON 12 NA FSCORSTEEL 155 -8 FREQ NA NA D 0.5 FL0415 -8 NA Y VP 1.5 JUN FEB HIGH LOW JAN FS HIGH FL0256 155 LOW -9 0 DEC -8 -9 0.5 2 NONE 9 -8 JUN 1.5 NOV D P NA N MUCK NONE NA -9 -2.0 0 NA -9 JUN HIGH OCT 1 155 NA 0.0 MED 6 MED LOW 40 NONE MUCK D NA 24 P Y NA LOW -2.0 NA JUN HIGH DEC 155 NA HIGH HIGH 0.0 NONE 5 -9 -8 0 -9 -8 2 D VP Y NA 156B NA NA MED NA HIGH MED HIGH -9 -8 7 -9 0 -8 2 VP D 156B LOW NA NA HIGH Y NA LOW HIGH NA -9 -9 -8 0 LOW HIGH -8 1 HIGH NA HIGH UNDRAINED DRAINED -9 HIGH LOW -9 HIGH LOW 0 NA 1 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL061 610330 SAND, ir ASTATULA 10 33 FL061 61034 9 ir 34 FL061 61035 35 2 ir FL061 61036 FL061 61039 36 8 ir FL061 61040 39 FL061 61041 8 ir 40 5 ir 41 5 ir

E-80 Soil Classification Database Appendix E ELECTRA SAND, 0 ELECTRA 5 PCT SLOPES TO HOLOPAW HOLOPAW FINE SAND ORSINO FINE SAND, 5 PCT 0 TO SLOPES MYAKKA FINE SAND, MYAKKA DEPRESSIONAL PERRINE VARIANT PERRINE VARIANT SANDY LOAM FINE CEIA MUCK S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 90 ENDSHWT MUCK DURSHWT FL0031 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUN SIL FL8002ECOLCOMM OCT 90MLRA 5 -1.0MUKIND DANFLOOD FREQ 1.0 Y JUNANFLOOD BEG VP 12 SEPANFLOOD END NONE HIGHROCKDEPTH FL0307 LOWROCKDEPTH 4 NA -8SLOPE LOW FS S 156B NA D HIGHSLOPE -8 Y 95 P NONE LOWPANDEPTH 18 -2.0 HIGHPANDEPTH PANHARD 0.0 JUN 0 -9 NA 155OTHERPH SEP 1 -9 20 NALEACH S 7RUNOFF FL0103CORCON 4CORSTEEL NONE NA D FS UNDRAINED -9 0 Y VP -9 25 1 NA 90 4.0 LOW HIGH 155 NA MED JUN MED 5.0 NA DEC -8 NA FL0027 S -8 MED HIGH FL0010 NONE LOW HIGH 7 -9 FS 0 -9 NA A 1 MW N 90 3 0.0 JUN 155 NA NA NOV 1.0 NA S -8 MED LOW NONE HIGH HIGH S 2.0 -8 90 JUL OCT 3.5 6 NONE -9 P NA 0 -9 D 5 Y 26 155 NA NA NA LOW HIGH -8 LOW MED 4 SP C S -8 6 N 155 NA NA NA -9 -8 -9 0 2 -8 S NA MED HIGH HIGH MED NA -9 -9 0 MED LOW 5 NA LOW HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL061 61042 ir TERRA 5 42 FL061 61044 ir 44 2 FL061 61045 45 ir 6 FL061 61046 46 ir 9 FL061 61047 FL061 61048 47 ir 7 48 ir 9

E-81 Appendix E Soil Classification Database MANATEE MUCKY LOAMY MANATEE FINE SAND, DEPRESSIONAL OLDSMAR FINE SAND, OLDSMAR FINE SAND, DEPRESSIONAL DEPRESSIONAL PITS FINE RIVIERA SAND, FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL061 61049 ir POMPANO 7 49 FL061 61050 FL061 61051 ir 50 11 51 6 ir FL061 61052 52 6 ir FL061 61053 53 6 ir S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT FS DURSHWT FL0032 0.0HYDRIC 0.5HYDROGRPDRAINAGE JUN DC0028 90ECOLCOMM OCT VAR FL0275MLRA 5 0.0MUKIND D 6.0ANFLOOD FREQ FS 95 Y NAANFLOOD BEG P NA 26ANFLOOD END -2.0 NONE HIGHROCKDEPTH 0.0 -9 JUN LOWROCKDEPTH NA SEP -8SLOPE LOW NA S 155 NA FL0282 HIGHSLOPE -8 N NONE E NA LOWPANDEPTH 4 HIGHPANDEPTH NONE DPANHARD NA 0 -9 Y FSOTHERPH 25 155 -8 2 95 NA -9 VPLEACH M -2.0 -8RUNOFF NA 0.0CORCON JUN 156 NA SEP -8CORSTEEL FL0322 NA S -8 -9 0 NA -9 4 NONE HIGH 4 HIGH -9 MED D HIGH 0 NA -9 25 2 Y NA VP MK-LFS 95 -2.0 MED HIGH NA 155 NA ND ND JUN NA 0.0 NA SEP -8 LOW HIGH S -8 NONE HIGH HIGH -9 4 0 -9 D 1 25 VP Y NA NA 155 HIGH LOW NA NA MED HIGH -8 -8 S -9 -9 0 2 HIGH NA LOW NA HIGH HIGH

E-82 Soil Classification Database Appendix E LOKOSEE FINE SAND SAMSULA SAMSULA MUCK HOLOPAW FINE SAND, HOLOPAW DEPRESSIONAL PINEDA FINE SAND, PINEDA FINE DEPRESSIONAL FLORIDANA MUCKY FINE MUCKY FINE FLORIDANA SAND, DEPRESSIONAL CLAY LOAM CLAY MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL061 61054 ir RIOMAR 2 54 FL061 61055 ir 55 6 FL061 61056 56 ir 6 FL061 61057 57 ir 6 FL061 61058 FL061 61059 58 ir 5 59 ir 8 RIAEPPVV VPP VPVP S S 1S5ID SS COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 90 ENDSHWT CL DURSHWT FL0433 1.0HYDRIC 1.0HYDROGRPDRAINAGEVPVP JAN FL0262ECOLCOMM DEC 95 MK-FSMLRA 12MUKINDSS -2.0 DANFLOOD FREQ 0.0 Y JUNANFLOOD BEG 19 SEPANFLOOD END FREQ HIGHROCKDEPTH 4 LOWROCKDEPTH JAN 40SLOPE LOW 155 DEC D HIGHSLOPE 20 Y FL0411 NONE LOWPANDEPTH 25 HIGHPANDEPTH FSPANHARD NA 95 0 -9OTHERPH NA -8 155 1 -9 -2.0LEACH -8RUNOFF 0.0 JUNCORCON SEPCORSTEEL FL0264 NA -9 NA 0 -9 4 1 NONE FS LOW HIGH D ND Y ND 95 25 NA -2.0 NA NA JUN 0.0 NA SEP 155 LOW HIGH -8 FL0092 -8 LOW MED NONE 4 FL0164 -9 D 0 -9 MUCK 25 Y 1 90 -2.0 NA 155 NA NA JUN OCT 0.0 FS -8 NA HIGH LOW -8 NONE LOW HIGH 0.5 90 JUL NOV 1.5 -9 5 0 -9 NONE 1 D 17 Y NA NA HIGH 155 NA MED NA -8 HIGH MED 5 -8 D 6 N NA 155 NA -9 -8 -9 0 -8 2 HIGH NA LOW UNDRAINED HIGH HIGH NA -9 -9 HIGH 0 LOW 2 NA HIGH LOW

E-83 Appendix E Soil Classification Database NO DATA WATER DELRAY KESSON MUCK CHOBEE MUCKY LOAMY LOAMY CHOBEE MUCKY SAND, DEPRESSIONAL FINE DELRAY DELRAY MUCK DEPRESSIONAL MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL061 61060SAND, FINE ir POMPANO 6 60 FL061 61061 FL061 ir 61 61062 5 62 ir 6 FL061 61063 FL061 61098 FL061 63 61099 ir 2 FL069 69006 98 ir 12 99 1 ir 6 0 lk S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0285 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4MUKIND DANFLOOD FREQ YANFLOOD BEG VP 17ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW S 155 NA FL0299 HIGHSLOPE -8 90 MUCK LOWPANDEPTH FL0412 -2.0 HIGHPANDEPTH PANHARD 0.0 MK-LFS 0 -9 JUNOTHERPH 95 1 -9 DECLEACH -2.0RUNOFFCORCON 7 0.0 JUNCORSTEEL SEP NA D Y NA VP NONE 25 4 HIGH HIGH NONE NA MED HIGH D FL0274 155 -8 VP NA Y S 12 MUCK -8 NA NA 155 NA NA 95 -8 0.0 -9 0 S -8 -9 DC0038 2 JAN 0.5 OUT DEC NA 0 -9 NA -9 0 -9 NA NA 1 NA FREQ -9 NA LOW HIGH 12 HIGH HIGH NA VP -9 D 100 NA NA NA 19 Y NA LOW HIGH -9 HIGH HIGH JAN 0 -9 155 -9 DEC NA NA NA NA -8 NA NA NA -9 S -8 NA NA NA NA -9 NA NA -9 NA -9 NA 0 -9 -9 NA NA NA 1 NA -9 NA NA NA NA NA -9 HIGH MED NA NA -9 NA M HIGH NA LOW -9 -9 -9 -9 NA NA NA -9 NA NA NA NA -9 -9 -9 -9 -9 NA NA NA NA NA NA -9 -9 -9 NA -9 NA NA NA NA NA

E-84 Soil Classification Database Appendix E HALLANDALE FINE SAND, TIDAL MATLACHA-URBAN MATLACHA-URBAN COMPLEX LAND HALLANDALE SAND FINE CAPTIVA CAPTIVA SAND FINE CANAVERAL - URBAN CANAVERAL LAND COMPLEX FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0060 1.5HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM NOV FL0060 70MLRA 6 FSMUKIND 1.0 CANFLOOD FREQ N 3.0ANFLOOD BEG SP JUN 2ANFLOOD END NOV NONE HIGHROCKDEPTH LOWROCKDEPTH NA 6 -8SLOPE LOW S 155 NA FL0273 HIGHSLOPE -8 NA LOW NPANDEPTH SP NONE HIGHPANDEPTH 2 95 FS FL0065PANHARD 0 -9 0.0OTHERPH NA 2 -9LEACH 155 0.5 -8 JUN NA C OCTRUNOFF -8CORCON FL0386 95 FSCORSTEEL NA 0.5 NA 5 JUN -9 1.5 0 SEP NONE D -9 2 P Y HIGH MED LOW MED 26 NONE 60 GR-FS NA NA FL0389 155 2.0 NA 4 NA JUN -8 OCT D 3.0 HIGH S -8 P MED N LOW MED 6 NONE NA 155 NA -9 0 20 -9 FS 1 S 7 5 NA 95 SP JAN 0.0 N DEC NA 1.0 NA NA 155 NA HIGH -9 FREQ HIGH NA 0 -9 LOW LOW 2 -8 C -8 NA MED NA HIGH LOW HIGH D 12 -9 P -9 0 Y 155 18 2 JAN MED NA DEC MED NA HIGH LOW 20 S 7 -9 -9 0 MED HIGH 2 NA HIGH MED NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL071 71002 le CANAVERAL 9 2 FL071 71004 le 11 4 FL071 71005 FL071 71006 le 7 5 FL071 71007 le 8 6 FL071 le 71008 11 7 le 2 8

E-85 Appendix E Soil Classification Database PECKISH MUCKY PECKISH MUCKY FINE SAND ESTERO MUCK VALKARIA VALKARIA FINE SAND BOCA SAND FINE FELDA FELDA SAND FINE MYAKKA MYAKKA SAND FINE POMPANO POMPANO SAND FINE SAND SOCD87878722 10111213141516 MUIDSTSSAIDMUSYM9 CNTYABBRLSPOSCODE8 MAPUNIT NAME FL071 71009 le EAUGALLIE FL071 71010 le FL071 71011 FL071 71012 le FL071 71013 le FL071 71014 FL071 71015 le FL071 71016 le le le COMPPCT 19595959595959595 DDDDDDD PPPPPVPVP 549941212 2222211 LOW-9-9-9-9-9-9-9-9 0000000 ENDNANANANANANADECDEC YNYNYYY DUR4 SSSSSSS LOW0 HIGH2 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG ENDSHWT SSHWT FL0154 0.5HYDRICN 1.5HYDROGRPD DRAINAGEP JUNECOLCOMM SEPMLRA FL0032MUKINDS ANFLOOD FREQ FSANFLOOD BEG 0.0 6ANFLOOD FL0059 0.5 NONE HIGHROCKDEPTH JUN LOWROCKDEPTH OCT NA -8SLOPE FL0127 155 FSSLOPE -8 0.5PANDEPTH 1.5 JUN HIGHPANDEPTH FL0054 SEPPANHARD NONE 26OTHERPHNANANANANANANANA -9 FSLEACH 0.0 FL0126 NARUNOFF JUL 1.0 155 NONE -8 MARCORCON -8CORSTEEL NA FL0301 6 FS 0.5 NONE FL0272 JUN NA FEB 155 1.5 LOW HIGH -8 -9 MED HIGH -8 NONE 26 FS 0.0 JUN SEP NA NA 155 1.0 -8 NONE -9 HIGH HIGH -8 HIGH MED JAN MUCK DEC 6 0.0 155 NA NA FREQ 0.5 MK-FS MED HIGH 40 JAN DEC -9 HIGH FREQ 0.0 HIGH 24 0.5 155 26 NA NA HIGH MED HIGH MED -8 -9 -8 155 HIGH JAN NA 18 LOW HIGH MED 155 -8 JAN -9 HIGH -8 19 HIGH HIGH NA MED -8 HIGH -8 LOW HIGH -9 HIGH NA HIGH HIGH HIGH HIGH -9 NA

E-86 Soil Classification Database Appendix E FINE SAND BEACHES KESSON TERRA CEIA MUCK GATOR GATOR MUCK MATLACHA GRAVELLY FINE SAND, LIMESTONE LIMESTONE FINE SAND, GRAVELLY MATLACHA SUBSTR. SAND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL071 71017 le DAYTONA 9 17 FL071 71018 le 18 11 FL071 71019 FL071 19 le 5 71020 FL071 71022 20 le 5 FL071 71024 22 le 2 24 le 2 COMPPCT 19595 95959595 VPVPPVP 2525NA18 SSMS 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT ENDSHWT SSHWT FL0230 DUR 3.5HYDRIC 5.0HYDROGRPDRAINAGEMWSP FL0387 JULECOLCOMM3NA NOV GR-FSMLRA 2.0 5MUKINDSS 3.0 BANFLOOD FREQ N JUNANFLOOD BEG OCTANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH 5 NA -8SLOPE LOW NA 155 NA N HIGHSLOPE -8 NONE LOWPANDEPTH HIGHPANDEPTH PANHARD NA 0 -9 155 60OTHERPH NA 5 -9LEACH 40RUNOFFCORCONCORSTEEL NA -9 0 NA -9 2 FL0415 LOW LOW MUCK HIGH MED NA NA FL0031 -2.0 LOW MED 0.0 JUN LOW MUCK APR HIGH DC0002 -2.0 FL0274 S NONE 11 JUN D 0.0 APR Y 0.0 NONE NA 155 FS JAN NA -8 DEC 6.0 11 D -8 Y FREQ 0.0 JAN DEC NA 155 0.5 -9 NA 0 -9 -8 FREQ 1 12 D -8 Y NA 155 UNDRAINED JAN LOW DEC HIGH -9 12 UNDRAINED HIGH HIGH 0 -9 -8 D 1 NA -8 Y JAN 155 NA DEC LOW HIGH MED MED -8 -9 NA -9 -8 1 2 NA HIGH HIGH HIGH HIGH -9 -9 0 HIGH LOW 1 LOW NA HIGH

E-87 Appendix E Soil Classification Database OLDSMAR SAND WULFERT WULFERT MUCK IMMOKALEE IMMOKALEE SAND POMPANO FINE SAND, FINE POMPANO DEPRESSIONAL PINEDA SAND FINE SUBTR. - URBAN LAND COMPLEXSUBTR. S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 60 ENDSHWT S DURSHWT FL0321 1.5HYDRIC 3.0HYDROGRPDRAINAGE JULECOLCOMM OCTMLRA 4MUKIND NAANFLOOD FREQ NANFLOOD BEG SP NAANFLOOD END RARE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C 155 NA HIGHSLOPE -8 LOWPANDEPTH FL0080 HIGHPANDEPTH 95PANHARD FS 0 -9OTHERPH 0.0 2 -9 FL0285LEACH 1.0RUNOFF JUNCORCON NOV 95CORSTEEL NA FS -2.0 6 NA D 0.0 JUN MAR Y P HIGH NONE LOW 26 HIGH HIGH FL0058 10 NA NONE D 155 -8 NA S -8 Y 25 VP FL0276 95 S NA 0.5 155 -9 NA FL0067 0 -8 JUN 1.5 SEP -9 2 S -8 95 NA NONE 0.0 MUCK -9 NA 4 JAN 0 DEC -9 0.5 D 2 LOW HIGH P LOW 6 HIGH N S FREQ 95 NA 0.5 SEP JUN NA NA 155 MED 1.5 HIGH NA -8 HIGH MED 12 NONE S D -8 VP 18 Y JAN 155 -9 DEC 4 0 -9 -8 D 2 P -8 6 S N NA NA 155 NA HIGH MED NA HIGH HIGH -9 -8 -9 0 -8 S 1 HIGH NA LOW HIGH HIGH NA -9 -9 0 HIGH LOW MED 2 HIGH NA NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL071 71025ORGANIC AUGUSTINE SAND, le ST. 11 25 FL071 71026 le 7 26 FL071 71027 27 le 6 FL071 71028 FL071 71023 28 le 8 FL071 71033 23 le 2 33 le 8

E-88 Soil Classification Database Appendix E ISLES FINE SAND, DEPRESSIONAL FINE SAND, ISLES ISLES FINE ISLES SAND, SLOUGH SATELLITE SATELLITE SAND FINE IMMOKALEE-URBAN IMMOKALEE-URBAN COMPLEX LAND WABASSO WABASSO SAND FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL071 71034 le MALABAR 7 34 FL071 71035 le 35 8 FL071 71036 le 36 11 FL071 71037 FL071 71038 37 le 9 FL071 71039 38 le 7 39 le 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0123 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0075 95ECOLCOMM NOV SMLRA 6 0.5MUKIND FL0058 D 1.5ANFLOOD FREQ Y JUNANFLOOD BEG P SEP 26ANFLOOD END 70 NONE HIGHROCKDEPTH S 0.5 4 LOWROCKDEPTH NA -8 1.5SLOPE LOW JUN D S 155 NA SEP HIGHSLOPE -8 N NONE P 6 LOWPANDEPTH FL0102 HIGHPANDEPTH PANHARD NA 4 0 -9OTHERPH NONE 155 -8 2 NA -9 FL0395 NALEACH S -8 NRUNOFF 95 P 6CORCON FS 1.5CORSTEEL JUN NA 3.5 NA 155 NOV -9 NA 0 NA -8 FL0396 -9 2 C -8 95 LOW HIGH NONE FS 0.0 JUN LOW HIGH OCT NA 1.0 6 C NA -9 0 -9 2 N LOW HIGH NONE SP 3 MED HIGH NA 155 NA 95 NA NA JUN -8 5 -2.0 MAR FS HIGH D MED 0.0 S -8 HIGH HIGH Y P NONE 26 NA 155 NA -9 72 0 -9 2 40 S 10 D NA LOW NA HIGH Y VP MED LOW 155 25 -9 NA -9 NA 0 1 72 HIGH NA MED 40 LOW NA HIGH S -9 -9 0 HIGH MED 1 NA HIGH LOW NA

E-89 Appendix E Soil Classification Database MALABAR FINE SAND, FINE MALABAR DEPRESSIONAL SMYRNA SMYRNA FINE SAND WABASSO SAND, WABASSO SUBSTR. LIMESTONE VALKARIA FINE SAND, VALKARIA DEPRESSIONAL DEPRESSIONAL MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL071 71040 leSAND, ANCLOTE 6 40 FL071 71041 le 41 6 FL071 71042 42 le 8 FL071 71043 FL071 71044 43 le 8 44 le 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT SSHWT DUR FL0315 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END FL0267 NONE 95 HIGHROCKDEPTH LOWROCKDEPTH FS -2.0 NA -8SLOPE LOW S 155 NA 0.0 HIGHSLOPE -8 JUN LOWPANDEPTH MAR HIGHPANDEPTH PANHARD 10 0 -9OTHERPH 2 -9LEACH DRUNOFF Y VP NONE 25 FL0419CORCONCORSTEEL NA NA NA 95 155 -8 NA S 0.5 S -8 HIGH HIGH 1.5 JUN MED HIGH SEP -9 FL0091 0 -9 2 4 NONE FL0286 D P N NA 6 95 NA 0.5 FS HIGH NA HIGH JUN 155 1.5 SEP NA HIGH MED 80 S 40 95 -2.0 NONE FS JUN 4 MAR 0.0 -9 0 -9 D 2 P N NONE 6 NA NA 155 10 NA NA LOW -8 HIGH MED D -8 S MED VP Y 25 155 NA NA -9 -8 0 -9 -8 2 S NA MED HIGH NA HIGH -9 HIGH -9 0 2 HIGH LOW NA HIGH NA LOW

E-90 Soil Classification Database Appendix E FLORIDANA SAND, FLORIDANA DEPRESSIONAL OLDSMAR FINE SAND, OLDSMAR FINE SAND, SUBSTR. LIMESTONE FELDA FINE SAND, FINE SAND, FELDA DEPRESSIONAL ST. AUGUSTINE ST. SAND DEPRESSIONAL S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT LS DURSHWT FL0265 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 21ANFLOOD END NONE HIGHROCKDEPTH FL0320 LOWROCKDEPTH 95 NA S 50SLOPE LOW S 155 NA 1.5 HIGHSLOPE 20 LOWPANDEPTH 3.0 JUL HIGHPANDEPTH OCTPANHARD FL0298 0 -9OTHERPH 4 1 -9LEACH 95RUNOFF C FSCORCON -2.0 N SP RARE NACORSTEEL NA 1.0 JUN DEC NA NA FL0391 -8 155 NA MED S HIGH -8 7 LOW HIGH NONE D VP Y 25 95 -9 0 FS 0.5 -9 2 NA JUN 1.5 SEP 155 NA -8 FL0262 S -8 NA NA NONE 4 HIGH MED HIGH HIGH -9 P 0 D -9 6 2 N 95 0.0 FS NA 155 NA JUN MAR NA 0.0 NA 72 MED HIGH 40 S HIGH HIGH NONE -9 10 0 -9 2 VP D 25 Y NA 155 NA LOW HIGH NA NA HIGH LOW -8 -8 S -9 -9 0 2 HIGH NA LOW MED LOW NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL071 71045 leLOAM, COPELAND SANDY 6 45 FL071 71048 le 48 9 FL071 71049 49 le 6 FL071 71050 50 le 8 FL071 71051 51 le 6

E-91 Appendix E Soil Classification Database ORSINO FINE SAND URBAN LAND SAND, TIDAL S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0307 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW S NA 155 HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH PANHARD FL0061 95 0 -9OTHERPH FS 2 -9LEACH 5.0RUNOFF 6.0CORCON JUNCORSTEEL SEP NA NA 4 FL0394 MED A HIGH 95 N HIGH W HIGH MUCK NONE 4 FL0384 0.0 0.5 JAN NA DEC 155 40 NA FS S DC0035 20 95 FL0103 12 0.0 FREQ JAN 1.0 DEC D -9 0 VP Y -9 2 18 VAR 95 JAN FREQ 2.0 155 12 DEC 72 FS NA NA NA 2.0 NA S 40 D P 95 Y HIGH LOW 4.0 18 LOW JUN NONE LOW DEC JAN 5.0 155 DEC -9 -9 0 NONE -9 40 1 24 S NA NA N NA NA 7 NA NA NA 155 MED HIGH -9 A HIGH MW HIGH -8 0 -9 3 1 NA N -8 NA 155 M NA HIGH LOW NA -8 HIGH HIGH -8 -9 S -9 0 2 HIGH NA MED ND ND -9 NA -9 0 LOW HIGH 5 NA MED LOW NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL071 71053DEPRESSIONAL FINE SAND, le MYAKKA 6 53FINE SAND COCOA MUCK ISLES BOCA FINE FL071 71055 le 55 9 FL071 71056 FL071 56 le 71057 2 FL071 71059 57 le FL071 71061 2 59 le 11 61 le 9

E-92 Soil Classification Database Appendix E SMYRNA-URBAN SMYRNA-URBAN LAND COMPLEX CALOOSA FINE SAND HALLANDALE - URBAN HALLANDALE - COMPLEX LAND SAND, HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL071 71062SAND, DEPRESSIONAL le WINDER 6 62 FINE MALABAR FL071 71063 le 63 8 FL071 71064 64 le 11 FL071 71066 FL071 71067 66 le 11 67 le 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT S DURSHWT FL0283 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW S 155 NA HIGHSLOPE -8 FL0390 LOW 95PANDEPTH HIGHPANDEPTH FS 0.5PANHARD 0 -9 1.5OTHERPH 2 -9 JUNLEACH SEP FL0065RUNOFFCORCON 4CORSTEEL 70 NA D FS NA 0.5 N P NONE 6 1.5 JUN LOW SEP HIGH LOW HIGH NA 155 -8 NA FL0420 S 4 -8 NONE NA FL0091 N P NA -9 0 95 -9 2 FS 2.5 NA 155 JUL NA 3.5 20 OCT C 7 NA NA 65 FS 0.5 NONE LOW HIGH JUN SEP 4 -9 1.5 HIGH LOW 0 -9 NA 2 N NONE MW NA NA NA 155 NA NA HIGH 4 MED NA -8 HIGH LOW P S 6 -8 N NA 155 NA -9 -8 0 -9 2 C -8 NA MED NA LOW HIGH -9 HIGH -9 0 2 HIGH NA MED HIGH NA HIGH

E-93 Appendix E Soil Classification Database BOCA FINE SAND, SLOUGH PINEDA FINE SAND, PINEDA FINE DEPRESSIONAL BRADENTON BRADENTON SAND FINE HEIGHTS SAND FINE FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL071 71069 GRAVELLY le MATLACHA 11 69 FL071 71070 le 8 70 FL071 71072 72 le FL071 8 71073 73 le 6 FL071 71074 74 le 7 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT GR-FS DURSHWT FL0386 2.0HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKIND NAANFLOOD FREQ NANFLOOD BEG SP NA FSANFLOOD END FL0365 95 NONE HIGHROCKDEPTH LOWROCKDEPTH NA 0.5 -8SLOPE LOW S FL0232 155 NA 1.5 HIGHSLOPE -8 JUN FS LOWPANDEPTH SEP HIGHPANDEPTH 95PANHARD 0 4 FL0411 0.5 -9OTHERPH 2 -9 D 1.5LEACH JUN SEP NRUNOFF P NONE 6CORCON FSCORSTEEL 95 NA NA 4 NA -2.0 155 NONE -8 D NA JUN S 0.0 -8 MAR FL0383 N P MED MED 8 LOW HIGH NA 155 NONE -9 0 NA -8 -9 1 10 S FS -8 D 95 Y VP 0.0 25 NA JUN OCT NA 1.0 NA -9 155 0 -9 NA 2 LOW -8 HIGH HIGH LOW NONE S -8 NA NA 5 LOW HIGH HIGH D -9 LOW 0 -9 P Y 1 26 155 NA NA NA HIGH NA LOW 40 HIGH LOW 24 S -9 -9 0 1 HIGH NA LOW HIGH NA MED

E-94 Soil Classification Database Appendix E CHOBEE MUCK WATER LIMESTONE SUBSTRATUM LIMESTONE S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0388 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKIND DANFLOOD FREQ YANFLOOD BEG P 26ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA 20SLOPE LOW S 155 NA HIGHSLOPE 7 LOWPANDEPTH FL0010 HIGHPANDEPTH 95 FSPANHARD 0 -9 2.0OTHERPH 1 -9LEACH 3.5 JULRUNOFF OCTCORCONCORSTEEL NA 4 FL0414 NA C N NONE HIGH SP 6 95 HIGH FS LOW HIGH 0.0 NA 1.0 -8 JUN 155 NA NOV S -8 6 NONE FL0412 -9 0 D -9 2 Y P 26 NA NA 95 155 MUCK NA DC0038 80 NA -2.0 S LOW 40 JUN MED 0.0 MAR LOW HIGH -9 NA 0 NONE -9 1 100 10 -9 NA NA D -9 NA Y VP 25 NA LOW HIGH NA NA LOW 155 HIGH NA -8 S -8 -9 NA NA NA NA -9 NA NA 0 -9 NA 1 -9 NA -9 M LOW HIGH NA HIGH HIGH -9 -9 -9 -9 NA NA NA NA NA NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL071 71075 le SAND, SLOUGH HALLANDALE FINE 7 75 FINE SAND ELECTRA SAND, PINEDA FINE FL071 71076 le 76 9 FL071 71077 77 le 7 FL071 71078 FL071 78 71099 le 5 99 le 1

E-95 Appendix E Soil Classification Database 1 SOCD00 0 0 0 0000 10 0 0 0 0 0 1NANANANANANANANANANANA 0 0000 0 0 7 11181920222324263035 LOW-9-9-9-9-9-9-9-9-9-9-9 LOW-9-9-9-9-9-9-9-9-9-9-9 ENDNANANANANANANANANANANA MUSYM ENDNANANANANANANANANANANA CNTYABBR NANANANANANANANANANANA LSPOSCODE0 NAMEMAPUNIT 1S5ID COMPPCT SURFTEXT mn CANOVA LOW-9-9-9-9-9-9-9-9-9-9-9 HIGHSHWT CASSIASHWT DELRAY BEGSHWT DUETTE mnSHWT DURSHWT EUGALLIE OUT -9HYDRIC FELDAHYDROGRPNANANANANANANANANANANA mn FELDADRAINAGENANANANANANANANANANANA NA OUT FELDAECOLCOMMMLRA -9 -9 FLORIDANA mn OUTMUKIND MYAKKA NAANFLOOD FREQ ONA ANFLOOD BEG NA -9 NANANANANANANANANANANA OUTANFLOOD -9 mn NA HIGHROCKDEPTH NA NANANANANANANANANANANA LOWROCKDEPTH NA -9 OUTSLOPE NA NA NA -9 HIGHSLOPE -9 -9 NA NA mnPANDEPTH HIGHPANDEPTH NA NA OUTPANHARD -9 NA NA mn -9 NAOTHERPHNANANANANANANANANANANA -9 -9 -9 NA -9LEACH OUT NARUNOFF NA NA NA mn -9CORCON OUT NACORSTEEL -9 -9 NA -9 -9 -9 NA NA mn OUT NA NA NA -9 NA NA -9 NA -9 NA -9 -9 NA NA -9 NA NA OUT NA NA mn -9 -9 NA NA NA -9 -9 -9 -9 NA OUT NA NA NA NA NA mn NA -9 NA NA -9 -9 NA NA NA -9 -9 NA -9 NA NA NA NA NA NA -9 NA -9 NA NA NA NA -9 -9 -9 -9 NA -9 NA NA NA NA NA NA -9 NA -9 -9 -9 -9 NA -9 NA -9 NA NA NA -9 NA NA NA -9 -9 NA NA NA NA NA -9 -9 -9 NA NA NA NA -9 NA NA -9 NA -9 -9 NA -9 NA NA -9 -9 NA NA NA MUIDSTSSAID FL081 81007 FL081 81011 FL081 81018 FL081 81019 FL081 81020 FL081 81022 FL081 81023 FL081 81024 FL081 81026 FL081 81030 FL08 81035

E-96 Soil Classification Database Appendix E STONY S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 0 ENDSHWT NA DURSHWT OUT -9HYDRIC -9HYDROGRPDRAINAGE NAECOLCOMM NA NA 0 OUTMLRA -9MUKIND -9 NAANFLOOD FREQ -9 NAANFLOOD BEG NA NA OUT NA NAANFLOOD END NA 0 NA HIGHROCKDEPTH -9 LOWROCKDEPTH -9 NA NA -9SLOPE LOW -9 NA NA NA NA NA HIGHSLOPE -9 OUT NA NA NA LOWPANDEPTH NA NA HIGHPANDEPTH -9 0PANHARD NA NA -9 -9 -9 NAOTHERPH -9 NA NA -9 NA -9 FL0523 NA NALEACH NA -9 -9 NARUNOFF NA GR-MUCK CORCON NACORSTEEL -9 NA NA 95 NA NA NA -9 -9 -9 NA NA 3.5 -9 -9 NA JUN -9 NA 5.0 NOV NA NA NA NA NA NA NA B 6 -9 -9 NA NA NA N NA -9 -9 -9 W 14 -9 RARE NA NA NA NA NA NA NA S 156A NA -9 -9 -9 16 -9 NA NA 4 NA NA NA NA 0 -9 2 -9 NA NA NA NA NA NA MED HIGH MED MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL081 81038 mn PALMETTO 0 38 POMELLO FL081 WAUCHULA 81042 WAVELAND mn SLOPES, EXTREMELY 2 PCT 0 TO MUCK, GRAVELLY PENNEKAMP 42 FL081 0 81051 mn FL081 51 81052 0 FL087 87002 mn 52 0 mo 2 9

E-97 Appendix E Soil Classification Database UDORTHENTS - URBAN - UDORTHENTS LAND COMPLEX KEYLARGO KEYLARGO MUCK, TIDAL ROCK OUTCROP - ROCK OUTCROP COMPLEX, TIDAL TAVERNIER FLOODED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL087 87003 MUCK, OCCASIONALLY, mo MATECUMBE 9 3 FL087 87004 mo 2 4 FL087 87006 mo FL087 87007 2 6 mo 11 7 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT MUCK DURSHWT FL0519 1.5HYDRIC 3.0HYDROGRPDRAINAGE JULECOLCOMM DECMLRA 6MUKIND CANFLOOD FREQ NANFLOOD BEG MW 14ANFLOOD END OCCAS HIGHROCKDEPTH LOWROCKDEPTH JUL 9SLOPE LOW S 156A DEC HIGHSLOPE 2 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 -9OTHERPH ROCK 1 DC0015 -9LEACH 65RUNOFF 0.0CORCONCORSTEEL 0.5 NA JAN NA DEC MED 12 HIGH LOW MED D VP FREQ Y 19 FL0521 MUCK JAN 156A DEC 20 C 95 0 DC0035 0.0 GRX-S 0.5 JAN DEC -9 0 -9 1 65 12 FREQ 2.0 NA JAN 4.0 D VP DEC NA Y 19 HIGH HIGH JAN 156A DEC LOW RARE HIGH 12 90 S SP NA 51 NA N 156A NA NA -9 0 -9 1 90 C 10 NA NA HIGH HIGH -9 HIGH HIGH 0 -9 1 NA LOW HIGH NA MED LOW

E-98 Soil Classification Database Appendix E KEYVACA VERY GRAVELLY LOAM, LOAM, GRAVELLY VERY KEYVACA STONY EXTREMELY ISLAMORADA ISLAMORADA MUCK, TIDAL URBAN LAND LIGNUMVITAE LIGNUMVITAE MARL, TIDAL COMPLEX, TIDAL COMPLEX, MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL087 87008 mo- CUDJOE ROCK OUTCROP 2 8 FL087 87009 mo 2 9 FL087 87011 FL087 87005 mo 11 11 mo FL087 87013 2 5 mo 9 13 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 60 ENDSHWT ROCK DURSHWT DC0015 0.0HYDRIC 0.5HYDROGRPDRAINAGE JANECOLCOMM DECMLRA 12MUKIND DANFLOOD FREQ YANFLOOD BEG VP 19ANFLOOD END FREQ HIGHROCKDEPTH LOWROCKDEPTH JAN 20SLOPE LOW C 156A DEC MARL FL0513 HIGHSLOPE 0 95 LOWPANDEPTH HIGHPANDEPTH 0.0PANHARD 0.5 0 -9OTHERPH JAN 1 -9 DECLEACH DC0035 VARRUNOFF FL0522 12CORCONCORSTEEL 95 MUCK NA D NA Y 2.0 P FREQ 19 2.0 NA FL0524 NA 95 HIGH HIGH JAN LOW 156A HIGH 0.0 DEC 40 GRV-L 0.5 -9 S JAN DEC 20 RARE NA N NA NA 12 FREQ 95 -9 0 NA -9 156A 3.0 1 NA D JUN 5.0 NOV -8 VP 19 Y 156A M JAN -8 NA DEC RARE NA 6 50 MED HIGH S -9 HIGH LOW 20 0 B -9 156A W 1 9 N NA NA -9 NA 0 -9 NA 6 1 LOW HIGH ND ND 3 S NA HIGH HIGH NA HIGH HIGH -9 -9 0 1 HIGH MED NA NA MED MED

E-99 Appendix E Soil Classification Database WATER OCCASIONALLY FLOODED OCCASIONALLY BEACHES SADDLEBUNCH MARL, KEYWEST KEYWEST MARL, TIDAL BAHIAHONDA FINE SAND, BAHIAHONDA FINE PCT SLOPES 3 TO 0 TIDAL S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT MARL DURSHWT FL0516 0.0HYDRIC 0.5HYDROGRPDRAINAGE JANECOLCOMM DECMLRA 12 FS FL0525MUKIND 95 DANFLOOD FREQ YANFLOOD BEG 2.5 P 19ANFLOOD END 3.5 FREQ JUN HIGHROCKDEPTH NOV LOWROCKDEPTH JAN 20 LOWSLOPE S 156A DEC 6 HIGHSLOPE 3 LOWPANDEPTH C HIGHPANDEPTH N RAREPANHARD 2 MW FL0515 0 -9OTHERPH 1 -9 MARLLEACH NA 156A 95RUNOFF NA 90CORCON DC0002 S 0.0CORSTEEL 60 NA 0.5 JAN DEC S FL0514 NA -9 0 95 MED HIGH -9 3 12 LOW HIGH 0.0 FREQ JAN 6.0 MARL DEC D P Y NA 19 95 NA 156A 0.5 JAN JUN NOV HIGH DEC MED FREQ 12 1.0 90 MED LOW S 40 D P OCCAS Y DC0038 156A NA JAN 6 DEC -9 0 -8 -9 1 156A D SP -8 14 M N JUN NOV NA NA NA MED 20 HIGH -9 HIGH LOW 1 -9 100 4 S -9 2 NA NA -9 NA NA HIGH HIGH NA -9 HIGH HIGH -9 0 1 MED HIGH NA -9 HIGH NA LOW NA NA NA NA NA NA NA -9 -9 M -9 -9 -9 NA NA -9 NA NA NA NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL087 87015 mo CUDJOE MARL, 2 15 FL087 87016 mo 16 9 FL087 87017 mo FL087 17 87018 2 FL087 87019 mo 18 2 mo 19 3 FL087 87099 mo 99 1

E-100 Soil Classification Database Appendix E CANDLER FINE SAND, CANDLER FINE 5 PCT 0 TO SLOPES BASINGER FINE SAND, BASINGER FINE DEPRESSIONAL ARCHBOLD FINE SAND, ARCHBOLD FINE PCT SLOPES 5 TO 0 NEARLY LEVEL NEARLY MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL095 95001 or ARENTS, 11 1 FL095 95002 or 9 2 FL095 95003 or 6 3 FL095 95004 or 10 4 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0097 1.5HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6 FL0434 90MUKIND FS NAANFLOOD FREQ N 3.5ANFLOOD BEG SP NA 6.0ANFLOOD END JUN NONE HIGHROCKDEPTH NOV LOWROCKDEPTH NA -8SLOPE LOW M 155 NA 6 HIGHSLOPE -8 A LOWPANDEPTH FL0261 HIGHPANDEPTH N MW NONE 3PANHARD 0 -9OTHERPH 2 90 -9 FSLEACH NARUNOFF -2.0 155 -8 NA SCORCON 1.0 JUN -8CORSTEEL SEP NA NA FL0003 -9 0 4 HIGH -9 MED 5 NONE D MED HIGH VP Y 17 NA 90 FS NA 6.0 NA 155 NA NA HIGH -8 6.0 LOW NA S LOW MED -8 NONE -9 0 -9 -9 2 A E N 4 NA NA NA 154 HIGH NA HIGH -8 HIGH MED S -8 -9 0 -9 5 NA HIGH NA LOW LOW HIGH

E-101 Appendix E Soil Classification Database CANDLER - URBAN LAND PCT SLOPES 5 TO 0 COMPLEX, CANDLER AND APOPKA FINE SLOPES PCT 12 TO SANDS, 5 TO 12 PCT SLOPES TO S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT ENDSHWT DURSHWT HYDRICHYDROGRPDRAINAGEECOLCOMMMLRA 90MUKIND FSANFLOOD FREQ FL0003 6.0ANFLOOD BEG 6.0ANFLOOD END HIGH NAROCKDEPTH LOW NAROCKDEPTH -9SLOPE LOW HIGHSLOPE A LOWPANDEPTH N HIGHPANDEPTH E 4PANHARD NONEOTHERPHLEACH NA -8 FL0003RUNOFF S 154 NA 60 -8 FSCORCONCORSTEEL 6.0 6.0 5 NA -9 12 -9 NA -9 A NA N NONE E NA 4 FL0003 HIGH NA LOW 154 -8 HIGH NA LOW U 50 -8 FS 6.0 6.0 NA -9 5 12 -9 NA -9 NONE NA NA NA N E HIGH NA LOW HIGH LOW NA 154 NA -8 C -8 -9 5 0 -9 NA NA HIGH LOW HIGH LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL095 95005 or SAND, 5 CANDLER FINE 10 5 FL095 95006 or 10 6 FL095 95007 11 or 7

E-102 Soil Classification Database Appendix E FLORIDANA ANDFLORIDANA CHOBEE SOILS, FLOODED FREQUENTLY CHOBEE FINE SANDY SANDY CHOBEE FINE FLOODED LOAM, FREQUENTLY NA NA CANOVA CANOVA MUCK D COMPLEX, 5 TO 12 PCT SLOPES PCT 12 TO 5 COMPLEX, MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL095 95008 or- URBAN LAND CANDLER 11 8 FL095 95009 FL095 or 5 95010 9 or 6 10 FL095 95011 or 6 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 50 ENDSHWT FS DURSHWT FL0003 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND NAANFLOOD FREQ NANFLOOD BEG E NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C NA 154 HIGHSLOPE -8 FL0256 LOWPANDEPTH 90 HIGH MUCKPANDEPTH FL0040PANHARD -2.0 5 -9OTHERPH 0.0 12 FSL -9 90 JUNLEACH DEC 0.0RUNOFF 7CORCON 0.5 NA JUNCORSTEEL D NA OCT Y NONE 25 VP 5 HIGH LOW FREQ D NA HIGH LOW 155 -8 NA Y 21 VP S FL0369 -8 JUN 155 FEB FS -8 -9 0 S 1 -8 -9 70 0.0 0.5 JUN NA -9 OCT 0 2 -9 DRAINE FREQ LOW NA HIGH 5 LOW HIGH D VP 21 Y LOW HIGH LOW MED JUL 155 SEP -8 U -8 -9 0 -9 2 NA LOW HIGH LOW MED

E-103 Appendix E Soil Classification Database FELDA FINE SAND, FINE SAND, FELDA FLOODED FREQUENTLY FELDA FINE SAND, FINE SAND, FELDA FLOODED OCCASIONALLY FELDA FELDA SAND FINE FREQUENTLY FLOODED FREQUENTLY MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL095 95012SANDS, FINE or EMERALDA AND HOLOPAW 6 12 FL095 95013 or 13 7 FL095 95014 or 14 7 FL095 95015 15 or 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 55 ENDSHWT FS DURSHWT FL0360 0.0HYDRIC 0.5HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKIND DANFLOOD FREQ YANFLOOD BEG P 21ANFLOOD END FREQ HIGHROCKDEPTH LOWROCKDEPTH JUN -8SLOPE LOW U FEB 155 HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 -9OTHERPH 2 -9LEACHRUNOFF FL0127CORCON 90 FSCORSTEEL NA 0.0 NA FL0329 1.0 JUL MAR MED HIGH 90 FS LOW HIGH 9 0.0 1.0 JUL D MAR Y NONE 12 P NA 9 NA FL0329 155 OCCAS -8 D S -8 Y 12 P JUL 90 FEB 155 FS -9 0 -8 -9 2 0.0 S -8 JUL 1.0 MAR NA NA -9 FREQ 0 -9 2 MED HIGH 9 HIGH MED D NA 12 Y NA P JUL HIGH MED FEB HIGH 155 MED -8 S -8 -9 0 -9 2 NA HIGH NA MED HIGH MED

E-104 Soil Classification Database Appendix E LAKE FINE SAND, 0 FINE SAND, LAKE 5 PCT SLOPES TO IMMOKALEE IMMOKALEE FINE SAND GATOR GATOR MUCK FLORIDANA MUCKYFLORIDANA SAND, DEPRESSIONAL FINE FLOODED S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 90 ENDSHWT FS DURSHWT FL0369 0.0HYDRIC 0.5HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKIND DANFLOOD FREQ YANFLOOD BEG VP 21ANFLOOD END FREQ HIGHROCKDEPTH LOWROCKDEPTH JUL -8SLOPE LOW S 155 SEP HIGHSLOPE -8 LOWPANDEPTH FL0262 HIGHPANDEPTH 90PANHARD MK-FS 0 -9OTHERPH -2.0 2 -9LEACH 0.0RUNOFF JUNCORCON SEPCORSTEEL NA 4 NA D Y VP LOW NONE HIGH 17 LOW MED FL0415 NA MUCK NA FL0058 155 -8 90 S -8 -2.0 FS 0.0 JUN FL0105 OCT 90 -9 0 0.5 -9 2 JUN 1.5 SEP 5 FS NONE D NA VP Y 25 NA 95 NONE 6.0 LOW HIGH NA NA 4 NA LOW NA 6.0 155 MED P D -8 6 N S -8 NONE NA 155 NA -8 -9 -9 0 -9 S -8 1 E A N 4 NA 154 NA NA -9 DRAINED 0 -9 HIGH LOW -8 2 NA HIGH HIGH -8 S NA HIGH MED HIGH HIGH -9 -9 0 NA 5 LOW NA HIGH HIGH LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL095 95016 or FLORIDANA FINE SAND, FREQUENTLY 6 16 FL095 95017 or 17 6 FL095 95018 FL095 95020 or 18 5 FL095 95021 20 or 8 21 or 10

E-105 Appendix E Soil Classification Database ONA - URBAN LAND COMPLEX ONA FINE SAND HONTOON HONTOON MUCK MILLHOPPER - URBAN LAND COMPLEX, 0 0 - URBAN LAND COMPLEX, MILLHOPPER 5 PCT SLOPES TO MALABAR MALABAR SAND FINE FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL095 95022 or LOCHLOOSA 9 22 FL095 95023 or 23 7 FL095 95024 or 24 11 FL095 95019 FL095 95026 or 19 5 FL095 95027 26 or 8 27 or 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0015 2.5HYDRIC 5.0HYDROGRPDRAINAGE JULECOLCOMM OCT FL0123MLRA 90 4 FSMUKIND B 0.0ANFLOOD FREQ N FL0247ANFLOOD BEG 1.0 SP 11 JUNANFLOOD END NOV NONE HIGHROCKDEPTH 50 FS LOWROCKDEPTH NA -8 6 3.5SLOPE LOW S 155 NA HIGHSLOPE 6.0 -8 AUG D FEB LOWPANDEPTH Y P NONE HIGH 26PANDEPTH PANHARD 0 -9OTHERPH 2 NA -9 7LEACH NONE 155 -8 NARUNOFF NA S -8 N MWCORCON NACORSTEEL NA NA NA 154 -9 0 NA -8 -9 2 C FL0090 LOW -8 MED HIGH HIGH NA FL0124 NA -9 0 -9 90 MUCK 5 LOW HIGH LOW -2.0 HIGH FL0124 JUN 0.0 OCT NA NA FS LOW LOW LOW MED 90 NONE 0.5 JUN SEP 5 1.5 D VP FS 22 Y NONE 50 JUN 0.5 SEP NA 155 1.5 NA -8 NONE 4 D P S -8 6 N NA 155 NA -9 0 -9 4 -8 NA P 1 NA -8 S N 155 NA NA UNDRAINED LOW MED NA HIGH HIGH NA -9 -8 -9 0 -8 C 2 NA MED HIGH HIGH HIGH NA -9 -9 0 HIGH MED 2 HIGH HIGH NA

E-106 Soil Classification Database Appendix E PINELLAS PINELLAS FINE SAND PINEDA FINE SAND, PINEDA FINE FLOODED FREQUENTLY PINEDA SAND FINE FLORAHOME - URBAN LAND FLORAHOME PCT SLOPES 5 TO 0 COMPLEX, TO 5 PCT SLOPES 5 PCT TO MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL095 95028SAND, 0 or FINE FLORAHOME 9 28 FL095 95029 or 29 11 FL095 95030 FL095 95031 or 30 7 31 or 6 FL095 95032 32 or 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 90 ENDSHWT FS DURSHWT FL0336 4.0HYDRIC 6.0HYDROGRPDRAINAGE JUNECOLCOMM DECMLRA 7MUKIND AANFLOOD FREQ NANFLOOD BEG MW NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH FL0336 NA -8 50SLOPE LOW S 154 FS NA HIGHSLOPE -8 4.0 LOWPANDEPTH 6.0 HIGHPANDEPTH JUNPANHARD DEC 0 -9OTHERPH 5 -9LEACH 7RUNOFFCORCON NA MW NCORSTEEL NONE NA NA NA FL0080 NA HIGH 154 -8 LOW NA C HIGH LOW -8 90 FS FL0479 0.0 1.0 JUN -9 0 NOV -9 5 90 FS 0.0 6 JUN NA 1.0 NOV NONE D P NA 26 Y HIGH FL0079 LOW HIGH LOW FREQ NA 155 6 NA -8 D P S 21 -8 Y 90 FS JUL 155 0.5 SEP JUN -9 SEP 0 -8 1.5 -9 2 S -8 NONE NA NA LOW -9 HIGH 0 -9 LOW HIGH 4 1 D P 12 N NA LOW NA NA HIGH 155 LOW NA HIGH -8 -8 S -9 -9 0 2 MED NA HIGH LOW HIGH NA

E-107 Appendix E Soil Classification Database ST. JOHNS ST. FINE SAND POMPANO POMPANO FINE SAND POMELLO - URBAN LAND COMPLEX, - URBAN LAND POMELLO PCT SLOPES 5 TO 0 0 TO 5 PCT SLOPES 5 TO 0 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL095 95033 or PITS 11 33 FL095 95034 SAND, POMELLO FINE or 9 34 FL095 95035 or 35 11 FL095 95036 FL095 95037 36 or 7 37 or 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT VAR DURSHWT DC0028 0.0HYDRIC FL0078 6.0HYDROGRP FS 90DRAINAGE NAECOLCOMM 2.0 NAMLRA -9 3.5MUKIND JUL NAANFLOOD FREQ NOV NANFLOOD BEG E NA 5ANFLOOD END NONE HIGHROCKDEPTH C FL0078 LOWROCKDEPTH N NA NONE -8 3SLOPE LOW MW M 155 NA FS HIGHSLOPE -8 50 LOWPANDEPTH 2.0 NA HIGHPANDEPTH 155 -8 NA 3.5PANHARD S 0 JUL -8 -9OTHERPH NOV 4 -9LEACHRUNOFFCORCON 5 -9 0CORSTEEL NONE NA -9 5 NA MW N NA NA NA MED HIGH NA FL0032 155 NA ND ND NA -8 C MED MED -8 FL0125 HIGH LOW FS 90 -9 0.0 0 -9 5 0.5 JUN OCT FS NA 90 NA 0.5 NONE MED MED 1.5 JUN 5 OCT D HIGH LOW P Y 26 NONE NA 155 NA 5 D -8 P S -8 6 N 155 NA NA -9 -8 0 -9 2 S -8 NA NA HIGH HIGH -9 MED -9 HIGH 0 2 NA MED HIGH NA HIGH HIGH

E-108 Soil Classification Database Appendix E SAMSULA - HONTOON - BASINGER - HONTOON - SAMSULA DEPRESSIONAL ASSOCIATION, SAMSULA SAMSULA MUCK ST. LUCIE - URBAN LAND LUCIE ST. PCT SLOPES 5 TO 0 COMPLEX, 0 TO 5 PCT SLOPES 5 TO 0 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL095 95038 FINE SAND, LUCIE or ST. 10 38 FL095 95039 or 11 39 FL095 95040 FL095 5 or 40 95041 or 41 5 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0057 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND AANFLOOD FREQ NANFLOOD BEG E 3 FL0057ANFLOOD END 55 NONE HIGHROCKDEPTH FS LOWROCKDEPTH 6.0 NA -8SLOPE LOW S 154 NA 6.0 HIGHSLOPE -8 NA LOWPANDEPTH NA HIGHPANDEPTH PANHARD -9 0 -9OTHERPH 5 -9 NALEACH NRUNOFF NONE E NACORCONCORSTEEL NA FL0092 NA NA 154 -8 NA C -8 90 MUCK HIGH LOW FL0092 MED -2.0 LOW 1.0 -9 0 JUN -9 5 MUCK OCT 50 5 -2.0 NA NONE D 1.0 NA JUN Y OCT HIGH 25 VP LOW MED LOW NONE NA 155 5 NA -8 D S -8 Y VP 17 NA 155 -9 NA 0 -9 -8 1 A -8 NA UNDRAINED LOW HIGH -9 UNDRAINED 0 HIGH -9 HIGH 1 NA LOW HIGH HIGH HIGH

E-109 Appendix E Soil Classification Database TAVARES FINE SAND, FINE TAVARES 5 PCT 0 TO SLOPES SMYRNA - URBAN SMYRNA COMPLEX LAND SMYRNA SMYRNA SAND FINE SEFFNER SEFFNER SAND FINE MUCK MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL095 95042 or SANIBEL 5 42 FL095 95043 or 43 9 FL095 95044 FL095 95045 or 44 8 or 45 FL095 11 95046 46 or 9 COMPPCT 19090904590 SSC S 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG ENDSHWT MUCK DURSHWT FL0073 -1.0HYDRIC 1.0HYDROGRPDRAINAGEVPSPSPSPMW JUN FS FL0426ECOLCOMM2566NA4 OCTMLRA 5MUKINDS 1.5 DANFLOOD FREQ FL0091 Y 3.5ANFLOOD BEG JUN FSANFLOOD END NOV NONE HIGHROCKDEPTH FL0091 LOWROCKDEPTH 0.5 6 NA -8SLOPE LOW 155 NA 1.5 JUN C HIGHSLOPE -8 SEP N FS LOWPANDEPTH NONE HIGHPANDEPTH PANHARD 0.5 0 -9 FL0021 OTHERPH NA 4 JUN 1 1.5 -9 NONE 155 SEP -8LEACH NA DRUNOFF -8 NCORCONCORSTEEL NONE NA NA FS UNDRAINED 155 -9 4 0 NA -8 -9 2 NA NA -8 3.5 N LOW HIGH JUN DEC LOW 6.0 HIGH NA NA 155 NA -9 NONE 0 -8 -9 NA 2 HIGH MED -8 LOW MED NA 7 A -9 MED N HIGH NA 0 -9 HIGH HIGH 2 NA 154 NA NA -8 MED HIGH HIGH -8 HIGH NA -9 -9 0 5 LOW NA HIGH LOW HIGH

E-110 Soil Classification Database Appendix E WABASSO WABASSO FINE SAND URBAN LAND TERRA CEIA TERRA CEIA MUCK TAVARES - URBAN 0 LAND COMPLEX, TAVARES 5 PCT SLOPES TO 0 TO 5 PCT SLOPES 5 TO 0 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL095 95047 FINE SANDS, AND MILLHOPPER or TAVARES 9 47 FL095 95048 or 48 11 FL095 95049 or FL095 49 5 95050 FL095 95051 50 or 11 51 or 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 65 ENDSHWT FS DURSHWT FL0021 3.5HYDRIC 6.0HYDROGRPDRAINAGE JUNECOLCOMM DECMLRA 7MUKIND AANFLOOD FREQ NANFLOOD BEG MW 4ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW U 154 NA HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 -9 FL0021OTHERPH 50 5 -9 FSLEACHRUNOFF 3.5CORCON 6.0CORSTEEL JUN NA DEC NA 7 HIGH LOW NA HIGH LOW MW N NONE NA NA 154 -8 NA FL0031 C -8 90 MUCK DC0035 -1.0 -9 0 -9 FL0075 5 1.0 JUN OCT VAR NA 95 NA 2.0 5 FS NONE D NA VP HIGH 2.0 NA LOW Y HIGH 90 LOW ND 0.5 JUN 1.5 NA SEP NONE 155 NA -8 -9 NA S NONE NA -8 N NA SP 4 D NA 155 -9 0 NA -9 6 1 -8 N M -8 NA 155 NA NA DRAINED -8 LOW HIGH MED -9 S -8 MED 0 -9 5 NA NA -9 MED HIGH -9 0 NA ND ND 2 LOW NA HIGH HIGH MED

E-111 Appendix E Soil Classification Database NO DATA WATER ZOLFO - ZOLFO URBAN COMPLEX LAND ZOLFO ZOLFO SAND FINE WAUBERG WAUBERG SAND FINE LAND COMPLEX MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL095 95052URBAN - or WABASSO 11 52 FL095 95053 or 7 53 FL095 95054 FL095 95055 or 54 9 55 or FL095 11 95098 FL095 95099 98 or 12 99 or 1 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 60 ENDSHWT FS DURSHWT FL0075 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4MUKIND NAANFLOOD FREQ N FL0346ANFLOOD BEG SP 90 NA FSANFLOOD END NONE HIGHROCKDEPTH 0.0 FL0288 LOWROCKDEPTH 1.0 NA -8 JUNSLOPE LOW C 155 NA DEC HIGHSLOPE -8 90 LOW FSPANDEPTH FL0288 HIGHPANDEPTH 7 2.0PANHARD D 3.5 JUN 0 -9OTHERPH NOV Y 2 -9 P NONE 22LEACH 55RUNOFF FS NACORCON 2.0 NA 6 JUNCORSTEEL 3.5 155 NA NONE -8 NOV C NA S NA -8 N 11 SP DC0038 LOW HIGH NONE NA HIGH MED 155 -9 0 6 0 NA NA -8 -9 NA 2 -9 S NA -8 SP NA NA N -9 NA NA NA 155 NA 100 NA NA -9 NA -9 0 -8 NA -9 2 -9 LOW HIGH CM -8 MED HIGH NA -9 NA NA NA NA NA NA -9 MED MED 0 -9 NA NA MED LOW NA 2 NA -9 NA NA -9 NA NA NA -9 MED NA MED NA NA MED LOW NA -9 M -9 -9 -9 -9 -9 NA NA NA NA NA NA -9 -9 -9 -9 NA NA NA NA NA NA

E-112 Soil Classification Database Appendix E CANDLER FINE SAND, 0 5 PCT SLOPES TO APOPKA FINE SAND, APOPKA FINE 5 PCT 0 TO SLOPES R EAUGALLIE CHOBEE ZEPHY SELLER S A MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL101 101001 ps WAUCHULA 0 1 POMON FL101 101002 101008 ps FL101 0 2 101035 FL101 ps 101039 0 8 FL101 101060 ps 105002 FL101 0 35 FL105 ps 39 0 105003 ps FL105 60 0 po 2 10 po 3 10 HTLW999999. 6.0 E LOW-9-9-9-9-9-96.0 1S5ID 1COMPPCT 1SURFTEXT HIGHSHWT SHWT BEGSHWT 0 ENDSHWT NA DURSHWT OUT -9HYDRICHYDROGRPDRAINAGENANANANANANAW NAECOLCOMM NA 0 NA OUTMLRA -9MUKIND -9 NAANFLOOD FREQ NAANFLOOD BEG OUT NA NA NAANFLOOD END 0 NA NA HIGHROCKDEPTH -9 -9 LOWROCKDEPTH OUT NA -9SLOPE LOW NA NA NA NA NA NA NA HIGHSLOPE -9 NA NA LOW 0PANDEPTH HIGHPANDEPTH NA -9 -9 OUT NAPANHARD NA -9 NA NA -9OTHERPH NA -9 -9 -9 NA NA NA NA NALEACH -9RUNOFF NA OUT -9 NA 0CORCON NA NA -9CORSTEEL NA NA NA NA NA NA NA -9 FL0024 -9 NA -9 NA NA -9 -9 -9 0 NA NA FS NA NA -9 -9 NA NA NA NA NA NA NA -9 NA -9 NA -9 NA -9 -9 -9 NA NA 90 NA NA 6.0 -9 FL0003 NA NA NA NA NA NA NA NA NA NA -9 -9 NA NA NA -9 -9 -9 NA A N -9 -9 NA NA 4 NA S NA NA NA NA NA NA NONE NA -9 -9 -9 NA -9 -9 -9 S 154 NA NA NA NA 90 6.0 NA NA NA NA -8 NA -9 -9 -8 -9 -9 A N -9 NA NA NONE NA NA NA 4 NA 0 -9 5 -9 NA NA NA 154 NA NA S NA NA NA -8 MED LOW -8 HIGH MED -9 0 -9 5 NA NA HIGH LOW HIGH LOW

E-113 Appendix E Soil Classification Database SAND SLICKENS LYNNE POMONA SAND FINE EATON MUCKY FINE EATON SAND, DEPRESSIONAL EAUGALLIE EAUGALLIE SAND FINE 5 TO 8 PCT SLOPES 8 TO 5 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT S DURSHWT FL0003 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND AANFLOOD FREQ NANFLOOD BEG E 4 FL0154ANFLOOD END 90 NONE HIGHROCKDEPTH FS LOWROCKDEPTH 0.5 NA -8SLOPE LOW S 154 NA FL0427 1.5 HIGHSLOPE -8 JUN LOWPANDEPTH SEP HIGHPANDEPTH 90PANHARD 4 MK-FS 5 -2.0 -9OTHERPH 8 -9 0.0 DLEACH JUN NRUNOFF NONE P MAR 6CORCONCORSTEEL FL0007 NA NA 10 NA 155 -8 NA NONE S D -8 FL8008 Y HIGH LOW FS VP HIGH 25 LOW 90 0.5 FL0009 NA -9 155 0 NA -9 1.5 -8 2 JUN SEP S -8 VAR 95 NA 0.0 NONE NA 4 JAN -9 2.0 DEC 0 S -9 LOW 2 HIGH D MED HIGH N NONE 90 P 0.5 6 JUL NA SEP NA 1.5 155 NA 12 LOW NA HIGH NONE -8 HIGH HIGH NA S -8 Y P NA 155 NA 3 NA -9 -8 D 0 -9 2 -8 M N SP 155 6 NA NA NA LOW HIGH NA HIGH HIGH -9 -8 -9 0 -8 S 1 HIGH LOW NA HIGH HIGH NA -9 -9 0 HIGH LOW 2 HIGH HIGH NA NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL105 105004 poFINE SAND, CANDLER 10 4 FL105 105005 po 8 5 105006 FL105 po 6 6 105007 FL105 105008 FL105 105009 po FL105 8 7 po 11 8 po 8 9

E-114 Soil Classification Database Appendix E URBAN LAND TAVARES FINE SAND, FINE TAVARES 5 PCT 0 TO SLOPES SAMSULA SAMSULA MUCK NEILHURST SAND, 1 TO 5 PCT 5 TO SAND, 1 NEILHURST SLOPES ARENTS - WATER ARENTS - WATER COMPLEX FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT FS DURSHWT FL0123 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0085 50ECOLCOMM NOV VARMLRA 6 6.0MUKIND D 6.0ANFLOOD FREQ Y NAANFLOOD BEG P NA 26ANFLOOD END NONE HIGHROCKDEPTH -9 LOWROCKDEPTH NA FL0480 -8SLOPE LOW NA S 155 NA HIGHSLOPE -8 N NONE W NA LOW SPANDEPTH 90 HIGHPANDEPTH 6.0PANHARD NA 0 -9OTHERPH 6.0 155 -8 2 NA -9 NALEACH C -8 NARUNOFFCORCONCORSTEEL -9 NA -9 NONE 35 A NA -9 FL0092 65 N NA E LOW HIGH LOW HIGH NA NA FL0021 155 NA NA -8 90 MUCK S -8 -2.0 MED HIGH LOW LOW 0.0 JUN APR FS 1 -9 5 -9 90 NONE 3.5 11 DC0035 6.0 JUN D NA DEC 22 NA Y LOW VP NONE HIGH LOW HIGH NA 155 NA 7 -8 A VAR S -8 4 N MW 90 2.0 154 NA NA 2.0 NA -9 NA 0 -9 -8 2 NONE -8 S NA HIGH LOW UNDRAINED HIGH HIGH -9 NA -9 0 -9 NA 5 NA NA N LOW 154 NA HIGH NA HIGH LOW NA -8 -8 M NA -9 -9 0 HIGH HIGH 8 ND NA ND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL105 105010 po MALABAR 7 10 FL105 105011 po 11 11 105012 FL105 po 12 10 105013 FL105 105015 FL105 po 13 5 po 105016 15 9 FL105 po 16 11

E-115 Appendix E Soil Classification Database POMELLO FINE SAND SPARR SAND, 0 SPARR 5 PCT SLOPES TO FORT MEADE FINE SAND, MEADE FORT 5 PCT 0 TO SLOPES FLORIDANA MUCKY FINE MUCKY FINE FLORIDANA SAND, DEPRESSIONAL MYAKKA FINE SANDS MYAKKA S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 60 ENDSHWT FS DURSHWT FL0091 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4MUKIND DANFLOOD FREQ NANFLOOD BEG SP 6 FL0262ANFLOOD END 90 MK-FS NONE HIGHROCKDEPTH LOWROCKDEPTH -2.0 NA -8SLOPE LOW 0.0 U 155 NA JUN HIGHSLOPE -8 MAR LOWPANDEPTH HIGHPANDEPTH PANHARD 10 0 -9OTHERPH 2 -9 DLEACH Y VP NONERUNOFF 25 FL0120CORCONCORSTEEL FS NA NA 155 90 NA -8 NA S -8 6.0 MED HIGH 6.0 NA HIGH HIGH NA -9 0 -9 2 -9 FL0008 NONE A W NA N NA 11 S LOW HIGH NA 90 154 LOW MED NA -8 1.5 FL0078 S -8 3.5 JUL OCT -9 0 NONE -9 4 5 FS 90 C SP 2.0 NA N 11 JUL NA 3.5 NOV LOW HIGH NA 154 HIGH LOW NA NONE -8 S -8 5 MW C -9 N 3 0 -9 5 NA NA NA -8 MED MED NA HIGH -8 S MED -9 -9 0 2 NA MED MED HIGH NA LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL105 105017 po SMYRNA AND 8 17 FL105 105019 po 19 6 105020 FL105 po 20 10 105014 FL105 po 105022 14 9 FL105 po 22 9

E-116 Soil Classification Database Appendix E KENDRICK FINE SAND, KENDRICK FINE 5 PCT 0 TO SLOPES LOCHLOOSA FINE SAND PLACID AND MYAKKAFINE AND MYAKKAFINE PLACID SANDS, DEPRESSIONAL NITTAW SANDY CLAY LOAM, SANDY CLAY NITTAW FLOODED FREQUENTLY SAND S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT FS DURSHWT FL0124 0.5HYDRIC 1.5HYDROGRP FL0210DRAINAGE JUN 90ECOLCOMM SEP SCLMLRA 4 0.0MUKIND 0.5 DANFLOOD FREQ JUN NANFLOOD BEG OCT P 6ANFLOOD END NONE HIGHROCKDEPTH 5 LOWROCKDEPTH NA -8 DSLOPE LOW S 155 NA Y HIGHSLOPE -8 FREQ VP LOWPANDEPTH 21 HIGHPANDEPTH FL0287PANHARD JUN 0 -9 155 -8OTHERPH SEP 2 -9 SLEACH -8 FS 60RUNOFFCORCON -2.0CORSTEEL 1.0 JUN NA -9 0 MAR NA -9 2 MED HIGH 10 HIGH HIGH NA NONE FL0015 NA D Y VP LOW HIGH 25 HIGH HIGH NA FL0005 FS 155 NA 90 -8 2.5 U -8 JUL 5.0 OCT -9 FS 0 90 -9 NONE 2 6.0 4 NA NA 6.0 B NA SP N 11 NA HIGH NONE HIGH NA HIGH HIGH 154 NA -8 -9 S -8 W A N 11 NA 155 NA -9 0 -9 -8 2 -8 S NA MED LOW NA HIGH HIGH -9 -9 0 5 LOW NA LOW HIGH MED NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL105 105023 po ONA FINE 8 23 FL105 105024 po 24 6 105025 FL105 po 25 6 105026 FL105 105027 FL105 po 26 9 po 27 10

E-117 Appendix E Soil Classification Database ANCLOTE MUCKY FINE ANCLOTE MUCKY FINE SAND, DEPRESSIONAL HOLOPAW FINE SAND, HOLOPAW DEPRESSIONAL NA NA KALIGA KALIGA MUCK D FINE SAND FINE POMPANO ADAMSVILLE 0 TO 5 PCT SLOPES 5 TO 0 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL105 105029 FINE SAND, LUCIE po ST. 10 29 FL105 105030 po 7 105031 30 FL105 105032 po 31 FL105 9 105033 FL105 po 32 5 po 33 105034 6 FL105 po 34 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 90 ENDSHWT FS DURSHWT FL0057 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND AANFLOOD FREQ NANFLOOD BEG E FL0032 3ANFLOOD END 90 FS NONE HIGHROCKDEPTH LOWROCKDEPTH 0.0 NA FL0036 -8SLOPE LOW 0.5 S 154 NA HIGHSLOPE -8 JUN LOWPANDEPTH 90 OCT FS HIGHPANDEPTH 5 FL0209 2.0PANHARD 0 -9 3.5OTHERPH 5 -9 JUN D FL0264 Y NOV NONE PLEACH 26RUNOFF 90 MUCK 6CORCON NA NA -2.0 NONECORSTEEL 155 -8 NA NA C 0.0 JUN S FS N -8 APR SP 6 90 -2.0 HIGH NA LOW JUN 154 NONE 0.0 FL0315 MED MAR LOW NA -9 0 -8 11 -9 2 S -8 NONE D Y VP 24 NA 10 NA -9 155 NA 0 -9 NA 2 D -8 FS VP Y HIGH S -8 25 HIGH 90 -2.0 155 NA NA MED HIGH JUN MAR NA NA 0.0 -8 HIGH NONE -9 MED -8 0 -9 S LOW MED 1 NA 10 -9 DRAINE LOW -9 0 HIGH 2 VP D HIGH HIGH NA Y 25 155 LOW NA HIGH NA HIGH MED -8 -8 S -9 -9 0 2 MED NA HIGH HIGH MED

E-118 Soil Classification Database Appendix E WAUCHULA WAUCHULA FINE SAND ARENTS, CLAYEY ARENTS, CLAYEY SUBSTRATUM ELECTRA ELECTRA FINE SAND PLACID FINE SAND, PLACID FLOODED FREQUENTLY BASINGER MUCKY FINE BASINGER MUCKY SAND, DEPRESSIONAL MUCK MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL105 105035 po HONTOON 5 35 FL105 105036 po 36 6 105037 FL105 po 37 6 105038 FL105 105039 FL105 po 38 9 105040 po FL105 39 11 po 40 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 90 ENDSHWT MUCK DURSHWT FL0090 -2.0HYDRIC 0.0HYDROGRPDRAINAGEVPVPVPSPSPP JUN MK-FS FL0261ECOLCOMM APR 90MLRA 11 -2.0MUKINDSSSSMS DANFLOOD FREQ 0.0 Y JUNANFLOOD BEG 22 MARANFLOOD END NONE HIGHROCKDEPTH 10 LOWROCKDEPTH NA -8SLOPE LOW 154 NA D HIGHSLOPE -8 Y FS FL0444 NONE LOWPANDEPTH 25 HIGHPANDEPTH PANHARD 90 0 NA -9OTHERPH 0.0 155 1 -8 -9 NALEACH -8 1.0RUNOFF JUN NOVCORCONCORSTEEL NA -9 UNDRAINED 6 0 -9 2 FL0010 NA FREQ MED D HIGH FS Y HIGH HIGH 22 FL0097 NA 90 JUN 155 2.0 LOW HIGH NOV -8 FS MED HIGH JUL 3.5 OCT -8 FL0153 90 1.5 -9 NONE JUN NOV 4 0 3.0 -9 NA 2 C NONE N 3 NA FS NA HIGH 155 HIGH NA 6 HIGH HIGH -8 90 0.5 NA SEP JUN -8 N NA 1.5 NA 155 NONE NA -9 -8 NA 0 -9 -8 2 4 NA MED LOW D LOW HIGH NA -9 6 N -9 NA 155 0 NA 5 MED NA LOW MED HIGH -8 -8 NA -9 -9 0 HIGH LOW 2 HIGH HIGH NA

E-119 Appendix E Soil Classification Database CHOBEE FINE SANDY CHOBEE FINE SANDY DEPRESSIONAL LOAM, ZOLFO ZOLFO FINE SAND ASTATULA FINE SAND, FINE ASTATULA 5 PCT 0 TO SLOPES PAISLEY PAISLEY SAND FINE OLDSMAR SAND FINE FELDA FELDA SAND FINE SAND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE77881096 MAPUNIT NAME FL105 105041 JOHNS po ST. 41 FL105 105042 po 42 105043 FL105 105044 FL105 po 43 105046 FL105 po 44 po 46 105047 FL105 105048 FL105 po 47 po 48 OKET O------8-8 -9-9 9090 NANA 19090909090 LOW-8-8-8-8-8 SPVP CD NANA LOW-9-9-9-9-9 21 ENDNANANANANA 00 DUR5944-9610 LOW00000 HIGH22218 SS 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT ENDSHWT SSHWT FL0125 0.0HYDRIC 0.5HYDROGRPDDDDA DRAINAGEPPPSPE JUN FL0127ECOLCOMM OCTMLRA FS 0.0MUKINDSSSSS FL0067 1.0ANFLOOD FREQ N JULANFLOOD BEG MAR 10ANFLOOD FL0016 NONE HIGHROCKDEPTH FS 0.5ROCKDEPTH NA -8 1.5SLOPE JUN 155 SEP FL0019SLOPE Y NONE 26PANDEPTH HIGHPANDEPTH FS 1.0PANHARD NA JUN 1.5OTHERPHNANANANANA NONE SEP 155 -8 -9LEACH NRUNOFF 6CORCON FS NONE 6.0CORSTEEL NA NA NA NA 6.0 155 FL0288 -8 -9 N NONE MED 6 HIGH FL0412 HIGH HIGH NA NA 155 -8 -9 MED HIGH N MED HIGH 3 FS NA 154 NA 2.0 JUN NOV 3.5 HIGH LOW -8 -9 NONE MED HIGH FSL NA JUN MAR -2.0 HIGH LOW NONE 0.0 MED HIGH -9 LOW N NA HIGH 155 LOW NA 11 HIGH -8 155 Y NA 25 -8 -9 MED MED MED NA LOW HIGH LOW -9 HIGH HIGH NA

E-120 Soil Classification Database Appendix E POMONA - URBANPOMONA - LAND COMPLEX CANDLER - URBAN LAND CANDLER - PCT SLOPES 5 TO 0 COMPLEX, ADAMSVILLE - URBAN ADAMSVILLE LAND COMPLEX LOAM, DEPRESSIONAL LOAM, MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL105 105048SANDY po CHOBEE FINE 48 6 FL105 105049 po 49 11 105050 FL105 po 50 11 105051 FL105 po 51 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT FSL DURSHWT FL0412 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END FL0036 75 FS NONE HIGHROCKDEPTH LOWROCKDEPTH 2.0 NA -8SLOPE LOW S 155 NA 3.5 HIGHSLOPE -8 JUN LOWPANDEPTH NOV HIGHPANDEPTH PANHARD 6 0 -9OTHERPH 1 -9 FL0003LEACH NA NRUNOFF SP NONE NACORCON FS 55CORSTEEL NA 6.0 NA NA 155 -8 NA 6.0 NA C NA -8 LOW HIGH HIGH HIGH -9 0 0 NONE NA 0 2 E N NA FL0007 NA 154 NA NA -8 HIGH C MED FS -8 55 MED LOW 0.5 1.5 JUN SEP -9 0 -9 5 NONE 4 NA NA NA HIGH LOW NA P N HIGH LOW NA 155 NA -8 C -8 -9 0 -9 2 MED NA HIGH NA HIGH HIGH

E-121 Appendix E Soil Classification Database PITS HAPLAQUENTS, CLAYEY SPARR - URBAN LAND SPARR PCT SLOPES 5 TO 0 COMPLEX, POMELLO POMELLO - URBAN LAND COMPLEX URBAN LAND COMPLEXURBAN LAND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL105 105053 - - IMMOKALEE po MYAKKA 11 53 FL105 105054 po 11 54 105055 FL105 po 11 55 105057 FL105 105058 po 6 FL105 57 po 58 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 40 ENDSHWT FS DURSHWT FL0059 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4MUKIND NAANFLOOD FREQ NANFLOOD BEG SP NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH FL0078 NA -8 60SLOPE LOW C 155 FS NA HIGHSLOPE -8 2.0 LOWPANDEPTH 3.5 HIGHPANDEPTH JULPANHARD NOV 0 -9OTHERPH 2 -9LEACH 5RUNOFF NACORCON FL0008 NCORSTEEL MW NONE NA NA NA 55 S NA 1.5 MED 154 -8 HIGH NA 3.5 C HIGH JUL HIGH -8 OCT -9 4 0 NA NONE -9 2 SP NA N FL8007 NA NA NA 155 NA -8 MED MED C -8 95 HIGH LOW DC0028 C -1.0 1.0 JUN OCT -9 0 -9 5 NONE D NA 90 5 0.0 NA VP VAR NA NA MED MED NA 6.0 Y HIGH MED NA 155 NONE NA -8 M -8 NA E -9 NA N -9 154 NA 0 -9 1 NA -8 NA M -8 NA LOW HIGH LOW MED -9 -9 1 4 NA LOW LOW ND NA ND

E-122 Soil Classification Database Appendix E WABASSO WABASSO FINE SAND ARENTS, ORGANIC SUBSTR.- ORGANIC SUBSTR.- ARENTS, COMPLEX LAND URBAN ARENTS SAND 0 TO 5 PCT SLOPES 5 TO 0 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL105 105059 po- URBAN LAND COMPLEX, ARENTS 11 59 FL105 105060 105061 po FL105 11 60 po 11 61 105062 FL105 po 8 62 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 55 ENDSHWT S DURSHWT FL0097 1.5HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND NAANFLOOD FREQ NANFLOOD BEG SP NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C 155 NA HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH FL0070 95PANHARD 0 -9 SOTHERPH FL0083 5 -9 2.0LEACH 4.0RUNOFF JUN 50CORCON JANCORSTEEL S 2.0 NA 8 NA 3.0 JUN NA NOV N MED MW MED NONE NA MED HIGH 6 NA NONE NA SP 155 -8 NA NA N FL0075 M -8 NA 155 NA -8 -9 0 C 90 -8 -9 2 0.5 FS JUN 1.5 SEP NA -9 0 -9 NA 2 NONE MED LOW D HIGH HIGH 4 NA SP NA 6 N MED LOW HIGH HIGH NA 155 NA -8 S -8 -9 0 -9 2 NA NA LOW HIGH MED HIGH

E-123 Appendix E Soil Classification Database BRADENTON BRADENTON FINE SAND FORT MEADE - URBAN LAND MEADE FORT PCT SLOPES 5 TO 0 COMPLEX, NEILHURST - URBAN LAND NEILHURST PCT SLOPES 5 TO 1 COMPLEX, COMPLEX, 0 TO 5 PCT SLOPES 5 TO 0 COMPLEX, COMPPCT 175555590 DUR7-9-94 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT ENDSHWT SSHWT FL0021 3.5HYDRIC 6.0HYDROGRPDRAINAGE JUNECOLCOMM DECMLRAMUKINDCCCS NAANFLOOD FREQ NANFLOOD BEG MW NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW 154 NA HIGHSLOPE -8 FL0480 LOWPANDEPTH HIGHPANDEPTH S 6.0PANHARD 0 -9 6.0OTHERPH 2 -9 NALEACH NARUNOFFCORCONCORSTEEL NA NA NA E N NONE NA HIGH LOW HIGH LOW FL0120 NA 155 -8 NA -8 S 6.0 6.0 -9 NA 1 -9 NA 5 NA NA NONE NA W NA N HIGH FL0232 LOW HIGH LOW NA 154 NA -8 -8 0.5 FS 1.5 JUN -9 0 SEP -9 5 NONE D NA NA HIGH 12 LOW SP HIGH N LOW NA 155 NA -8 -8 -9 0 -9 2 NA LOW NA HIGH LOW HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL105 105063URBANLAND - po TAVARES 11 63 FL105 105064 po 11 64 105066 FL105 po 11 66 105067 FL105 po 8 67

E-124 Soil Classification Database Appendix E GYPSUM SPOIL BRADENTON - FELDA - CHOBEE FELDA - - BRADENTON FLOODED FREQUENTLY ASSOCIATION, DUETTE DUETTE SAND FINE UNKNOWN CODE 5 PCT SLOPES 5 S5ID 1S5ID 1COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT S DURSHWT FL0097 1.5HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA NA 6 0MUKIND NA NAANFLOOD FREQ N -9ANFLOOD BEG SP NA -9ANFLOOD END NA NONE HIGHROCKDEPTH NA FL0323 LOWROCKDEPTH NA 90 -8 FS LOWSLOPE M 155 NA -9 HIGHSLOPE -8 4.0 FL0348 NA LOWPANDEPTH 6.0 JUN NA HIGH NAPANDEPTH NA OCT NAPANHARD 0 40 -9OTHERPH FS 2 -9LEACH 0.0 5 NA A NA JUN -9RUNOFF NA 1.0 NA SEP NCORCON MW -9 NONE 3CORSTEEL NA NA NA 4 -9 155 FREQ -9 D NA -8 -9 S P -9 MED MED Y -8 MED HIGH 21 NA JUN 155 NA NOV -9 0 -8 -9 DC0017 A 2 NA NA -8 NA NA NA NA -9 0 95 -9 GYP MED 2 LOW 6.0 LOW HIGH NA NA 6.0 NA NA LOW HIGH LOW HIGH NONE -9 NA NA N NA NA 155 NA -8 M -8 -9 0 -9 2 NA NA LOW MED HIGH HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL105 105068 0 TO po ARENTS, 11 68 FL105 105069 po 12 69 105070 FL105 105072 FL105 po 9 70 po 72 6 105073 FL105 po 73 11

E-125 Appendix E Soil Classification Database PAISLEY FINE SAND, PAISLEY SUBSTR. STONEY SATELLITE SATELLITE SAND MILLHOPPER FINE MILLHOPPER SAND, PCT SLOPES 5 TO 0 VALKARIA VALKARIA SAND SAND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL105 105074 po NARCOOSSEE 9 74 FL105 105075 po 105076 75 7 FL105 po 76 9 105077 FL105 105078 FL105 po 77 9 po 78 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 90 ENDSHWT S DURSHWT FL0156 2.0HYDRIC 3.5HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6 FL0126 90MUKIND C SANFLOOD FREQ N 0.0ANFLOOD BEG FL0247 SP 1.0ANFLOOD END 11 JUN NONE HIGHROCKDEPTH SEP 90 LOWROCKDEPTH NA -8SLOPE LOW S FS 155 NA 3.5 4 HIGHSLOPE -8 6.0 AUG LOWPANDEPTH D FEB HIGH YPANDEPTH P NONEPANHARD 26 0 -9OTHERPH 2 -9LEACH 7 NA FL0102 NONERUNOFF 155 -8 NA A SCORCON -8 N MWCORSTEEL NA 11 FL0438 NA NA 90 154 -9 NA 0 -8 S 1.5 -9 MED 2 MED JUN S -8 3.5 HIGH MED NOV NA 90 -9 NA NONE 0 1.0 JUN -9 FS 5 SEP 1.5 HIGH 6 HIGH MED HIGH SP C N NA RARE 3 NA LOW LOW NA 155 MED LOW NA -8 4 P D S -8 N 6 NA 155 NA -9 -8 0 -9 2 -8 S NA HIGH NA MED MED LOW -9 -9 0 2 LOW NA HIGH NA MED HIGH

E-126 Soil Classification Database Appendix E ARCHBOLD SAND, 5 PCT 0 TO SLOPES FELDA FINE SAND, FELDA FLOODED FREQUENTLY ST. AUGUSTINE ST. SAND FREQUENTLY FLOODED FREQUENTLY S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 90 ENDSHWT FSL DURSHWT FL0040 0.0HYDRIC 0.5HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKIND DANFLOOD FREQ YANFLOOD BEG VP 21ANFLOOD END FREQ HIGHROCKDEPTH LOWROCKDEPTH JUN -8SLOPE LOW FL0320 S FEB 155 95 S HIGHSLOPE -8 LOWPANDEPTH 1.5 HIGHPANDEPTH 3.0PANHARD JUL 0 -9OTHERPH OCT 2 -9 FL0329LEACHRUNOFF 4CORCON 90 FSCORSTEEL C NA N SP 0.0 NONE NA NA 1.0 JUL MAR NA LOW HIGH NA LOW 155 -8 MED S -8 FL0434 9 FREQ D P Y 21 -9 0 -9 2 90 JUL S FEB 155 3.5 -8 JUN 6.0 NOV S -8 NA NA HIGH MED NONE HIGH -9 HIGH 0 -9 6 2 A MW 3 N NA NA NA NA MED 155 HIGH MED HIGH -8 S -8 -9 0 -9 5 NA HIGH LOW NA LOW MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL105 105080 SANDY LOAM, po CHOBEE FINE 6 80 FL105 105081 po 81 9 105082 FL105 po 82 6 105083 FL105 po 83 9

E-127 Appendix E Soil Classification Database UNKNOWN CODE NO DATA WATER BASINGER SAND FINE FELDA FINE SAND, FELDA DEPRESSIONAL DEPRESSIONAL MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL105 105085 poFINE SAND, WINDER 6 85 FL105 105086 po 86 6 105087 FL105 105092 FL105 po 87 7 105098 po 92 FL105 12 105099 FL105 po 98 12 po 99 1 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT FS DURSHWT FL0283 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ Y FL0298ANFLOOD BEG VP 90 25ANFLOOD END FS NONE -2.0 HIGHROCKDEPTH LOWROCKDEPTH NA 1.0 -8 LOWSLOPE JUN S 155 NA DEC HIGHSLOPE -8 LOWPANDEPTH FL0063 7 HIGHPANDEPTH PANHARD 0 -9 DOTHERPH 90 2 -9 Y VP FSLEACH NA NONE 0.0 17RUNOFFCORCON 1.0 JUN NA FEBCORSTEEL NA 155 -8 NA NA S 0 -8 NA -9 9 LOW NA HIGH -9 NONE NA LOW HIGH NA D P -9 0 Y 26 -9 2 NA NA 155 -9 DC0038 NA -8 NA NA 0 NA S -9 NA -8 NA NA NA NA NA MED HIGH -9 HIGH MED NA NA NA NA -9 0 100 -9 -9 -9 NA 2 NA NA -9 NA -9 -9 NA NA NA NA NA NA NA -9 HIGH HIGH -9 -9 HIGH MED NA -9 NA -9 NA NA NA NA NA NA -9 NA NA NA NA -9 NA NA NA NA NA -9 M -9 -9 -9 -9 -9 NA NA NA NA -9 NA NA -9 -9 -9 NA NA NA NA NA NA

E-128 Soil Classification Database Appendix E ADAMSVILLE VARIANT FINE VARIANT ADAMSVILLE SLOPES 5 PCT SAND, O TO SAND S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 0 ENDSHWT NA DURSHWT OUT -9HYDRIC -9HYDROGRPDRAINAGE NA 0 NA OUTECOLCOMM NA -9MLRA -9MUKIND -9 NA NAANFLOOD FREQ NA OUT NAANFLOOD BEG NA NA NAANFLOOD END 0 -9 NA HIGHROCKDEPTH NA -9 LOWROCKDEPTH NA NA -9 OUT -9 NA NASLOPE LOW NA NA NA NA NA NA HIGHSLOPE -9 NA LOWPANDEPTH 0 OUT -9 HIGHPANDEPTH NA NA -9 -9PANHARD NA NA NA NA NA -9 NA -9 -9OTHERPH NA -9 -9 NA -9 OUT NALEACH 0 NARUNOFF -9 -9CORCON NA NA NA NA -9 -9 -9 FL0036CORSTEEL NA NA NA NA NA -9 NA -9 -9 NA NA NA -9 0 NA NA -9 -9 NA S NA NA -9 NA NA NA NA NA FL0082 NA NA NA NA NA NA NA -9 -9 -9 NA -9 -9 NA JUN 95 -9 2.0 -9 NA NA NA NOV NA NA 3.5 NA NA NA NA NA NA NA -9 NA FS C NA -9 -9 -9 N NA 6 -9 -9 SP NA NA NA 15 JUN NA NA 95 NOV 2.0 NONE -9 NA NA NA 3.5 -9 -9 -9 NA NA -9 -9 S 155 NA C NA NA N NA SP -8 6 NONE NA NA -9 15 NA -9 -8 -9 -9 NA NA NA NA NA 155 NA NA NA S 0 -9 2 -9 -8 NA NA NA NA NA -8 NA HIGH MED MED -9 LOW 0 -9 5 NA NA LOW MED MED HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL115 115009 sa DELRAY 0 9 EAUGALLIE FL115 115010 HOLOPAW sa PINEDA 0 115022 10 FL115 PAISLEY CHOBEE 115031 ADAMSVILLE FL115 119009 sa 22 0 FL119 119068 FL119 610001 sa 31 FL610 0 610002 sm 9 0 FL610 sm 68 0 os 1 9 os 2 9

E-129 Appendix E Soil Classification Database CANDLER SAND, 5 CANDLER SAND, SLOPES 12 PCT TO CANDLER SAND, OCANDLER SAND, 5 PCT SLOPES TO BASINGER FINE SAND, BASINGER FINE DEPRESSIONAL BASINGER SAND FINE ARENTS, O TO 5 TO O ARENTS, PCT SLOPES FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0086 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUL FL0097 95ECOLCOMM SEP SMLRA 3 1.5MUKIND D 3.0ANFLOOD FREQ N JUNANFLOOD BEG P NOV 6ANFLOOD END NONE FL0063 HIGHROCKDEPTH 6 LOWROCKDEPTH NA -8SLOPE LOW NA S 155 NA 95 N HIGHSLOPE -8 FL0261 NONE FS SP LOWPANDEPTH 0.0 NA HIGHPANDEPTH 1.0 JUNPANHARD FEB NA 0 30OTHERPH 155 -8 NA 2 50 95 MLEACH -8 FSRUNOFF -2.0 9CORCON JUN 0.0 NONE D MARCORSTEEL THIN -9 Y P 0 NA FL0003 -9 26 5 NONE NA LOW HIGH 155 NA 10 NA HIGH -8 HIGH D S -8 NA Y VP 25 HIGH MED 95 FL0003 MED NA HIGH 155 S 6.0 -9 NA NA NA 0 -8 -9 6.0 2 S -8 NA NONE NA -9 HIGH HIGH -9 -9 0 HIGH MED 2 A 95 NA E 6.0 4 N S NA NA HIGH 6.0 HIGH NA 154 NA HIGH MED NONE NA -8 -8 S -9 A -9 -9 E N 0 4 154 5 NA NA HIGH NA LOW LOW NA HIGH -8 -8 S -9 -9 HIGH 5 LOW NA 12 LOW HIGH NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL610 610003 os ANKONA 8 3 FL610 610004 os 11 4 610005 FL610 610006 FL610 os 7 5 os 6 6 610007 FL610 610008 os FL610 10 7 os 10 8

E-130 Soil Classification Database Appendix E HONTOON HONTOON MUCK HOLOPAW HOLOPAW SAND FINE FLORIDANA FLORIDANA SAND FINE EAUGALLIE EAUGALLIE SAND FINE DELRAY LOAMY LOAMY DELRAY SAND FINE FINE SAND FINE MUIDSTSSAIDMUSYM91011121415 CNTYABBRLSPOSCODE NAMEMAPUNIT FL610 610009 os CASSIA 9 FL610 610010 os 6 610011 FL610 610012 FL610 os 8 610014 FL610 os 610015 6 FL610 os 7 os 5 HTDR1410611 DUR7104 S S SS 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT FSSHWT FL0100 1.5HYDRIC 3.5HYDROGRPDRAINAGE JUL FL0299 95ECOLCOMM JAN FSMLRA -2.0MUKINDSS C 0.0ANFLOOD FREQ N JUNANFLOOD BEG SP 3 MARANFLOOD END FL0154 NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8 95SLOPE LOW FS D 155 NA FL0262 HIGHSLOPE -8 Y 0.5 VP NONE LOWPANDEPTH 25 1.5 HIGH JUNPANDEPTH SEPPANHARD NA FL0027 0 -9OTHERPH 155 -8 2 NA 95 -9 FSLEACH -8 -2.0RUNOFF FL0090 NONE JUN 0.0CORCON MAR D PCORSTEEL N NA -9 6 0 NA -9 2 95 FS NONE 0.0 NA 155 MED JUN NA MED NOV -8 1.0 HIGH MED NA -8 D VP Y NA NONE 25 MUCK 90 -2.0 MED HIGH JUN NA APR 155 LOW -9 MED NA 0.0 0 -9 -8 2 NONE -8 P D N NA 13 155 NA NA LOW NA HIGH -9 MED 0 -9 -8 HIGH 2 VP D -8 Y 25 NA 155 NA HIGH NA LOW NA LOW MED -9 -8 -9 0 -8 2 HIGH NA LOW NA MED HIGH -9 -9 0 HIGH LOW 2 NA HIGH HIGH DRAINED

E-131 Appendix E Soil Classification Database MYAKKA MYAKKA FINE SAND MALABAR - PINEDA - MALABAR COMPLEX MALABAR FINE FINE MALABAR SAND, DEPRESSIONAL GENTRY GENTRY SAND FINE LOKOSEE SAND FINE KALIGA KALIGA MUCK FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL610 610016 os IMMOKALEE 8 16 FL610 610017 610018 os FL610 17 5 610013 FL610 os 18 8 610020 FL610 os 13 6 os 610021 20 FL610 6 610022 FL610 os 21 7 os 22 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0058 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEP FL0031 90MLRA 4 MUCKMUKIND FL0390 -2.0 DANFLOOD FREQ N 0.0ANFLOOD BEG FS P JUN 6ANFLOOD END 95 APR FL0207 NONE HIGHROCKDEPTH 0.5 LOWROCKDEPTH NA 11 -8 1.5SLOPE LOW JUN S 155 NA SEP HIGHSLOPE -8 D FS FL0286 Y LOWPANDEPTH NONE 95 VP HIGHPANDEPTH 25 -2.0PANHARD 4 0 JUN -9 0.0OTHERPH NONE NA JAN 2 -9 DLEACH 155 -8 NA N FS S PRUNOFF -8 13CORCON 95 -2.0 FREQCORSTEEL NA NA JUN 8 155 FL0123 NA 0.0 NA MAR -8 -9 0 D S -9 -8 1 Y VP 22 MED NONE HIGH HIGH HIGH JUN 155 NA SEP -9 10 0 -8 DRAINED -9 2 S -8 D FS NA LOW HIGH VP Y 25 MED FL0059 MED 0.0 55 NA NA JUN 155 NA NOV -9 HIGH 1.0 LOW 0 -9 -8 LOW HIGH NONE 2 UNDRAINED -8 S NA NA HIGH LOW HIGH MED 6 -9 -9 FS 0 P 2 D 0.5 26 HIGH 95 JUN Y NA SEP NA LOW 155 HIGH NA MED 1.5 NONE -8 -8 C NA 4 -9 -9 HIGH 0 P D 6 LOW 2 NA HIGH 155 NA N LOW NA -8 NA -8 S HIGH -9 MED -9 HIGH 0 HIGH NA 2

E-132 Soil Classification Database Appendix E PARKWOOD LOAMY LOAMY PARKWOOD FINE SAND PAOLA SAND, 0 SAND, 0 PAOLA 5 PCT SLOPES TO ONA FINE SAND OLDSMAR SAND FINE NITTAW NITTAW MUCK NARCOOSSEE NARCOOSSEE SAND FINE LAND COMPLEX S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 50 ENDSHWT FS DURSHWT FL0059 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4MUKIND NA FL0156ANFLOOD FREQ 95 N FSANFLOOD BEG P NAANFLOOD END 2.0 NONE HIGHROCKDEPTH 3.5 LOWROCKDEPTH JUN NA -8 FL0210SLOPE LOW NOV C 155 NA HIGHSLOPE -8 FL0067 LOWPANDEPTH 6 95 MUCK HIGHPANDEPTH CPANHARD 0.0 N 0 -9 FL0124 NONEOTHERPH 15 FS 0.5 SP 2 JUN -9LEACH OCT 95RUNOFF FL0056 0.5 NACORCON 155 JUN -8 NA 1.5CORSTEEL SEP S NA 5 -8 FS FREQ NA D 95 Y 21 VP 0.5 MED NONE JUN HIGH -9 SEP 0 1.5 HIGH HIGH FL0099 4 -9 2 JUN D S 155 SEP P -8 6 N 95 NONE S -8 NA 6.0 NA NA NA 6.0 155 NA NA NONE 4 -8 D MED MED -9 S HIGH -8 0 MED P -9 6 N 2 NA 155 NA LFS NA -9 95 -9 -8 JUN 0.5 A NA 0 -9 SEP 2 LOW HIGH -8 1.5 E OCCAS S N HIGH 3 NA HIGH 154 NA NA HIGH NA LOW HIGH MED -9 -8 -9 0 -8 S 2 HIGH NA MED HIGH 4 NA HIGH D -9 155 P JUL N 13 -9 NOV 0 LOW HIGH HIGH 5 NA LOW NA -8 -8 S -9 HIGH LOW LOW -9 HIGH 0 NA 2 NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL610 610023 - URBAN os MYAKKA 11 23 FL610 610024 os 9 24 610025 FL610 610026 FL610 os 25 610027 5 FL610 610028 os 26 8 FL610 os 27 610029 8 FL610 os 28 10 os 29 8

E-133 Appendix E Soil Classification Database POMPANO POMPANO FINE SAND POMONA FINE SAND POMELLO FINE SAND, FINE POMELLO 5 PCT SLOPES O TO PLACID VARIANT VARIANT PLACID SAND FINE FINE SAND FINE PITS PLACID FINE SAND FINE ADPHLW99999-9-9 9595 NANA 19595959595 NANA LOW-9-9-9-9-9 ENDNANANANANA S SS 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG ENDSHWT FS DURSHWT FL0080 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN DC0028ECOLCOMM NOV VAR FL0287MLRA 6 0.0MUKINDSMSS D 6.0ANFLOOD FREQ FS N NA FL0426ANFLOOD BEG P NA 13ANFLOOD -2.0 NONE HIGHROCKDEPTH 0.0 -9 JUN LOWROCKDEPTH NA MAR -8 LOWSLOPE FS NA 155 HIGHSLOPE -8 NA NA 1.5 NA NA FL0078PANDEPTH 10 HIGHPANDEPTH 3.5 JUN D NOVPANHARD Y NA 0 NONEOTHERPHNANANANANA VP 25 155 -8 2 -9LEACH -8RUNOFF NA 6CORCON 155 NONE FS -8CORSTEEL D NA 2.0 N -8 SP -9 15 FL0007 -9 JUL -9 3.5 NOV NA LOW 155 HIGH LOW FL0032 HIGH 0 -8 NA -9 2 NONE -8 5 NA NA NA C ND ND MW N 4 FS 0 -9 0.5 HIGH HIGH 2 NA 155 SEP JUN HIGH HIGH 1.5 NA -8 -8 FS HIGH NONE MED LOW 0.0 MED OCT JUN 0.5 4 NONE P 0 -9 D 5 N 6 NA 155 NA MED MED LOW HIGH 5 -8 P D -8 Y 26 155 NA -8 -9 0 -8 2 MED NA HIGH HIGH HIGH -9 HIGH HIGH 0 MED HIGH NA 2 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL610 610030 os PINEDA 7 30 FL610 610031 610032 FL610 os 31 11 610033 FL610 os 32 6 610034 os 33 FL610 9 os 610035 34 9 FL610 610036 FL610 os 35 8 os 36 7

E-134 Soil Classification Database Appendix E SMYRNA SMYRNA FINE SAND SATELLITE SATELLITE SAND SAMSULA SAMSULA MUCK RIVIERA FINE SAND, DEPRESSIONAL RIVIERA RIVIERA SAND FINE DEPRESSIONAL MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL610 610037SAND, FINE os POMPANO 6 37 FL610 610038 os 38 610039 7 FL610 os 39 6 610040 FL610 610041 FL610 os 40 610042 5 FL610 os 41 9 os 42 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0285 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKINDSSSSSS DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8 FL0064SLOPE LOW 155 NA 95 HIGHSLOPE -8 FS LOW 0.0PANDEPTH HIGHPANDEPTH FL0275 1.0PANHARD JUN 0 -9 DECOTHERPH 2 -9 95LEACH FS 7 -2.0RUNOFFCORCON 0.0 JUN DCORSTEEL MAR NA Y P NONE 13 NA 10 HIGH NA HIGH NONE 155 -8 MED NA HIGH D FL0092 -8 Y VP 22 NA 155 FL0102 -9 0 NA -8 95 -9 2 MUCK -2.0 -8 JUN FL0091 0.0 APR NA S NA -9 0 -9 95 1.5 2 LOW HIGH NONE 11 HIGH HIGH JUN NOV 3.5 NA D VP NA 25 Y LOW HIGH FS NONE 0.5 HIGH 95 HIGH JUN SEP NA 155 6 NA 1.5 -8 NONE -8 SP C 4 N NA 155 NA 4 -9 0 -9 -8 1 P -8 D 6 N NA 155 NA HIGH LOW UNDRAINED HIGH NA HIGH NA -9 -8 -9 0 -8 2 MED NA HIGH LOW MED NA -9 -9 0 HIGH MED 2 HIGH HIGH NA

E-135 Appendix E Soil Classification Database WAUCHULA WAUCHULA FINE SAND VERO SAND FINE TAVARES FINE SAND, FINE TAVARES PCT SLOPES 5 TO 0 ST. LUCIE FINE SAND, LUCIE ST. 5 PCT SLOPES O TO FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL610 610042 os SMYRNA 8 42 FL610 610043 os 43 10 610044 FL610 os 44 9 610045 FL610 610046 FL610 os 45 8 os 46 8 HTDR-744 DUR4-97 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FSSHWT FL0091 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUN FL0057 95ECOLCOMM SEP FSMLRA 6.0MUKIND D 6.0ANFLOOD FREQ N NAANFLOOD BEG P NA 6ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW FL0021 A S 155 NA HIGHSLOPE -8 N NONE E LOWPANDEPTH 3 95 HIGHPANDEPTH FSPANHARD 3.5 NA 0 -9OTHERPH 155 -8 2 NA 6.0 -9LEACH S JUN -8RUNOFF DECCORCON FL0208CORSTEEL NA -9 0 NA NONE -9 5 A FL0153 N MED MW HIGH 95 4 FS HIGH HIGH NA 0.5 NA 154 NA 1.5 NA JUN -8 SEP LOW HIGH S -8 MED LOW 95 FS 0.5 NONE JUN 1.5 -9 SEP 0 -9 5 D P N NONE 6 NA NA 155 NA NA HIGH LOW -8 HIGH LOW D S -8 P N NA 6 NA -9 -8 0 -9 2 -8 S NA LOW NA HIGH HIGH MED -9 -9 0 2 LOW NA HIGH HIGH NA HIGH

E-136 Soil Classification Database Appendix E WATER ANCLOTE ANCLOTE ANCLOTE CANDLER CANDLER BASINGER BASINGER NO DATA FINE SAND FINE OPC 900000 0 1950100000000 -9-9-9-9-9-9-9-9-9 -9-9-9-9-9-9-9-9-9 LOW-9-9-9-9-9-9-9-9-9-9 HIGH0.0-9-9-9-9-9-9-9-9-9 ENDNANANANANANANANANANA BEGJUNNANANANANANANANANA DUR7 MUIDSTSSAIDMUSYMCNTYABBR HIGH2 LSPOSCODEMAPUNIT NAME FL610 1S5ID 610047 os WINDER COMPPCT 7 47 1SURFTEXT SHWT FL610 610098 LOWSHWT 610099SHWT FL610 ENDSHWT os 715001 LFS 98 12SHWT FL0076 FL715HYDRIC 715002 1.0HYDROGRP os 99DRAINAGE 1 FL715 NAECOLCOMM NA DEC 715003MLRA155NANANANANANANANANA bvMUKIND FL715 DC0038 1 D -9ANFLOOD NA FREQ 715004 0 Y OUTANFLOOD BEG P NA 12ANFLOOD FL715 715005 NONE HIGHROCKDEPTH NA -9 bv LOWROCKDEPTH OUT NA NA 2 -8 LOWSLOPE 0 NA S FL715 715006SLOPE -8 NA NA NA NAPANDEPTH -9 NA NA HIGHPANDEPTH OUT bv NA 715007 FL715PANHARD NA NA NA 0 3 NA NAOTHERPHNANANANANANANANANANA -9 0 -9LEACH NA -9 NA OUT -9 FL715 NARUNOFF NA NA NA NA bvCORCON NA NA -9CORSTEEL M NA 4 -9 -9 0 OUT NA NA -9 NA NA -9 NA NA -9 NA NA bv NA LOW HIGH -9 -9 LOW HIGH OUT -9 NA 5 NA NA 0 NA NA NA NA -9 NA NA NA NA NA -9 bv NA -9 NA NA -9 -9 OUT NA NA 6 NA NA NA NA NA 0 NA NA NA NA NA NA -9 NA -9 -9 bv -9 -9 NA NA NA NA NA NA NA NA NA NA NA NA NA 7 NA -9 0 -9 -9 -9 NA NA -9 NA NA NA NA NA NA NA NA NA NA NA -9 -9 -9 NA NA -9 NA -9 NA NA NA NA NA NA NA NA NA NA NA -9 -9 NA -9 NA NA -9 NA NA NA NA -9 -9 NA NA -9 NA -9 NA NA NA NA -9 NA -9 NA NA NA NA

E-137 Appendix E Soil Classification Database SOCD00 0 0000 00 10 0 1NANANANANANANANANA 0 0000 00 LOW-9-9-9-9-9-9-9-9-9 LOW-9-9-9-9-9-9-9-9-9 ENDNANANANANANANANANA ENDNANANANANANANANANA MUIDSTSSAIDMUSYMCNTYABBR LOW-9-9-9-9-9-9-9-9-9 LSPOSCODE0 NAMEMAPUNIT 1S5ID COMPPCT FL715 715008SURFTEXT bv BRADENTON 8 HIGHSHWT CANAVERALSHWT BEGSHWT CANAVERAL FL715 715009SHWT CANOVA DURSHWT OUT -9 CHOBEEHYDRICNANANANANANANANANA bvHYDROGRPNANANANANANANANANA 9 CHOBEE 715010DRAINAGENANANANANANANANANA FL715 NA BEACHESECOLCOMM COCOAMLRA -9 OUTMUKIND WABASSO 715011ANFLOOD FREQ -9 bv FL715ANFLOOD BEG NA 10 715012ANFLOOD NA NA HIGHROCKDEPTH FL715 OUT 715013 LOWROCKDEPTH NA -9 -9SLOPE NA NA FL715 715014 HIGHSLOPE -9 bv -9PANDEPTH NA 11 NA HIGHPANDEPTH FL715 715015 OUT NAPANHARDOTHERPHNANANANANANANANANA 715016 NA bv -9 -9 -9LEACHNANANANANANANANANA -9 FL715 NA NA 12 OUTRUNOFF -9 -9CORCONNANANANANANANANANA FL715 NA NACORSTEEL NA NA bv OUT 13 NA -9 -9 -9 -9 NA NA NA -9 NA OUT -9 bv NA NA 14 NA NA -9 -9 NA NA OUT NA NA NA -9 -9 bv -9 NA NA 15 OUT -9 NA NA -9 -9 NA NA NA NA NA bv -9 NA 16 -9 -9 -9 NA NA -9 NA -9 NA NA NA NA NA NA -9 NA -9 NA -9 -9 -9 NA NA -9 NA NA NA NA -9 NA -9 -9 NA -9 -9 NA NA NA NA NA NA NA NA -9 NA -9 NA -9 -9 NA NA NA -9 -9 -9 -9 NA NA NA -9 -9 NA NA NA NA NA

E-138 Soil Classification Database Appendix E HOLOPAW LAND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL715 715017 bv EAUGALLIE 0 17 RIVIERA WINDER FL715 715019 RIVIERA 715020 FL715 FLORIDANA bv 19 0 715021 FLORIDANA FL715 RIVIERA 715022 bv URBAN 20 FL715 0 715023 bv 21 FL715 0 715018 bv 22 715025 FL715 715026 0 FL715 FL715 bv 23 0 bv 18 0 bv 25 11 bv 26 0 COMPPCT 10 0000 1NANANANANANANANANA 0 000 LOW-9-9-9-9-9-9-9-9-9 LOW-9-9-9-9-9-9-9-9-9 ENDNANANANANANANANANA ENDNANANANANANANANANA LOW-9-9-9-9-9-9-9-9-9 1S5ID COMPPCT SURFTEXT HIGHSHWT SHWT BEGSHWT SHWT DURSHWT OUT -9HYDRICNANANANANANANANANA HYDROGRPNANANANANANANANANA DRAINAGENANANANANANANANANA NAECOLCOMM OUTMLRA -9MUKIND -9ANFLOOD FREQ OUTANFLOOD BEG NA NAANFLOOD NA HIGHROCKDEPTH -9 -9 OUT LOWROCKDEPTH NA -9 NASLOPE NA NA HIGHSLOPE -9 OUT NAPANDEPTH -9 -9 HIGHPANDEPTH NA NAPANHARD NAOTHERPHNANANANANANANANANA -9 -9 NA -9 NA NALEACHNANANANANANANANANA OUT -9 NA -9 -9RUNOFF NACORCONNANANANANANANANANA NACORSTEEL NA NA NA NA -9 NA -9 -9 -9 -9 OUT NA -9 NA NA NA NA NA -9 NA NA OUT NA -9 -9 -9 NA NA NA -9 OUT -9 NA NA -9 NA NA -9 NA -9 NA -9 NA NA NA NA NA NA -9 -9 NA -9 -9 NA -9 NA -9 NA NA NA -9 NA NA -9 NA NA NA NA -9 -9 NA -9 NA NA -9 NA -9 NA NA NA NA NA -9 NA NA -9 NA -9 -9 NA NA -9 -9 -9 -9 NA NA NA -9 -9 NA NA NA NA NA

E-139 Appendix E Soil Classification Database COMPPCT 100 0 000 000 LOW-9-9-9-9-9-9-9-9-9 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT 1S5ID COMPPCT FL715 715027 1SURFTEXT bv HOLOPAW 0 27 HIGHSHWT IMMOKALEESHWT FL715 715028 MALABAR BEGSHWT ENDSHWT MALABAR NA DURSHWT bv OUT 28 HOLOPAW -9 0HYDRIC 715029 FL715HYDROGRP MICCODRAINAGENANANANANANANANANA NA MICCO 715030ECOLCOMM NA NA OUT EVERGLADES FL715MLRA -9 bv -9MUKIND EVERGLADES 29 715031 NAANFLOOD FREQ 0 NA NA FL715ANFLOOD BEG NA NAANFLOOD END OUT 715032 NA NA HIGHROCKDEPTH -9 bv 715033 30 LOWROCKDEPTH FL715 NA NA -9 -9SLOPE LOW 715034 NA 0 NA NA NA OUT FL715 HIGHSLOPE -9 NA NA LOWPANDEPTH NA NA NA FL715 HIGHPANDEPTH bv 31PANHARD NA -9 -9 715035 OUT -9 -9 -9OTHERPH NA NA NA NA -9 0 -9 NA NALEACHNANANANANANANANANA -9 NA NA NARUNOFF FL715 CORCON NA bv 32 OUTCORSTEEL -9 NA NA -9 NA -9 -9 NA NA NA -9 NA -9 NA NA 0 -9 OUT NA NA NA bv 33 -9 NA NA OUT NA NA -9 NA NA NA NA NA 0 -9 bv NA 34 NA NA NA NA NA -9 -9 -9 NA -9 -9 NA -9 NA NA NA -9 0 NA NA NA NA NA -9 OUT NA NA NA NA NA NA -9 -9 -9 NA NA -9 -9 NA bv NA -9 35 NA -9 NA -9 NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0 -9 -9 -9 -9 NA -9 -9 NA -9 NA NA NA NA NA NA NA -9 NA NA NA NA -9 NA NA NA NA -9 -9 -9 NA -9 -9 NA NA -9 -9 NA NA NA NA -9 NA -9 -9 NA -9 -9 NA NA NA NA NA NA NA -9 -9 NA NA -9 -9 NA -9 NA NA NA -9 NA NA NA NA -9 -9 -9 -9 NA NA NA NA NA

E-140 Soil Classification Database Appendix E HILOLO LAND PAOLA PAOLA URBAN BEACH OLDSMAR ORSINO PALM LAND COMPPCT 10 0 0 0 0 0 0000 0 LOW-9-9-9-9-9-9-9-9-9-9-9 1S5ID COMPPCT 1SURFTEXT HIGHSHWT SHWT BEGSHWT ENDSHWT NA DURSHWT OUT -9HYDRICHYDROGRPDRAINAGENANANANANANANANANANANA NA NA OUTECOLCOMM NA -9MLRA -9MUKIND OUT NA NA NAANFLOOD FREQ NA NAANFLOOD BEG NAANFLOOD END -9 -9 OUT NA HIGHROCKDEPTH NA NA NA LOWROCKDEPTH NA NA NA -9SLOPE LOW OUT NA NA NA NA HIGHSLOPE -9 -9 -9 NA LOWPANDEPTH NA NA NA HIGH NAPANDEPTH NA NAPANHARD -9 NA NA OUT NA NA -9 -9OTHERPH -9 -9 NA -9 -9 -9 NA NALEACHNANANANANANANANANANANA NA NA NA NARUNOFF OUT NA NA NA NACORCON -9 -9 -9CORSTEEL NA -9 NA NA OUT -9 -9 -9 NA NA -9 NA NA NA NA NA NA NA NA OUT -9 NA -9 -9 NA NA NA -9 -9 -9 NA NA NA NA NA OUT -9 NA -9 NA NA NA NA NA NA NA -9 NA NA OUT NA NA -9 -9 -9 NA NA -9 NA NA NA -9 -9 NA -9 NA NA NA NA NA NA NA NA NA NA NA NA -9 -9 -9 -9 NA NA NA NA -9 -9 -9 NA -9 NA NA NA NA NA NA NA NA NA NA NA NA -9 NA NA -9 NA NA -9 NA -9 -9 NA NA NA NA -9 NA NA -9 -9 NA NA NA NA -9 NA NA NA NA -9 -9 NA NA NA NA NA NA -9 -9 -9 NA -9 -9 NA NA -9 NA NA NA NA NA -9 NA NA NA NA -9 -9 -9 -9 -9 NA NA NA -9 NA NA NA NA NA NA -9 -9 -9 -9 -9 NA NA NA -9 NA NA -9 -9 -9 -9 NA -9 NA NA NA NA -9 -9 NA NA -9 -9 NA NA NA NA NA NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL715 715036 bv MYAKKA 0 36 ARENTS FL715 715037 MYAKKA 715038 FL715 URBAN bv 37 0 715039 FL715 715040 bv FL715 38 0 715041 FL715 715042 bv 39 715043 11 FL715 715044 715045 FL715 bv 40 715046 FL715 0 FL715 bv 41 FL715 0 bv 42 0 bv 43 0 bv 44 bv 45 0 bv 46 11 0

E-141 Appendix E Soil Classification Database ST. ST. LUCIE ST. ST. JOHNS JOHNS COMPPCT 1000000 0 000 LOW-9-9-9-9-9-9-9-9-9-9 1S5ID COMPPCT 1SURFTEXT HIGHSHWT SHWT BEGSHWT ENDSHWT NA DURSHWT OUT -9HYDRICHYDROGRP NA OUTDRAINAGENANANANANANANANANANA NAECOLCOMM NA -9MLRA -9 OUTMUKIND NA NA NAANFLOOD FREQ NA NAANFLOOD BEG NA -9 -9ANFLOOD END OUT NA HIGHROCKDEPTH NA NA NA NA LOWROCKDEPTH NA NA -9 NASLOPE LOW NA NA NA -9 HIGHSLOPE -9 NA OUT -9 NA LOWPANDEPTH NA NA NA HIGHPANDEPTH NA NA -9 NA NA NA NAPANHARD -9 -9 -9 NAOTHERPH -9 -9 OUT -9LEACHNANANANANANANANANANA NA NA -9 NARUNOFF NA NA NA NA -9CORCON NA NA NA -9 -9 -9CORSTEEL -9 NA -9 NA NA NA -9 NA NA -9 NA OUT NA NA NA -9 -9 NA -9 NA NA NA -9 -9 NA -9 NA NA NA NA NA NA -9 OUT NA NA NA NA NA NA NA NA NA -9 NA -9 -9 -9 -9 NA OUT NA -9 -9 NA NA NA NA NA OUT NA NA NA NA NA NA NA -9 -9 -9 NA NA -9 -9 -9 NA -9 NA -9 NA NA NA NA NA NA NA NA NA NA NA -9 NA -9 -9 NA NA NA NA -9 -9 -9 NA NA NA NA -9 NA NA NA NA NA NA NA -9 -9 NA -9 NA NA NA NA NA NA NA NA NA NA -9 NA -9 NA -9 -9 -9 -9 NA NA NA NA -9 NA NA NA -9 NA NA NA -9 -9 -9 NA -9 -9 NA NA NA -9 NA -9 -9 -9 -9 -9 NA NA NA NA NA -9 -9 -9 NA -9 NA NA NA NA NA NA NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL715 715047 bv PINEDA 0 47 FL715 715048 DELRAY POMELLO 715049 FL715 bv POMELLO 48 0 POMPANO 715050 FL715 QUARTZIPSAM bv 49 SATELLITE 715051 0 FL715 ST. 715052 bv 50 FL715 0 715053 bv 51 FL715 0 715054 715055 bv 715056 FL715 52 FL715 0 FL715 bv 53 0 bv 54 bv 55 0 bv 56 0 0

E-142 Soil Classification Database Appendix E UNKNOWN CODE CEIA TURNBULL UDORTHENTS ARENTS SWAMP SAMSULA TAVARES TERRA LUCIE S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 0 ENDSHWT NA DURSHWT OUT -9HYDRIC -9HYDROGRP NA 0 OUTDRAINAGE NAECOLCOMM NA -9MLRA -9 -9MUKIND NA NA OUTANFLOOD FREQ NA NA NAANFLOOD BEG 0 NA -9 NAANFLOOD END -9 NA NA HIGHROCKDEPTH NA -9 LOWROCKDEPTH NA NA NA NA -9SLOPE LOW NA NA NA NA OUT NA HIGHSLOPE -9 -9 NA LOWPANDEPTH NA NA HIGHPANDEPTH -9 NA NA NA 0 NA OUTPANHARD NA -9 NA -9 -9 -9OTHERPH -9 -9 NA NA NA -9LEACH OUT NARUNOFF NA 0CORCON -9 -9 NA NA NA -9 -9 -9 -9 -9CORSTEEL NA NA NA NA -9 -9 NA NA OUT NA NA NA 0 NA NA -9 NA NA NA -9 NA NA -9 NA -9 NA NA -9 NA NA OUT NA -9 -9 NA NA NA NA NA -9 NA NA NA NA OUT -9 -9 NA NA NA NA 0 NA -9 NA NA NA NA NA NA NA NA NA -9 NA -9 -9 -9 NA NA NA -9 NA NA -9 -9 NA NA -9 NA NA NA NA NA -9 0 NA NA NA -9 -9 NA NA -9 NA -9 -9 NA NA -9 NA -9 NA NA -9 0 NA NA NA -9 NA NA -9 NA NA NA NA NA NA -9 -9 NA -9 NA NA -9 -9 -9 NA NA -9 NA NA NA NA NA NA NA NA NA NA NA NA -9 -9 -9 NA NA NA -9 -9 -9 NA NA NA NA NA NA -9 -9 -9 -9 -9 NA -9 NA NA NA NA NA -9 -9 -9 -9 NA NA NA NA NA NA NA NA NA NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL715 715057 bv ST. 0 57 FL715 715058 bv 58 715059 0 FL715 bv 715060 59 FL715 0 715061 FL715 715062 FL715 715063 bv 60 0 FL715 715064 715065 bv 61 FL715 0 FL715 bv 62 0 bv 63 0 bv 64 0 bv 65 12

E-143 Appendix E Soil Classification Database COMPPCT 10000 0 0 000 LOW-9-9-9-9-9-9-9-9-9 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT 1S5ID COMPPCT FL715 715066 1SURFTEXT bv BESSIE 0 66 HIGHSHWT FL715 715067 TOMOKASHWT TOMOKA BEGSHWT 715068 bv FL715 ENDSHWT URBAN LAND 67 0 NA DURSHWT OUT 715069 VALKARIA -9HYDRIC FL715 WABASSOHYDROGRP NA OUT bvDRAINAGENANANANANANANANANA NA 68 WELAKAECOLCOMM 0 NA -9 WINDER 715070MLRA -9 SYMRNA MUKIND FL715 OUT NA NA NAANFLOOD FREQ bv NA NA 69 715071ANFLOOD BEG NA -9 11 -9ANFLOOD END FL715 OUT NA HIGHROCKDEPTH NA NA 715072 NA NA LOWROCKDEPTH NA NA -9 NASLOPE LOW NA NA NA 715073 FL715 HIGHSLOPE -9 NA -9 -9 bv 70 LOWPANDEPTH NA NA 715074 NA NA HIGH OUTPANDEPTH 0 FL715 NA -9 NA NA NA NAPANHARD -9 NA -9 -9OTHERPH NA -9 -9 FL715 -9LEACHNANANANANANANANANA NA bv 71 NA NA OUTRUNOFF NA NA NA -9 NA -9CORCON -9 0 NA -9CORSTEEL NA -9 -9 NA -9 NA NA NA NA OUT bv 72 NA NA NA NA -9 -9 -9 NA NA -9 -9 NA NA -9 -9 -9 NA 0 NA NA NA OUT NA NA NA bv 73 NA NA NA NA OUT -9 NA -9 NA NA -9 NA NA NA NA NA NA -9 -9 -9 0 NA NA -9 bv 74 NA -9 NA NA NA NA NA NA NA NA NA NA NA -9 NA NA -9 NA 0 NA -9 -9 -9 NA NA -9 -9 NA -9 NA NA NA NA NA NA -9 -9 NA NA NA NA NA NA NA -9 NA -9 -9 NA -9 -9 NA -9 NA -9 NA NA NA NA NA NA NA NA NA -9 NA -9 -9 NA NA NA -9 -9 -9 NA NA NA NA NA -9 -9 -9 -9 -9 -9 NA NA NA NA NA -9 -9 -9 -9 NA NA NA NA NA NA NA NA

E-144 Soil Classification Database Appendix E OPC 000000 0 100000 LOW-9-9-9-9-9-9-9-9-9 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME 1S5ID COMPPCT FL715 715076 1SURFTEXT bv BLUFF 0 76 FL715 715077 HIGHSHWT GATORSHWT 715078 FL715 SCOGGIN BEGSHWT bv 77 ENDSHWT 0 PAISLEY NA 715079 DURSHWT OUT POMPANO FL715 -9HYDRIC POMONA bv 715080HYDROGRP 78 NA OUTDRAINAGENANANANANANANANANA 0 POMONA NA FL715ECOLCOMM NA -9 JOHNS ST. 715081MLRA -9 OUT NA POMONA MUKIND NA bv FL715 NA 79ANFLOOD FREQ 715082 NA NA -9ANFLOOD BEG 0 -9 NA OUTANFLOOD END FL715 NA 715083 NA NA NA HIGHROCKDEPTH NA NA bv 80 LOWROCKDEPTH NA NA -9 OUTSLOPE LOW FL715 -9 NA NA NA 715085 0 -9 NA NA HIGHSLOPE -9 NA NA NA LOWPANDEPTH NA NA NA HIGHPANDEPTH -9 NA NA NA bv FL715 81 OUTPANHARD NA -9 -9 -9 -9 -9OTHERPH NA -9 NA -9 NALEACHNANANANANANANANANA NA 0 NA NA NA NA NA -9RUNOFF NA OUT bvCORCON -9 82 -9 -9 NA -9 -9CORSTEEL NA -9 NA NA NA -9 NA NA NA OUT 0 NA NA NA NA NA -9 -9 -9 NA bv 83 -9 NA -9 -9 NA NA NA NA NA NA NA -9 NA -9 NA NA NA NA OUT NA NA 0 NA -9 NA -9 -9 NA NA NA NA -9 -9 bv -9 85 NA NA NA NA -9 -9 NA NA NA NA NA NA NA NA NA NA -9 -9 NA -9 NA 0 -9 -9 NA -9 NA NA NA -9 NA NA NA NA NA NA NA -9 NA NA NA NA -9 -9 -9 NA -9 NA -9 -9 NA NA NA NA NA NA NA NA -9 NA NA NA -9 -9 -9 -9 -9 -9 NA NA NA NA NA NA NA NA NA -9 -9 -9 -9 -9 NA -9 NA NA NA NA -9 NA -9 -9 NA -9 NA NA NA NA NA NA

E-145 Appendix E Soil Classification Database ANCLOTE DATA NO WATER URBAN LAND COMPLEX ARENTS - CEIA S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 0 ENDSHWT NA DURSHWT OUT -9HYDRIC -9HYDROGRPDRAINAGE NA NA 0ECOLCOMM OUT NAMLRA -9 -9MUKIND NA -9ANFLOOD FREQ NA NAANFLOOD BEG NA NA NAANFLOOD END OUT NA NA HIGHROCKDEPTH -9 0 LOWROCKDEPTH NA NA -9 NASLOPE LOW -9 NA NA NA NA OUT HIGHSLOPE -9 NA -9 NA LOWPANDEPTH NA NA NA HIGHPANDEPTH 0 NAPANHARD OUT -9 -9 -9 -9 -9 NA NA NAOTHERPH NA -9 -9 NA NA -9 NA -9LEACH NA NARUNOFF NA OUTCORCON 0 NACORSTEEL -9 -9 NA NA -9 NA -9 NA NA -9 NA -9 -9 NA NA NA NA NA NA -9 OUT NA -9 NA NA NA NA 0 -9 FL0097 -9 NA NA NA NA NA NA NA NA NA NA NA -9 NA NA NA -9 -9 -9 NA -9 -9 -9 NA S NA NA NA NA 0 -9 NA -9 NA NA NA NA NA NA NA NA -9 NA -9 -9 NA -9 NA -9 JUN -9 -9 NA 1.5 60 NA NOV NA -9 NA NA 3.0 NA NA NA NA NA NA NA NA NA -9 -9 NA -9 NA N -9 -9 -9 NA 6 SP NA NA NA NA NA NA NA NONE NA NA NA -9 NA -9 -9 -9 C -9 -9 155 NA NA NA NA NA NA -8 NA -9 -8 -9 -9 -9 NA NA NA NA NA NA 0 -9 5 -9 NA NA NA NA NA NA HIGH LOW MED HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL715 715086 bv DAYTONA 0 86 TUSCAWILLA FL715 715087 ELECTRA TERRA bv 87 0 715088 FL715 715090 FL715 715091 bv -8 0 FL715 715098 FL715 bv 715099 90 0 716002 FL715 bv FL716 91 0 bv 98 12 bv 99 1 br 2 11

E-146 Soil Classification Database Appendix E DANIA MUCK LAND COMPLEX BEACHES - URBAN CANAVERAL BOCA SAND FINE BASINGER SAND FINE LAND COMPLEX MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL716 716003 - URBAN ORGANIC br SUBSTR. ARENTS, 11 3 FL716 716004 br 7 716005 4 FL716 716006 FL716 br 8 716007 5 FL716 br 2 6 716008 br 11 FL716 7 br 4 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 60 ENDSHWT CB-S DURSHWT FL0083 2.0HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND NAANFLOOD FREQ NANFLOOD BEG SP NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C 155 NA HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH FL0063 FS 95PANHARD 0 -9OTHERPH 2 0.0 -9LEACH FL0054 1.0RUNOFF JUNCORCON FEB FSCORSTEEL 95 DC0002 NA NA 0.5 9 D 1.5 FL0060 JUN FEB Y MED P LOW NONE 26 S HIGH HIGH 95 0.0 NA 9 JAN 6.0 156A NONE -8 D NA DEC S -8 N S 8 P 60 1.5 JUN FREQ FL0055 NOV 3.0 156A NA -9 12 0 NA 40 -9 D 2 S 24 NONE Y P NA 155 JAN NA 6 DEC NA -9 -8 NA 0 -9 2 NA HIGH -8 M HIGH N SP 155 MED HIGH 95 MUCK NA JUN -2.0 NA APR NA 0.0 NA -8 -9 MED HIGH NONE 1 -9 -8 HIGH MED C 5 NA HIGH HIGH NA -9 HIGH HIGH 11 -9 D 0 5 24 156A VP MED HIGH Y NA NA MED LOW NA NA 20 8 S -9 -9 0 LOW HIGH 2 HIGH NA MED UNDRAINED

E-147 Appendix E Soil Classification Database HALLANDALE - URBAN LAND COMPLEX HALLANDALE SAND FINE DADE - URBAN COMPLEX LAND DUETTE - URBAN DUETTE LAND COMPLEX FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL716 716009 br DADE 9 9 FL716 716010 br 11 10 716011 FL716 br 11 11 716012 FL716 716013 FL716 br 8 12 br 13 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0351 5.0HYDRIC 6.0HYDROGRPDRAINAGE JUN FL0323 50ECOLCOMM SEP SMLRA 4 4.0MUKIND A 6.0ANFLOOD FREQ N JUNANFLOOD BEG W OCT 9ANFLOOD END FL0351 NONE HIGHROCKDEPTH 5 LOWROCKDEPTH NA 40SLOPE LOW NA S 50 155 NA HIGHSLOPE 20 N FS NONE MW LOW 5.0PANDEPTH NA HIGHPANDEPTH 6.0 FL0065 JUNPANHARD SEP NA 0 -9OTHERPH -8 155 2 NA -9LEACH C -8RUNOFF 4 FL0065 CORCON 95 NONE NA FSCORSTEEL 0.5 W NA N -9 JUN 0 NA 1.5 NA -9 SEP 2 NA HIGH LOW 155 NA 40 MED LOW NONE NA 50 C 20 FS NA 0.5 4 D JUN SEP MED 1.5 P LOW N 8 HIGH LOW -9 0 NONE -9 NA 2 156A NA 20 7 NA S NA 4 NA P HIGH LOW N NA MED LOW 156A NA -9 NA 0 -9 20 2 7 C NA MED NA HIGH LOW HIGH -9 -9 0 2 MED NA HIGH NA LOW HIGH

E-148 Soil Classification Database Appendix E IMMOKALEE - URBAN IMMOKALEE LAND COMPLEX IMMOKALEE, LIMESTONE LIMESTONE IMMOKALEE, - URBAN LAND COMPLEX SUBSTR. IMMOKALEE IMMOKALEE SAND FINE LIMESTONE SUBSTR. LIMESTONE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL716 716014SAND, FINE GRAVELLY br MATLASHA 11 14 FL716 716015 br 8 15 716016 FL716 br 16 11 716017 FL716 17 br 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT GR-FS DURSHWT FL0387 2.0HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKIND NAANFLOOD FREQ NANFLOOD BEG SP NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA 60SLOPE LOW S 156A NA HIGHSLOPE 40 LOWPANDEPTH HIGHPANDEPTH FSPANHARD FL0058 95 0 -9OTHERPH 2 -9LEACH 0.5RUNOFF 1.5CORCON FL0380 JUNCORSTEEL SEP FS NA NA 50 4 D 0.5 MED HIGH 1.5 JUN N LOW P HIGH NONE 6 SEP NA 155 -8 4 NA NONE S NA -8 N P 6 FL0058 155 -9 NA 0 -9 2 NA 80 C 40 FS NA 50 NA 0.5 -9 JUN 0 MED HIGH 1.5 -9 SEP 2 HIGH HIGH NA NONE NA HIGH MED 4 NA HIGH MED N P 6 155 NA NA -8 -8 C -9 0 -9 2 NA HIGH NA MED HIGH HIGH

E-149 Appendix E Soil Classification Database PENNSUCO SILTY PENNSUCO SILTY LOAM, DRAINED CLAY PALM BEACH PALM SAND PAOLA - URBAN PAOLA COMPLEX LAND PAOLA SAND FINE OKEELANTA OKEELANTA MUCK MARGATE MARGATE SAND FINE MUCK S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT MUCK DURSHWT FL0069 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM FS APR FL0094MLRA 95 11MUKIND -1.0 DANFLOOD FREQ Y FL0071ANFLOOD BEG 1.0 VP 24 JUNANFLOOD END MUCK FEB NONE HIGHROCKDEPTH 90 LOWROCKDEPTH -1.0 9 NA FL0056 40SLOPE LOW S 155 NA HIGHSLOPE 0.0 20 JUN D FS LOWPANDEPTH JAN Y P NONE FL0056 HIGH 16PANDEPTH PANHARD 95 0 -9 6.0OTHERPH 8 1 NA -9LEACH 40 156A NONE NA NA FS 6.0 DRUNOFF S 20 NA Y VPCORCON 22 FL0066CORSTEEL NA 50 6.0 156A NA UNDRAINED NONE -9 -8 0 NA NA -9 6.0 -9 2 NA NA -8 S LOW HIGH FL0352 A E MED HIGH N 3 NONE S 155 NA NA -9 -9 0 6.0 NA 95 -9 UNDRAINED -8 2 HIGH HIGH -8 NA NA HIGH S MED NA 6.0 E N 155 NA NA NA NONE NA SICL LOW HIGH NA -9 -8 HIGH MED 0 -9 0.0 NA 95 -8 8 C -9 JUN NONE 1.0 NA A NOV LOW HIGH 155 2 W LOW N -9 HIGH NA -9 0 NA 8 -8 HIGH LOW NA NA LOW 6 -8 HIGH S 155 D P 18 Y NA -9 NA -9 HIGH 0 LOW 72 DRAINED 8 LOW NA LOW 40 S MED -9 HIGH -9 HIGH LOW 0 NA 1 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL716 716018 br LAUDERHILL 4 18 FL716 716019 br 19 716021 7 FL716 716022 br FL716 21 5 716023 FL716 22 br 10 716024 FL716 23 br 11 716025 FL716 24 br 10 25 br 3

E-150 Soil Classification Database Appendix E PALM BEACH - URBAN PALM LAND COMPLEX PERRINE SILTY CLAY CLAY PERRINE SILTY DRAINED LOAM, POMPANO POMPANO SAND FINE POMELLO POMELLO SAND FINE PLANTATION PLANTATION MUCK LAND COMPLEX COMPPCT 1609095959550 S SSS C 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG ENDSHWT GR-FS DURSHWT FL0387 2.0HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKINDC NAANFLOOD FREQ N MUCKANFLOOD BEG FL0095 SP NAANFLOOD END NONE HIGHROCKDEPTH -2.0 LOWROCKDEPTH NA 0.0 60SLOPE LOW FS JUN FL0078 156A NA HIGHSLOPE 40 APR LOWPANDEPTH HIGHPANDEPTH 11 FL0032PANHARD 2.0 D 0 -9OTHERPH 2 FS -9 Y 3.5LEACH VP JUL NONE 24 FL0373 NOVRUNOFFCORCONCORSTEEL NA 156A 0.0 NA 40 5 NA NA SICL JUN 1.0 20 NONE OCT C MW N 4 HIGH HIGH LOW HIGH 0.0 155 NONE -9 0 FL0066 JUN NA NOV 5 -9 0.5 1 -8 NA D P -8 Y NONE 26 NA 156A S DRAINED NA NA 6 -9 -8 LOW HIGH 0 -9 D P 5 HIGH -8 MED 155 NA 24 Y 6.0 NA NA NA NA 6.0 NA -9 MED 40 MED NONE 0 -9 LOW HIGH 20 2 NA NA HIGH HIGH HIGH MED -9 -9 -9 NA W 155 0 DRAINED NA 1 N LOW HIGH NA NA HIGH LOW NA -8 -8 NA -9 -9 0 LOW HIGH 8 LOW NA LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL716 716020 - URBAN br MATLACHA 11 20 FL716 716027 br 5 27 716028 FL716 716029 FL716 br 28 9 716030 FL716 29 br 7 716031 30 br FL716 3 31 br 11

E-151 Appendix E Soil Classification Database URBAN LAND COMPLEX LAND URBAN UDORTHENTS - SUBSTR. MARLY UDORTHENTS, TERRA CEIA TERRA CEIA MUCK, TIDAL ST. LUCIE LUCIE ST. SAND FINE SANIBEL SANIBEL MUCK SILT LOAM SILT MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL716 716032 br PERRINE VARIANT 2 32 FL716 716033 716034 br FL716 33 5 716035 FL716 br 34 10 716036 FL716 35 br 2 716037 FL716 36 br 11 37 br 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT SIL DURSHWT FL0371 0.0HYDRIC 0.5HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKIND DANFLOOD FREQ FL0073 Y 90ANFLOOD BEG VP MUCK 19ANFLOOD END FL0057 -1.0 FREQ HIGHROCKDEPTH 0.0 LOWROCKDEPTH FS JAN JUN 40SLOPE LOW 95 S 155 APR DEC FL0374 HIGHSLOPE 20 6.0 LOWPANDEPTH 11 HIGHPANDEPTH 6.0 NA NAPANHARD MUCK D 0 -9 FL0089OTHERPH Y VP 1 95 NONE -9 24LEACH 0.0RUNOFF -9 NA 0.5CORCON JAN NONE CB-S NA DEC -8 ACORSTEEL 156A E NA FL0377 N S -8 3 UNDRAINED 95 FREQ NA 155 12 6.0 NA LOW HIGH -8 NA 6.0 LOW HIGH -9 NA GR-S 0 D S -8 -9 VP 1 DRAINED Y 19 NONE NA JAN 155 DEC NA 50 -9 -9 -8 0 2.0 -9 2 -8 JAN S 4.0 DEC W LOW HIGH NA TIDAL NONE N HIGH LOW NA NA NA 156A NA -9 LOW HIGH 0 -9 LOW -8 MED 1 12 NA -8 M NA NA SP LOW 155 HIGH NA NA N HIGH HIGH NA -9 -9 2 40 80 NA MED NA HIGH 40 C LOW LOW -9 -9 0 MED 2 LOW MED NA LOW

E-152 Soil Classification Database Appendix E FINE SAND WATER AND MYAKKA LAWNWOOD NO DATA URBAN LAND UDORTHENTS - UDORTHENTS URBAN LAND COMPLEX SHAPED S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT CB-S DURSHWT FL0376 2.0HYDRIC 4.0HYDROGRPDRAINAGE JANECOLCOMM DECMLRA 12 FL0376 CB-SMUKIND 50 NAANFLOOD FREQ N 2.0ANFLOOD BEG SP NAANFLOOD END 4.0 JAN NONE HIGHROCKDEPTH DEC LOWROCKDEPTH NA 72 LOWSLOPE M 12 156A NA HIGHSLOPE 40 NA LOWPANDEPTH DC0035 HIGHPANDEPTH N SP NONE NA VARPANHARD NA 0 -9OTHERPH 95 5 -9LEACH NA 155 NA 2.0RUNOFF DC0038 80 NA CCORCON 2.0 FL0221 40 NACORSTEEL NA 0 NA NA -9 NA -9 -9 NA -9 0 NA 100 HIGH FS NA -9 LOW 2 NONE -9 MED HIGH NA NA NA N -9 NA NA -9 60 NA NA 0.5 155 NA NA NA JUN NA NA -8 NA OCT 1.5 NA HIGH -9 NA LOW M -8 HIGH MED NA NA NA NA NONE NA NA -9 D 5 -9 NA NA -9 NA P 0 6 -9 NA 2 N -9 M 155 -9 NA -9 NA NA -9 -9 NA HIGH -9 -8 HIGH ND U ND -8 NA -9 NA -9 -9 NA NA -9 NA NA NA NA 20 NA NA 0 30 2 NA NA THIN LOW NA HIGH HIGH HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL716 716038 br UDORTHENTS, 11 38 FL716 716039 br 11 39 716040 FL716 716098 FL716 716099 FL716 753002 11 br 40 FL753 12 98 br 1 99 br 2 8 ma

E-153 Appendix E Soil Classification Database PAOLA AND ST. LUCIE SAND, LUCIE AND ST. PAOLA 8 PCT 0 TO SLOPES WAVELAND AND LAWNWOOD AND LAWNWOOD WAVELAND SAND, DEPRESSIONAL FINE FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL753 753004 AND IMMOKALEE ma WAVELAND 8 4 FL753 753005 ma 6 5 753006 FL753 ma 10 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 60 ENDSHWT FS DURSHWT FL0133 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEPMLRA 4MUKIND DANFLOOD FREQ NANFLOOD BEG P 6ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW U FL0266 155 NA HIGHSLOPE -8 55 FS LOWPANDEPTH HIGH -2.0PANDEPTH PANHARD 0.0 0 JUN -9OTHERPH 2 -9 FEBLEACHRUNOFF 9CORCONCORSTEEL D NA Y NA NONE VP 25 FL0056 LOW HIGH NA HIGH HIGH 155 -8 NA U 60 -8 S 6.0 6.0 NA 20 NA 0 30 2 -9 NONE THIN A NA N E 3 LOW HIGH HIGH HIGH NA 155 NA -8 U -8 -9 0 -9 8 NA NA LOW HIGH HIGH LOW

E-154 Soil Classification Database Appendix E ARCHBOLD SAND PLACID AND BASINGER FINE PLACID SAND, DEPRESSIONAL POMELLO SAND, 0 SAND, 0 POMELLO 5 PCT SLOPES TO 0 TO 8 PCT SLOPES 8 TO 0 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 70 ENDSHWT S DURSHWT FL0066 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND AANFLOOD FREQ NANFLOOD BEG W 2ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C 155 NA HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH FL0078 90PANHARD 0 -9 SOTHERPH 8 -9 2.0LEACH 3.5RUNOFF JULCORCON NOVCORSTEEL NA FL0287 5 NA C 60 N HIGH LOW NONE MW LOW LOW 6 FS -2.0 0.0 NA JUN 155 -8 MAR NA S -8 10 NONE D VP -9 0 FL0434 Y -9 5 25 NA 155 NA NA -8 90 U NA -8 3.5 S MED MED 6.0 JUN HIGH LOW NOV -9 0 -9 2 NONE 6 NA MW A NA N HIGH HIGH HIGH 6 HIGH NA 155 NA -8 S -8 -9 0 -9 2 NA HIGH NA LOW MED LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL753 753008 BEACH-BEACHES COMPLEX, ma PALM 10 8 FL753 753009 ma 9 9 753013 FL753 ma 6 13 753014 FL753 ma 9 14

E-155 Appendix E Soil Classification Database URBAN LAND OKEELANTA OKEELANTA MUCK FINE SAND FINE WINDER SAND, DEPRESSIONAL WINDER PINEDA AND RIVIERA WABASSO WABASSO SAND FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL753 753016 ma OLDSMAR 8 16 FL753 753017 ma 17 753019 8 FL753 ma 19 6 753021 FL753 ma 21 7 753022 FL753 753023 FL753 ma 22 5 ma 23 11 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 90 ENDSHWT FS DURSHWT FL0067 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUN FL0075 90ECOLCOMM SEP SMLRA 4 0.5MUKIND FL0283 D 1.5ANFLOOD FREQ N JUNANFLOOD BEG P SEP 6ANFLOOD END 95 NONE HIGHROCKDEPTH S -2.0 4 LOWROCKDEPTH NA -8 0.0SLOPE LOW JUN D S 155 NA MAR HIGHSLOPE -8 N NONE P LOWPANDEPTH 6 HIGHPANDEPTH PANHARD NA 10 0 -9OTHERPH NONE 155 -8 2 NA -9 DLEACH S -8 YRUNOFF VP FL0080CORCON 25CORSTEEL NA NA 155 -9 NA 0 NA -8 -9 2 S -8 60 LOW HIGH 0.0 FS HIGH MED NA JUN 1.0 NOV NA -9 0 FL0071 -9 2 LOW HIGH HIGH MED NONE NA 6 DC0035 NA HIGH LOW D LOW Y HIGH P 90 26 -1.0 MUCK JUN NA 155 JAN 0.0 NA -8 U -8 NONE VAR 95 2.0 NA NA 8 2.0 -9 0 -9 NONE D 2 Y VP 22 NA NA 155 HIGH LOW NA NA LOW HIGH -8 -9 -8 S NA NA N NA 155 NA NA -9 -9 0 -8 1 -8 HIGH M NA LOW MED DRAINED HIGH -9 NA -9 HIGH 0 MED 5 NA ND ND

E-156 Soil Classification Database Appendix E SALERNO SALERNO SAND ST. LUCIE - PAOLA - URBAN LAND - PAOLA LUCIE ST. PCT SLOPES 8 TO 0 COMPLEX, BESSIE MUCK CANAVERAL SAND, CANAVERAL PCT SLOPES 5 TO 0 0 TO 5 PCT SLOPES 5 TO 0 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL753 753027 ORGANIC SUBSTR., ma ARENTS, 11 27 FL753 753028 ma 9 28 753030 FL753 753034 FL753 ma 30 5 ma 34 11 753035 FL753 ma 35 8 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT S DURSHWT FL0083 2.0HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND NAANFLOOD FREQ NANFLOOD BEG SP NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW FL0060 M 155 NA 95 HIGHSLOPE -8 LOWPANDEPTH S 1.5 HIGHPANDEPTH 3.0PANHARD 0 JUN -9OTHERPH 2 NOV -9LEACHRUNOFF FL0245 6CORCON CCORSTEEL FL0057 NA N MW 95 NA NONE NA MUCK 0.0 HIGH MED 0.5 JUN NA HIGH DEC S HIGH 40 155 -8 NA S -8 6.0 NA 6.0 NA 7 FREQ D VP -9 0 19 Y -9 5 NONE -9 NA JAN E 155 NA NA DEC FL0162 -8 N NA S -8 NA HIGH MED 155 NA LOW MED -8 -9 C -8 0 -9 1 90 S 0.5 JUN NA -9 1.5 SEP 0 -9 NA LOW 8 HIGH HIGH NONE HIGH NA HIGH NA LOW MED LOW 4 D P 6 N NA 155 NA -8 S -8 50 72 0 2 LOW THIN HIGH HIGH NA HIGH

E-157 Appendix E Soil Classification Database HALLANDALE SAND JONATHAN SAND, 0 TO 5 PCT 5 TO SAND, 0 JONATHAN SLOPES SANIBEL SANIBEL MUCK FLORIDANA FINE FLORIDANA SAND, DEPRESSIONAL SLOPES MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL753 753036 2 PCT 0 TO ma ARENTS, 11 36 FL753 753038 ma 6 38 753040 FL753 753041 ma FL753 40 5 ma 41 9 753042 FL753 ma 42 8 COMPPCT 19595959090 1S5ID COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG ENDSHWT S DURSHWT FL0097 1.5HYDRIC 3.0HYDROGRPDRAINAGESPVPVPMWP JUNECOLCOMM NOVMLRA 6MUKIND NAANFLOOD FREQ NANFLOOD BEG NAANFLOOD END FL0262 NONE HIGHROCKDEPTH FS LOWROCKDEPTH NA 0.0 -8SLOPE LOW M 155 NA 0.0 HIGHSLOPE -8 JUN LOWPANDEPTH MAR HIGHPANDEPTH PANHARD 10 0 -9OTHERPH 2 D -9 FL0073LEACH YRUNOFF NONE 17CORCONCORSTEEL NA MUCK FL0159 NA -1.0 NA 156B -8 NA 0.0 S JUN APR -8 HIGH MED S MED HIGH 3.0 11 -9 0 NONE JUN -9 D 2 5.0 OCT Y 22 NA 155 NONE NA NA 5 NA -8 LOW B S HIGH -8 FL0065 MED LOW 6 N 155 NA -9 NA 0 -9 -8 2 S -8 S 0.5 NA JUN SEP UNDRAINED 1.5 LOW HIGH 50 NA HIGH LOW 0 75 5 NONE THIN LOW LOW 4 LOW HIGH D 6 N 155 NA NA 20 7 S -9 NA -9 0 2 NA HIGH HIGH HIGH LOW

E-158 Soil Classification Database Appendix E UDORTHENTS, UDORTHENTS, PCT SLOPES 35 TO 0 MALABAR FINE FINE MALABAR SAND, HIGH WULFERT AND WULFERT DURBIN MUCK, TIDAL RIVIERA FINE RIVIERA SAND, DEPRESSIONAL JUPITER SAND FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 90 ENDSHWT FS DURSHWT FL0079 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUN FL0053 90ECOLCOMM SEP SMLRA 4 FL0275 0.5MUKIND D 1.5ANFLOOD FREQ N JUNANFLOOD BEG P 95 NOV 13ANFLOOD END FS -2.0 NONE HIGHROCKDEPTH 6 LOW 0.0ROCKDEPTH JUN NA -8 MARSLOPE LOW D S 155 NA HIGHSLOPE -8 N FL0276 NONE P 13 LOWPANDEPTH HIGHPANDEPTH 10PANHARD NONE NA 0 -9 DOTHERPH 156B 20 2 NA -9 YLEACH S 60 17 8 VPRUNOFF MUCK 0.0CORCON JAN 155 NA 0.5 DECCORSTEEL NA NA -8 FL0390 -9 0 NA S -9 1 -8 FREQ MED HIGH 12 LOW HIGH NA -9 FL0089 0 D -9 NA FS 2 Y 19 VP 90 HIGH HIGH 0.5 155 JUN HIGH LOW JAN SEP NA 1.5 DEC NA -8 LOW HIGH U HIGH NONE HIGH -8 CB-S 4 95 6.0 NA -9 NA 0 -9 6.0 D P 1 6 N NONE 155 NA NA NA HIGH LOW NA HIGH HIGH -8 S -9 -8 NA W NA N 155 NA -9 NA -9 0 2 -8 HIGH NA LOW HIGH LOW NA -8 M -9 -9 MED 2 HIGH LOW 35 NA LOW NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL753 753047 ma PINELLAS 8 47 FL753 753048 ma 753049 FL753 48 8 ma 49 6 753050 FL753 ma 50 753052 2 FL753 753053 FL753 ma 52 8 ma 53 11

E-159 Appendix E Soil Classification Database HOBE FINE SAND, HOBE FINE 5 PCT 0 TO SLOPES GATOR AND GATOR MUCK TEQUESTA CHOBEE LOAMY SAND, CHOBEE LOAMY DEPRESSIONAL WABASSO AND OLDSMAR FINE AND OLDSMAR FINE WABASSO SAND, DEPRESSIONAL FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 90 ENDSHWT FS DURSHWT FL0063 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0281ECOLCOMM 60 FEB FSMLRA 9 -2.0MUKIND DANFLOOD FREQ 0.0 Y JUNANFLOOD BEG P 26 MARANFLOOD END NONE HIGHROCKDEPTH 10 LOWROCKDEPTH NA -8SLOPE LOW S D 155 NA HIGHSLOPE -8 Y NONE LOW VP 26PANDEPTH HIGHPANDEPTH PANHARD FL0412 NA 0 -9OTHERPH 155 -8 2 NA -9LEACH U -8 90RUNOFF LSCORCON 0.0CORSTEEL 0.5 NA JUN -9 OCT 0 NA -9 2 HIGH HIGH 5 MED HIGH FL0415 NA NONE D NA Y VP NA LOW HIGH MED HIGH NA 55 MUCK 155 NA -2.0 -8 FL0158 S JUN -8 0.0 APR -9 NONE 0 -9 FS 11 2 95 D 5.0 VP 25 JUN Y NA OCT 6.0 NA LOW HIGH NA 156B HIGH HIGH NA NONE -8 U -8 5 SE A 3 -9 N 0 -9 155 NA 1 NA NA -8 HIGH LOW DRAINED -8 S HIGH HIGH -9 -9 0 NA 5 LOW NA MED HIGH LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL753 753055 ma BASINGER 7 55 FL753 753056 ma 56 6 753057 FL753 ma 57 6 753058 FL753 ma 753061 58 FL753 5 ma 61 9

E-160 Soil Classification Database Appendix E PAOLA AND ST. LUCIE SAND, LUCIE AND ST. PAOLA PCT SLOPES 20 TO 8 SAMSULA SAMSULA MUCK CANOVA CANOVA MUCK HONTOON HONTOON MUCK KESSON SAND, TIDAL HOLOPAW HOLOPAW SAND FINE SAND MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL753 753063 ma NETTLES 8 63 FL753 753066 ma 66 753067 7 FL753 ma 753069 FL753 67 2 753070 FL753 ma 753073 69 FL753 5 753077 ma FL753 70 5 ma 73 5 ma 77 10 COMPPCT 190909595959560 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT ENDSHWT S DURSHWT FL0228 0.5HYDRIC 1.5HYDROGRP FL0027DRAINAGEPPVPVPVPVPE JUNECOLCOMM626192225253 SEP FSMLRA 4 0.0 FL0274MUKIND 1.0 DANFLOOD FREQ JUN N NOVANFLOOD BEGANFLOOD END S NONE FL0090 HIGHROCKDEPTH 6 0.0 LOWROCKDEPTH 0.5 NA JAN D -8SLOPE LOW DEC S 155 NA Y NONE HIGHSLOPE -8 FL0249 LOWPANDEPTH HIGHPANDEPTH NA FL0092 12PANHARD MUCK -2.0 FREQ 155 0 -8 30 NA JUNOTHERPH 0.0 D 2 APR S 50 -8LEACH YRUNOFF FL0056 CORCON MUCK JANCORSTEEL NONE 0.0 155 -9 THIN 0 DEC JUN 11 -8 -9 DEC NA 2 0.5 MUCK S -8 D Y LOW NA HIGH NONE -2.0 JUN APR MED HIGH NA 0.0 -9 NA 155 NA S 0 -9 7 NONE 1 -8 MED HIGH HIGH S -8 MED D NA NA Y 6.0 NA NA NA 155 6.0 NONE NA HIGH 11 MED -9 HIGH LOW -9 0 40 D 2 Y 24 S NA NA 155 NA HIGH UNDRAINED LOW HIGH -9 -8 HIGH -9 NA -9 -8 0 S A 1 NA NA 155 N HIGH NA LOW HIGH UNDRAINED LOW -9 -9 -8 NA HIGH 0 NA LOW -8 HIGH 2 U HIGH MED -9 -9 LOW HIGH NA HIGH 8 20

E-161 Appendix E Soil Classification Database VALKARIA VALKARIA FINE SAND BRADENTON BRADENTON FINE SAND BASINGER AND PLACID BASINGER AND PLACID DEPRESSIONAL SOILS, FINE SAND FINE WATER BASINGER NO DATA FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0323 4.0HYDRIC 6.0HYDROGRPDRAINAGE JUN NA 0ECOLCOMM OCT NAMLRA 5 -9MUKIND DC0038 A -9ANFLOOD FREQ N NA FL0063 NA 100ANFLOOD BEG MW NA 3ANFLOOD END -9 NONE HIGHROCKDEPTH -9 NA 95 FS FL0261 -9 LOWROCKDEPTH NA NA -8 LOWSLOPE NA S 155 NA NA HIGHSLOPE -8 NA 0.0 NA JUN LOWPANDEPTH 1.0 -9 NA FEB HIGHPANDEPTH NA NA FSPANHARD 60 NA NA NA 0 -9OTHERPH NA -9 NA 2 NA -9 9LEACH NA -2.0 -9 JUN DRUNOFF P 0.0 MAR Y NA NONECORCON NA FL0232 NA 26 -9CORSTEEL M NA -9 -9 -9 NA NA -9 -9 NONE 155 NA 10 D -8 FL0126 S VP MED Y MED -8 -9 -9 HIGH 25 LOW -9 NA -9 FS NA 95 NA 155 NA NA 0.5 JUN -9 NA NA 0 SEP -8 NA -9 NA 2 1.5 NA U -8 NA NA NA NA NA NONE FS NA 95 -9 JUN 4 0 0.0 HIGH SEP -9 HIGH 1 MED P D HIGH 1.0 N 8 NA NONE NA NA 155 HIGH HIGH NA MED HIGH -8 4 S -8 D P Y 26 NA 155 NA -9 0 -9 2 -8 NA S -8 LOW HIGH NA HIGH LOW -9 -9 0 2 HIGH HIGH NA HIGH NA MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL753 753078 ma DUETTE 9 78 FL753 753098 753099 FL753 ma 757002 98 12 FL757 ma 757003 99 1 FL757 ok 2 7 ok 757004 3 6 FL757 757005 FL757 ok 4 8 ok 5 7

E-162 Soil Classification Database Appendix E IMMOKALEE IMMOKALEE FINE SAND FT. DRUM FT. FINE SAND RIVIERA FINE SAND PINEDA SAND FINE FLORIDANA, RIVERIA, AND RIVERIA, FLORIDANA, SOILS, DEPRESSIONAL PLACID SAND, DEPRESSIONAL COMPPCT 195 -9 45 -9-9-9-9 95959595 VP NA 10 PPPP D 6744 NANANANA LOW-9 1 ENDNA DUR10 0 DDDD 2222 LOW0 HIGH2 U 0000 NA 1S5ID COMPPCT NANANANA 1SURFTEXT SSSS HIGHSHWT LOWSHWT SHWT BEG ENDSHWT LFSSHWT FL0322 -2.0HYDRIC 0.0HYDROGRPD DRAINAGEVP JUNECOLCOMM MARMLRAMUKINDS ANFLOOD FREQ YANFLOOD BEG 25ANFLOOD NONE HIGHROCKDEPTH FL0262 LOWROCKDEPTH FS NA -8SLOPE 155 -2.0SLOPE -8PANDEPTH 0.0 JUN HIGHPANDEPTH MARPANHARDOTHERPHNA -9LEACHRUNOFFCORCON Y NONECORSTEEL 16 NA FL0080 NA 155 -8 LOW HIGH -8 LOW HIGH FS FL0064 0.0 1.0 JUN NOV FL0225 -9 FS 0.0 FL0058 JUN NA 1.0 DEC NONE Y 26 FS LOW HIGH 0.5 MED LOW NONE JUN SEP NA 155 1.5 -8 -8 FS Y 26 NONE 0.5 JUN SEP NA 155 1.5 -8 NONE -9 -8 8 N 155 NA NA HIGH LOW -8 -9 HIGH LOW -8 6 N 155 NA NA HIGH MED HIGH HIGH -8 -9 -8 HIGH NA MED HIGH LOW -9 HIGH MED HIGH NA HIGH SOCD66 7788 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE6 NAMEMAPUNIT FL757 757006 FINE LOAMY ok MANATEE 6 FL757 757007 ok 7 757008 FL757 757009 FL757 ok 8 757010 FL757 757011 ok FL757 9 ok 10 ok 11

E-163 Appendix E Soil Classification Database PARKWOOD FIND SAND ORSINO FINE SAND OKEELANTA OKEELANTA MUCK MYAKKA MYAKKA SAND FINE MANATEE, FLORIDANA AND FLORIDANA MANATEE, OCC. FLOODED SOILS, TEQUESTA TO 35 PCT SLOPES 35 TO MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL757 757012 2 ok UDORTHENTS, 11 12 FL757 757013 ok 5 13 757014 FL757 757015 FL757 ok 14 8 757017 FL757 ok 15 757018 5 FL757 ok 17 9 ok 18 8 COMPPCT 19545 95959595 U 1S5ID SSCOMPPCT SS 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT ENDSHWT CB-S DURSHWT FL0089 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKINDM NAANFLOOD FREQ FL0289 LFS NANFLOOD BEG W NAANFLOOD END 0.0 NONE HIGHROCKDEPTH 0.5 LOWROCKDEPTH NA -8SLOPE LOW JUN 155 NA HIGHSLOPE -8 OCT LOWPANDEPTH 5 HIGHPANDEPTH DPANHARD 2 -9 YOTHERPH 35 OCCAS -9 VP 25LEACHRUNOFFCORCON JUNCORSTEEL 155 -8 FEB NA FL0059 -8 NA FS HIGH FL0071 HIGH LOW 0.5 LOW -9 0 2 -9 1.5 JUN MUCK SEP FL0103 NA -1.0 NA 4 NONE FL0099 0.0 JUN D LOW FS HIGH JAN P N LOW 6 MED NONE NA 4.0 155 NA 8 JUN -8 FS 5.0 D DEC -8 Y VP 22 NONE NA 0.5 155 NA JUN -9 SEP 1.5 0 -8 NONE 2 -9 7 -8 A MW 3 N NA NA 155 NA NA -9 MED HIGH 0 -9 1 HIGH 4 -8 HIGH P D -8 N 6 NA NA 155 HIGH MED UNDRAINED NA MED HIGH NA -9 -8 -9 0 2 -8 LOW NA HIGH LOW MED NA -9 -9 0 HIGH MED 2 NA HIGH LOW

E-164 Soil Classification Database Appendix E WABASSO WABASSO FINE SAND TERRA CEIA MUCK ST. JOHNS ST. SAND FINE POMELLO FINE SAND, POMELLO FINE 5 PCT SLOPES O TO SOILS, FREQ. FLOODED FREQ. SOILS, MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL757 757019 OKEELANTA AND PLACID ok FLORIDANA, 5 19 FL757 757020 ok 20 9 757023 FL757 757024 FL757 ok 23 7 757025 FL757 ok 24 5 ok 25 8 SHWT DUR5 5 5114 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 45 ENDSHWT FSSHWT FL0369 0.0HYDRIC 0.5HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRAMUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END FREQ HIGHROCKDEPTH LOWROCKDEPTH JUL -8SLOPE LOW U 155 SEP HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH PANHARD 0 FL0078 -9OTHERPH 95 1 -9 FSLEACHRUNOFF 2.0CORCON 3.5CORSTEEL JUL NA NOV NA LOW HIGH FL0125 C LOW MED N MW NONE 3 95 FS FL0031 NA 0.0 NA 155 -8 0.5 JUN S OCT -8 FL0075 95 MUCK -2.0 -9 0 JUN 0.0 NONE APR -9 5 D P N FS 6 95 NA NONE NA 0.5 NA NA 155 JUN SEP 1.5 -8 MED MED S D VP -8 Y HIGH LOW NONE 24 NA 155 NA -9 0 -8 -9 2 P S -8 D N 6 NA NA 155 NA NA -9 MED HIGH 0 -9 HIGH -8 HIGH 1 -8 S NA HIGH UNDRAINED MED MED MED NA -9 -9 0 2 HIGH NA LOW HIGH MED

E-165 Appendix E Soil Classification Database ARENTS - URBAN LAND ARENTS - COMPLEX, ORGANIC SUBSTR. ARENTS - URBAN LAND ARENTS PCT SLOPES 5 TO 0 COMPLEX, ADAMSVILLE FINE SAND, SAND, FINE ADAMSVILLE ORGANIC SUBSTR. FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL757 757099 ok WATER 1 99 FL760 760002 ANCLOTE pb 2 757021 6 FL757 ok 21 9 760004 FL760 pb 4 11 760005 FL760 pb 5 11 S5ID 1S5ID 1COMPPCT 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 100 ENDSHWT NA DURSHWT DC0038 -9HYDRIC FL0315 95 -9HYDROGRP FSDRAINAGE NAECOLCOMM NA FL0082 -2.0MLRA -9 0.0MUKIND JUN 95 NAANFLOOD FREQ MAR NA FSANFLOOD BEG NA NA 10 2.0ANFLOOD END NA HIGHROCKDEPTH D 3.5 JUN Y LOWROCKDEPTH NOV NA VP -9 17SLOPE LOW M NA NA HIGHSLOPE -9 NONE 6 LOWPANDEPTH FL0097 NA HIGHPANDEPTH C -8 NA 156APANHARD S N SP NONE -9 -8 -9 6OTHERPH -9 -9LEACH 65RUNOFF S NA 155CORCON 0 -9 NA 1.5 -8CORSTEEL 2 -9 NA S JUN -8 3.0 NOV NA NA NA NA -9 NA 0 NA NA 6 -9 2 NONE FL0083 NA SP HIGH N HIGH MED HIGH NA NA NA 155 NA MED NA MED -8 HIGH MED 60 C -8 S 2.0 JUN NOV 3.0 -9 0 -9 5 NONE NA 6 NA NA HIGH SP MED HIGH N MED NA 155 NA NA -8 C -8 -9 0 -9 2 NA HIGH NA LOW HIGH HIGH

E-166 Soil Classification Database Appendix E FINE SAND BEACHES BOCA BASINGER AND MYAKKA BASINGER AND MYAKKA SANDS, DEPRESSIONAL BASINGER - URBAN BASINGER - LAND COMPLEX FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0063 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0063ECOLCOMM 60 FEB FSMLRA 9 0.0MUKIND DANFLOOD FREQ 1.0 Y JUNANFLOOD BEG P 26 FEBANFLOOD END NONE HIGHROCKDEPTH 9 LOWROCKDEPTH FL0261 NA -8SLOPE LOW S NA 156B NA HIGHSLOPE -8 N NONE 60 LOW P NAPANDEPTH S HIGHPANDEPTH -2.0PANHARD 0.0 NA JUN 0 155 -9OTHERPH -8 2 NA -9 MARLEACH C -8RUNOFFCORCONCORSTEEL 10 DC0002 NA NONE D -9 0 NA -9 Y 2 25 FLO383 VP HIGH HIGH 95 156B MED NA HIGH NA S 0.0 NA -8 NA JAN U 6.0 -8 DEC HIGH HIGH HIGH MED 95 0.0 FS JUN -9 FREQ OCT 0 1.0 -9 12 2 D NONE NA Y P NA 155 NA HIGH HIGH JAN 5 HIGH DEC MED D -8 26 M -8 Y P 156B NA NA 20 -9 1 -9 S 7 3 NA HIGH HIGH NA -9 HIGH HIGH -9 0 2 MED HIGH NA HIGH NA MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL760 760006 pb BASINGER 7 6 FL760 760007 pb 11 7 760008 FL760 pb 6 8 760009 FL760 760010 FL760 pb 2 9 pb 7 10

E-167 Appendix E Soil Classification Database FLORIDANA FLORIDANA FINE SAND DANIA MUCK COCOA - URBAN LANDCOCOA PCT SLOPES 5 TO 0 COMPLEX, CHOBEE FINE SANDY LOAM TO 5 PCT SLOPES 5 PCT TO S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 60 ENDSHWT FS DURSHWT FL0060 1.0HYDRIC 3.0HYDROGRPDRAINAGE JUNECOLCOMM NOVMLRA 6MUKIND NAANFLOOD FREQ NANFLOOD BEG SP NAANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C 155 NA HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH PANHARD FL0412 0 -9 95OTHERPH FSL 2 -9LEACH -2.0RUNOFF 0.0CORCON JUNCORSTEEL FL0061 MAR NA NA S 10 65 D HIGH 6.0 MED LOW Y MED VP NONE 6.0 25 NA NA NA 155 -8 NA -9 S -8 NONE NA W N NA FL0055 -9 0 -9 NA 1 FL0262 155 NA 40 C 20 95 MUCK NA -2.0 NA 0.0 JUN FS LOW APR -9 HIGH 0 -9 HIGH 90 HIGH 5 0.0 JUN NONE 0.5 OCT 11 NA D NA HIGH NONE VP LOW 24 Y LOW LOW 5 NA 156A D NA VP 20 25 Y 8 S 156A NA NA -8 -9 0 -9 S -8 2 NA LOW DRAINED HIGH -9 MED -9 HIGH 0 NA 2 MED NA HIGH MED LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL760 760011LAND COMPLEX, 0 - URBAN pb CANAVERAL 11 11 FL760 760012 pb 6 12 760013 FL760 pb 13 11 760014 FL760 760015 FL760 pb 14 4 pb 15 6

E-168 Soil Classification Database Appendix E OKEELANTA OKEELANTA MUCK OKEECHOBEE OKEECHOBEE MUCK MYAKKA MYAKKA FINE SAND LAUDERHILL LAUDERHILL MUCK JUPITER SAND FINE IMMOKALEE IMMOKALEE SAND FINE HOLOPAW HOLOPAW SAND FINE FINE SAND FINE S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0065 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUNECOLCOMM SEP FL0264MLRA 90 4 FSMUKINDSSSSSSSS D 0.0ANFLOOD FREQ N FL0058ANFLOOD BEG 1.0 P 6 JUNANFLOOD END NOV NONE HIGHROCKDEPTH 95 FS LOWROCKDEPTH NA FL0556 20 0.5 6SLOPE LOW 156A NA HIGHSLOPE 1.5 7 JUN D LOW SEPPANDEPTH Y NONE FL0069 HIGH PPANDEPTH 25PANHARD 95 FS 0 -9OTHERPH 2 NA -9 0.0 156A 4LEACH -8 NONE NA JUN 0.5 FL0059 DRUNOFF NOV N -8CORCON P 6CORSTEEL NA 95 MUCK 156A FL0028 NA NA -2.0 NONE JUN -9 0 APR NA -8 0.0 -9 6 2 HIGH HIGH -8 D LOW HIGH Y NONE FS 156A FL0431 P 26 NA 95 NA 0.5 NA JUN -9 SEP 0 NA -9 20 1.5 11 2 MED HIGH 156A D NONE HIGH MED MUCK 8 Y 24 NA VP 95 JUN -2.0 APR NA NA MED HIGH NA NONE 0.0 -9 40 HIGH HIGH 0 -9 156A 4 1 MUCK 20 D NA N 6 P HIGH JUN HIGH NA NA JAN -1.0 95 HIGH NONE 156A LOW NA -9 -9 -8 0.0 0 11 2 HIGH D LOW NA -8 HIGH Y NA VP 25 UNDRAINED MED NA 156A NA -8 -9 -9 HIGH 0 MED 8 -8 HIGH 2 NA HIGH D NA VP DRAINED 24 Y NA HIGH -9 LOW HIGH -9 LOW -8 0 NA 1 DRAINED -8 HIGH LOW HIGH -9 MED -9 NA 0 1 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL760 760016 pb HALLANDALE 8 16 FL760 760017 pb 17 760018 7 FL760 760019 pb FL760 18 8 760020 FL760 pb 19 760021 7 FL760 760023 pb 20 FL760 4 760024 pb FL760 21 8 pb 23 5 pb 24 5

E-169 Appendix E Soil Classification Database PITS, 0 TO 5 0 TO PITS, PCT SLOPES PINELLAS PINELLAS FINE SAND MYAKKA - URBAN MYAKKA COMPLEX LAND PALM BEACH - URBAN LAND BEACH - URBAN LAND PALM PCT SLOPES 8 TO 0 COMPLEX, PAHOKEE PAHOKEE MUCK SAND S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT S DURSHWT FL0067 0.5HYDRIC 1.5HYDROGRPDRAINAGE JUN FL0072 95ECOLCOMM SEP MUCKMLRA 4 -1.0MUKIND FL0066 D 0.0ANFLOOD FREQ N JUNANFLOOD BEG P S FEB 6 60ANFLOOD END NONE HIGHROCKDEPTH 6.0 9 LOWROCKDEPTH NA 6.0 NA -8SLOPE LOW D S 156A NA NA Y HIGHSLOPE -8 NONE VP LOWPANDEPTH 24 HIGHPANDEPTH PANHARD -9 NA 156A 0 NONE -9OTHERPH 51 NA 2 NA -9 SLEACH N 36 W FL0059RUNOFF NACORCON 155 NACORSTEEL NA NA -9 -8 0 NA -9 1 C -8 FS 60 0.5 MED HIGH FL0079 HIGH MED 1.5 JUN NA -9 SEP DRAINED 0 -9 8 FL0097 LOW HIGH NA MED NONE HIGH NA 4 FS NA 95 LOW HIGH 0.5 N P LOW NA LOW JUN 1.5 155 SEP NA NA NONE -8 CB-S 95 1.5 -8 C JUN 3.0 NOV 4 D NONE 13 -9 N P 156A 0 -9 2 NA NA NA NA -8 6 NA MED HIGH 156A -8 NA S HIGH HIGH N SP NA NA -9 -8 -9 0 NA -8 2 M HIGH NA MED LOW HIGH -9 NA -9 0 MED HIGH 5 NA HIGH MED MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL760 760025 pb OLDSMAR 8 25 FL760 760026 pb 760027 26 4 FL760 pb 27 11 760022 FL760 pb 760030 22 11 FL760 760031 FL760 pb 30 8 pb 31 11

E-170 Soil Classification Database Appendix E RIVIERA FINE SAND, DEPRESSIONAL RIVIERA FINE SAND QUARTZIPSAMMENTS, QUARTZIPSAMMENTS, 5 PCT SLOPES 0 TO SHAPED, POMPANO POMPANO SAND FINE 0 TO 5 PCT SLOPES 5 TO 0 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL760 760033 pb SAND, POMELLO FINE 9 33 FL760 760034 pb 34 760035 7 FL760 pb 35 11 760036 FL760 760037 FL760 pb 36 7 pb 37 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT FS DURSHWT FL0078 2.0HYDRIC 3.5HYDROGRPDRAINAGE JULECOLCOMM NOVMLRA 5MUKIND CANFLOOD FREQ NANFLOOD BEG MW 3 FL0032ANFLOOD END 95 NONE HIGHROCKDEPTH FS LOWROCKDEPTH NA 0.0 -8SLOPE LOW FL0437 S 156A NA 0.5 HIGHSLOPE -8 JUN LOWPANDEPTH OCT 95 HIGHPANDEPTH FSPANHARD 5 2.0 0 -9OTHERPH 5 8.0 -9 NA DLEACH NA P YRUNOFF NONE 26CORCONCORSTEEL NA NA 156A -9 NA NONE -8 NA NA S -8 MW FL0064 N MED MED NA HIGH LOW 155 NA FL0275 -9 0 NA -8 -9 2 95 FS M -8 0.0 1.0 JUN NA DEC NA -9 0 -9 95 FS 5 HIGH HIGH NONE -2.0 MED HIGH JUN 0.0 7 MAR NA D P NA HIGH Y NONE LOW 26 HIGH 156B LOW NA NA 10 -8 D VP S -8 156B 25 Y NA NA -9 -8 0 -9 2 -8 S NA MED NA HIGH HIGH HIGH -9 -9 0 2 MED NA HIGH HIGH HIGH NA

E-171 Appendix E Soil Classification Database KESSON MUCKY KESSON MUCKY SAND, TIDAL TERRA MUCK CEIA TEQUESTA TEQUESTA MUCK ST. LUCIE - PAOLA - URBAN LAND - URBAN LAND - PAOLA LUCIE ST. PCT SLOPES 8 TO 0 COMPLEX, SANIBEL SANIBEL MUCK LAND COMPLEX S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 60 ENDSHWT FS DURSHWT FL0064 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUNECOLCOMM DECMLRA 7MUKIND FL0073 NAANFLOOD FREQ 90 N MUCKANFLOOD BEG P NA FL0057ANFLOOD END -1.0 NONE HIGHROCKDEPTH 0.0 S JUN LOWROCKDEPTH 40 NA APR -8SLOPE LOW C 156B NA 6.0 HIGHSLOPE -8 LOWPANDEPTH 11 6.0 NA HIGH DPANDEPTH NAPANHARD Y 0 NONE -9 25OTHERPH VP 2 -9LEACH -9RUNOFF NONE NA NA 156ACORCON -8 NA NCORSTEEL NA E S NA -8 NA 155A NA FL0077 NA -8 MED HIGH -9 0 C HIGH HIGH -8 -9 2 FL0031 MUCK 90 NA -9 -2.0 0 -9 DRAINED FL0274 8 0.0 JAN NA MUCK DEC LOW HIGH LOW HIGH NA 95 -2.0 NONE LOW HIGH 12 MUCK JUN LOW MED 0.0 D APR 24 Y VP NONE 156B 95 0.0 NA JAN 11 DEC NA 0.5 -8 D FREQ 156A S -8 24 VP Y NA 12 NA -9 155 0 -8 -9 D 2 DRAINED 52 19 S VP Y NA JAN DRAINED LOW HIGH DEC MED LOW -9 -9 -8 NA 0 1 -8 S HIGH NA LOW MED MED -9 -9 0 HIGH HIGH 1 NA HIGH LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL760 760038 pb - URBAN RIVIERA 11 38 FL760 760039 760041 pb FL760 5 39 pb 41 11 760042 FL760 760043 FL760 pb 42 760044 5 FL760 pb 43 4 pb 44 2

E-172 Soil Classification Database Appendix E WATER NO DATA WINDER WINDER FINE SAND WABASSO WABASSO SAND FINE URBAN LAND UDORTHENTS, 2 UDORTHENTS, 35 PCT SLOPES TO TORRY MUCK DURBIN MUCK, TIDAL COMPPCT 15095959595950100 SM MSSNAM 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT ENDSHWT MUCK DURSHWT FL0276 0.0HYDRIC 0.5HYDROGRPDRAINAGE JANECOLCOMM DECMLRA 12MUKINDU DANFLOOD FREQ YANFLOOD BEG MUCK VP FL0074 19ANFLOOD END FREQ HIGHROCKDEPTH FL0089 CB-S -2.0 LOWROCKDEPTH JAN -8 0.0SLOPE LOW 155 DEC JUN HIGHSLOPE -8 APR LOWPANDEPTH 6.0 HIGHPANDEPTH 11PANHARD 6.0 NA 0 -9OTHERPH NA D 1 -9 DC0035LEACH Y VP NONE VAR 24RUNOFF FL0075 -9CORCON NACORSTEEL NONE NA FS NA NA 156A -8 FL0283 W NA N NA 52 2.0 LOW 2.0 NA HIGH NA 155 NA HIGH NA NA HIGH FS -8 0.5 -9 0 -8 -9 1 1.5 DC0038 JUN NONE -9 SEP NA NONE NA -9 NA NA -2.0 NA 2 N DRAINED -9 4 35 JUN 0.0 MAR NA NA 155 LOW HIGH D NONE NA NA MED HIGH P 6 NA -8 N -9 -8 156A LOW HIGH NA NA NA LOW NA LOW -9 NA 10 D -8 -9 NA VP NA -8 -9 156A NA 26 -9 0 -9 Y 5 NA NA NA -9 NA -9 HIGH HIGH NA -8 NA -9 NA 0 NA ND 2 ND -8 NA -9 NA NA MED HIGH NA NA NA NA NA NA MED HIGH NA -9 NA -9 NA -9 NA 0 HIGH -9 MED 2 NA LOW HIGH -9 -9 NA -9 NA NA -9 -9 -9 NA NA NA NA NA NA -9 -9 NA NA -9 NA -9 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL760 760045 AND pb WULFERT 2 45 FL760 760046 760047 pb FL760 46 4 pb 47 11 760048 FL760 760049 FL760 760050 pb FL760 48 11 760098 760099 pb FL760 49 8 FL760 pb 50 6 pb 98 12 pb 99 1

E-173 Appendix E Soil Classification Database ARENTS, ORGANIC SUBSTR. ARENTS, 45 TO ARENTS, 45 TO PCT SLOPES 65 ARENTS, 0 TO ARENTS, 0 TO 5 PCT SLOPES ANKONA - URBAN COMPLEX LAND ANKONA AND SAND FARMTON DEPRESSIONAL MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL766 766001 slSAND, ANCLOTE 6 1 FL766 766002 sl 8 2 766003 FL766 sl 11 3 766004 FL766 766005 FL766 sl 11 4 766006 FL766 11 sl 5 11 sl 6 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT S DURSHWT FL0315 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND FL0086 DANFLOOD FREQ 90 YANFLOOD BEG VP S 17 0.5ANFLOOD END NONE HIGHROCKDEPTH 1.5 JUL LOWROCKDEPTH NA SEP -8SLOPE LOW S FL0086 156b NA HIGHSLOPE -8 3 LOWPANDEPTH HIGHPANDEPTH 50 DPANHARD N 0.5 P S 0 NONE -9OTHERPH 6 2 -9 1.5LEACH JUL SEPRUNOFF FL0097 NA 155CORCON -8 NACORSTEEL S NA -8 3 NA NONE NA 95 FL0085 N P HIGH HIGH 1.5 30 NA 0 MED S HIGH 50 2 3.0 JUN NOV NA 155 NA -8 C FL0083 THIN -8 NONE NA 95 6 6.0 LOW HIGH NA NA NA 6.0 VAR HIGH 30 HIGH N 0 50 SP NA 2 NONE 155 NA THIN NA -8 NA 95 -9 M -8 LOW HIGH NA 2.0 HIGH S JUN HIGH NOV 3.0 W NA N NONE -9 155 NA -9 0 NA 5 NA -8 M -8 NA 6 MED HIGH NA HIGH MED NA SP N 155 -9 NA -9 45 NA NA 65 HIGH -8 LOW LOW LOW NA -8 M -9 -9 NA 0 LOW 2 LOW HIGH HIGH NA

E-174 Soil Classification Database Appendix E CHOBEE LOAMY CHOBEE LOAMY SAND, DEPRESSIONAL 0 TO 5 PCT 0 TO SLOPES BEACHES SAND, FINE CANAVERAL SAND S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 95 ENDSHWT S DURSHWT FL0019 6.0HYDRIC 6.0HYDROGRPDRAINAGE NAECOLCOMM NAMLRA -9MUKIND AANFLOOD FREQ NANFLOOD BEG E 3ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW S 155 NA HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH FL0063 95PANHARD 0 -9OTHERPH S 5 -9 0.0LEACH DC0002 1.0RUNOFFCORCON JUN FL0060CORSTEEL FEB 95 NA 9 NA S 0.0 6.0 D JAN HIGH Y LOW NONE DEC P 95 HIGH LOW 26 1.5 FS 12 3.0 NA JUN 155 FREQ -8 NA NOV S D -8 Y FL0412 P NA NONE 6 JAN 155 -9 0 DEC -8 -9 C 2 M N -8 2 SP NA 95 155 NA NA -2.0 NA -8 -9 MK-FS JUN 1 0.0 -9 MAR S -8 HIGH 3 HIGH MED HIGH NONE NA -9 NA HIGH 0 -9 HIGH 10 5 HIGH HIGH D NA Y HIGH VP 25 MED NA NA LOW MED 156b NA -8 -8 S -9 -9 0 1 LOW NA HIGH HIGH NA HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL766 766007SLOPES 5 PCT 0 TO SAND, sl ASTATULA 10 7 BASINGER FL766 766008 7 sl 766009 8 FL766 766010 FL766 sl 2 9 sl 9 10 766011 FL766 sl 6 11

E-175 Appendix E Soil Classification Database HILOLO HILOLO SAND LOAMY HALLANDALE SAND FLUVAQUENTS, FLUVAQUENTS, FLOODED FREQUENTLY FLORIDANA SAND, FLORIDANA DEPRESSIONAL SLOPES S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG 95 ENDSHWT FS DURSHWT FL0010 2.0HYDRIC 3.5HYDROGRPDRAINAGE JULECOLCOMM OCTMLRA 4MUKIND CANFLOOD FREQ NANFLOOD BEG SP 11ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW S 155 NA FL0262 HIGHSLOPE -8 95 S LOWPANDEPTH HIGHPANDEPTH -2.0PANHARD 0.0 0 -9OTHERPH JUN 5 -9 MARLEACHRUNOFFCORCON 10CORSTEEL FL0087 NA D Y NA VP NONE 25 95 LOW C MED 0.0 NA HIGH LOW 156b -8 NA 1.0 JUN S FEB -8 9 FL0065 -9 0 FREQ -9 2 D P Y 12 FL0233 NA 95 JUN 155 NA 0.5 S FEB -8 JUN 1.5 LOW SEP S HIGH -8 LOW MED NONE 95 -9 0 4 -9 0.5 2 JUN LS SEP 1.5 D P 6 N NA NONE NA NA 155 LOW NA HIGH MED HIGH 20 4 S 7 D P N 13 NA 155 -9 NA 0 -9 2 -8 S -8 NA HIGH NA HIGH LOW HIGH -9 -9 0 2 HIGH NA LOW NA HIGH LOW MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE MAPUNIT NAME FL766 766012 sl 5 ELECTRA FINE PCT SAND, 0 TO 9 12 FL766 766013 sl 13 6 766014 FL766 14 sl 6 766015 FL766 766016 FL766 15 sl 8 16 sl 8

E-176 Soil Classification Database Appendix E LAWNWOODURBAN - LAND COMPLEX LAWNWOOD AND SAND MYAKKA KALIGA MUCK, KALIGA DEPRESSIONAL HONTOON MUCK, HONTOON DEPRESSIONAL 5 PCT SLOPES 5 MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL766 766017 sl TO HOBE SAND, 0 9 17 FL766 766018 sl 18 5 766020 FL766 20 sl 766021 5 FL766 766022 21 sl FL766 8 22 sl 11 COMPPCT 19595956060 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT SHWT BEG ENDSHWT S DURSHWT FL0158 5.0HYDRIC 6.0HYDROGRPDRAINAGESEVPVPPP JUNECOLCOMM OCTMLRA 5MUKINDSSSUC A FL0090ANFLOOD FREQ NANFLOOD BEG MUCK 3ANFLOOD END -2.0 NONE HIGHROCKDEPTH 0.0 LOWROCKDEPTH JUN NA -8 APRSLOPE LOW 155 NA HIGHSLOPE -8 FL0209 LOWPANDEPTH 11 HIGHPANDEPTH MUCK DPANHARD Y 0 -9OTHERPH NONE 5 -9 -2.0 24LEACH 0.0RUNOFF FL0221 JUN APR NACORCON 155 -8 NACORSTEEL NA S -8 NA 11 NONE 0.5 MED D LOW FL0221 -9 Y 0 HIGH JUN LOW 1.5 -9 OCT 24 2 NA 155 NA -8 NA NONE S 5 -8 UNDRAINED LOW HIGH D 0.0 HIGH N HIGH JUN 6 OCT -9 1.0 0 -9 UNDRAINED NA 1 155 NA NONE -8 NA -8 NA 5 HIGH LOW HIGH HIGH NA 20 N 0 30 NA 2 155 NA NA THIN -8 HIGH LOW NA HIGH -8 HIGH 20 30 0 2 THIN HIGH LOW HIGH HIGH

E-177 Appendix E Soil Classification Database PAOLA SAND, 0 TO SAND, 0 PAOLA 8 PCT SLOPES PALM BEACH FINE SAND, BEACH FINE PALM 5 PCT 0 TO SLOPES OLDSMAR SAND, DEPRESSIONAL JONATHAN SAND, JONATHAN PCT SLOPES 5 TO 0 MYAKKA MYAKKA SAND FINE FINE SAND FINE MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL766 766023 sl MALABAR 7 23 FL766 766024 sl 24 766019 8 FL766 19 sl 9 766026 FL766 766027 26 sl FL766 6 27 sl 766028 10 FL766 28 sl 10 OPC 99999 95 19595959595 S S 1S5ID COMPPCT S 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT ENDSHWT FS DURSHWT FL0123 0.0HYDRIC 1.0HYDROGRPDRAINAGE JUN FL0059ECOLCOMM NOV FSMLRA 6 0.5MUKINDSSS FL0159 D 1.5ANFLOOD FREQ Y JUNANFLOOD BEG P SEP 26ANFLOOD END S NONE HIGHROCKDEPTH 3.0 4 LOWROCKDEPTH NA 5.0 -8 JUNSLOPE LOW D 155 NA OCT N HIGHSLOPE -8 NONE FL0282 6 P LOWPANDEPTH HIGHPANDEPTH PANHARD 5 NA 0 -9 NONEOTHERPH 155 -8 NA 2 -9 BLEACH -8 NRUNOFF S MW 6 -2.0 FL0066CORCON JUN 0.0CORSTEEL NA MAR NA 155 -9 NA 0 -8 NA -9 2 -8 NONE LOW HIGH LOW HIGH 10 NA 50 NA D 6.0 0 FS VP 75 NA Y NA 5 MED 6.0 HIGH 25 HIGH FL0056 HIGH NA 155 THIN NA NONE -8 NA LOW LOW -8 LOW HIGH -9 A W -9 N -9 2 0 NA 155 2 NA 6.0 NA S NA NA -8 6.0 HIGH LOW NA -8 NONE HIGH MED -9 -9 0 -9 5 NA LOW E HIGH A LOW N NA LOW 155 3 NA NA -8 -8 -9 -9 0 LOW HIGH NA 8 HIGH LOW NA

E-178 Soil Classification Database Appendix E SAND PITS POMPANO PINEDA SAND PEPPER AND SAND EAUGALLIE PENDARVIS - URBAN PENDARVIS COMPLEX LAND 5 PCT SLOPES 5 S5ID 1S5ID COMPPCT 1 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT 60 ENDSHWT S DURSHWT FL0220 2.0HYDRIC 3.5HYDROGRPDRAINAGE JUNECOLCOMM OCTMLRA 5MUKIND CANFLOOD FREQ NANFLOOD BEG MW 6ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW U 155 NA HIGHSLOPE -8 LOWPANDEPTH HIGHPANDEPTH FL0220PANHARD 60 0 30OTHERPH 5 50 SLEACH 2.0RUNOFF 3.5CORCON JUNCORSTEEL OCT THIN NA 5 FL0227 NA LOW MED MW N HIGH NONE MED 60 NA S 0.5 NA 1.5 JUN 155 -8 NA SEP FL0080 C -8 DC0028 FL0032 4 30 NONE D 0 P 95 50 5 N 0.0 6 S JUN 1.0 NOV THIN NA 95 155 NA NA -8 0.0 NA NA U 6.0 VAR -8 NONE LOW MED HIGH 95 MED 6 0.0 D JUN NONE P S OCT 0.5 15 Y 30 0 NONE 26 2 NA THIN -9 156b NA NA E -8 N NA S NA -8 155 NA LOW 5 D HIGH MED NA HIGH P -8 26 Y -9 155 -9 NA -8 M 0 NA NA 2 -8 -9 -8 S -9 NA LOW NA HIGH LOW 0 HIGH 4 -9 MED MED NA ND -9 NA ND 0 HIGH HIGH 2 MED NA HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL766 766029 TO AND POMELLO sl SAND, 0 PENDARVIS 9 29 FL766 766030 sl 30 11 766031 FL766 31 sl 8 766032 FL766 766033 FL766 766034 FL766 32 sl 7 33 sl 11 34 sl 7

E-179 Appendix E Soil Classification Database SAMSULA - MYAKKA MYAKKA - SAMSULA SALINE SLIGHTLY COMPLEX, SALERNO AND SAND PUNTA RIVIERA SAND FINE RIVIERA SAND, RIVIERA DEPRESSIONAL POPLE SAND CEIA COMPLEX, TIDAL MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL766 766035 sl KESSON - TERRA 2 35 FL766 766036 766037 FL766 sl 36 7 37 sl 766038 6 FL766 766039 FL766 38 sl 7 766040 FL766 39 sl 8 40 sl 5 S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 70 ENDSHWT FS DURSHWT FL0274 0.0HYDRIC 0.5HYDROGRPDRAINAGE JANECOLCOMM DECMLRA 12MUKIND DANFLOOD FREQ YANFLOOD BEG VP 19 FL0241ANFLOOD END 95 FREQ HIGHROCKDEPTH S FL0275 LOWROCKDEPTH 0.0 JAN -8SLOPE LOW C 155 DEC 1.0 95 HIGHSLOPE -8 JUN S LOW SEPPANDEPTH -2.0 HIGHPANDEPTH 0.0 FL0064 4 JUNPANHARD 0 MAR -9OTHERPH 1 -9 DLEACH Y P FL0162RUNOFF NONE 26 10CORCON 95 NONECORSTEEL NA NA 0.0 D FS NA Y NA VP 155 -8 JUN 25 1.0 DEC S -8 FL0092 NA MED HIGH NA 156b 60 LOW HIGH -8 0.5 S NONE JUN S 7 SEP -8 -9 0 1.5 -9 2 D P Y 26 NONE -9 0 NA NA -9 156b 2 NA NA 60 4 -2.0 JUN APR -8 LOW HIGH MUCK 0.0 D NA S -8 HIGH LOW P 6 N NA NONE 155 HIGH NA LOW HIGH NA HIGH -9 -8 0 -9 2 -8 11 U NA D 155 HIGH VP NA 24 LOW Y NA HIGH HIGH 50 NA 72 0 2 -8 HIGH THIN LOW HIGH HIGH -8 NA C -9 -9 HIGH 0 NA LOW HIGH 2 HIGH UNDRAINED

E-180 Soil Classification Database Appendix E TERRA CEIA MUCK, TERRA CEIA FLOODED FREQUENTLY TANTILE AND TANTILE SAND POMPANO SUSANNA AND SAND WAUCHULA ST. LUCIE SAND, LUCIE ST. PCT SLOPES 8 TO 0 SAND S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT S DURSHWT FL0102 1.5HYDRIC 3.5HYDROGRPDRAINAGE JUN FL0057ECOLCOMM 95 NOVMLRA 6 S 6.0MUKIND CANFLOOD FREQ 6.0 N NAANFLOOD BEG SP NA 6ANFLOOD END NONE HIGHROCKDEPTH FL0226 -9 LOWROCKDEPTH NA -8SLOPE LOW S 155 NA A HIGHSLOPE -8 N E 60 NONE LOWPANDEPTH 3 HIGHPANDEPTH S 0.5PANHARD 1.5 NA 0 -9 JUNOTHERPH 155 -8 2 FL0224 -9 NA SEPLEACH S -8RUNOFFCORCON 4CORSTEEL NA NONE 60 -9 D 0 NA N -9 P 8 FL0305 0.0 S 6 1.0 JUN HIGH MED OCT NA MED LOW 155 NA NA -8 NA U -8 NONE HIGH LOW 5 95 MED LOW 0.0 D Y 15 JUN P 0.5 0 MUCK APR 30 2 26 NA 155 FREQ NA -8 THIN NA U -8 LOW HIGH 11 HIGH HIGH D Y 15 VP 30 0 22 155 JUN 2 NOV THIN -8 LOW NA -8 HIGH S HIGH HIGH -9 -9 0 NA 1 LOW HIGH MED MED NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL766 766041 SATELLITE sl 9 41 FL766 766042 sl 42 10 766043 FL766 43 sl 8 766044 FL766 766045 44 FL766 sl 7 45 sl 5

E-181 Appendix E Soil Classification Database WAVELAND AND WAVELAND FINE SAND IMMOKALEE WABASSO FINE SAND, FINE WABASSO SUBSTRATUM GRAVELLY WABASSO WABASSO SAND URBAN LAND CLAY LOAM, TIDAL CLAY S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT BEGSHWT 95 ENDSHWT CL DURSHWT FL0432 0.0HYDRIC 0.5HYDROGRPDRAINAGE JANECOLCOMM DECMLRA 12MUKIND DANFLOOD FREQ DC0035 Y 95ANFLOOD BEG VP VAR FL0075 19ANFLOOD END 2.0 FREQ HIGHROCKDEPTH 2.0 LOWROCKDEPTH S 95 NA JAN FL0244 -8SLOPE LOW NA S 155 DEC 0.5 HIGHSLOPE -8 LOWPANDEPTH -9 1.5 JUN HIGHPANDEPTH SEPPANHARD NA 95 S 0 -9 NOTHERPH NA NONE 1 -9 NA 0.5 4LEACH 1.5RUNOFF JUN NONE D NA SEPCORCON P NA N 155 -8CORSTEEL 6 NA FL0133 M -8 NA NONE NA 4 NA 156b -8 LOW D HIGH S -9 HIGH P -8 HIGH 0 N -9 13 2 NA 156b 60 NA FS -9 0.5 -8 NA 0 -9 JUN 1.5 2 S NA -8 SEP MED HIGH ND NA NONE ND NA -9 HIGH LOW 0 -9 4 2 HIGH MED D NA P 6 N HIGH 155 NA LOW NA NA HIGH MED -8 -8 U 30 50 0 2 HIGH THIN LOW NA HIGH HIGH MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODE NAMEMAPUNIT FL766 766046 SANDY sl MCKEE 2 46 FL766 766047 766048 FL766 sl 47 11 766049 FL766 48 sl 8 49 sl 8 766050 FL766 50 sl 8

E-182 Soil Classification Database Appendix E WINDER SAND, SAND, WINDER SUBSTR. SHELLY WINDER WINDER SAND LOAMY WINDER SAND, SAND, WINDER DEPRESSIONAL WAVELAND - URBAN - WAVELAND COMPLEX LAND DEPRESSIONAL S5ID 1S5ID COMPPCT 1 1SURFTEXT HIGHSHWT LOWSHWT SHWT BEG 60 ENDSHWT S DURSHWT FL0266 -2.0HYDRIC 0.0HYDROGRPDRAINAGE JUNECOLCOMM MARMLRA 10MUKIND DANFLOOD FREQ YANFLOOD BEG VP 25ANFLOOD END NONE HIGHROCKDEPTH LOWROCKDEPTH NA -8SLOPE LOW C 155 NA HIGHSLOPE -8 LOWPANDEPTH FL0133 70 HIGHPANDEPTH PANHARD FS 0.5 0 30OTHERPH 2 50 1.5LEACH JUNRUNOFF SEPCORCONCORSTEEL 4 THIN FL0283 NA NA N P NONE NA LOW 95 HIGH HIGH S HIGH -2.0 NA 0.0 JUN 155 -8 NA MAR C FL0076 -8 10 30 NONE D 0 FL0236 50 2 95 Y 25 VP 0.0 LS JUN 1.0 THIN DEC NA 155 NA NA -8 S -8 LOW HIGH NONE 95 HIGH 0.0 7 HIGH S JUL SEP D 1.0 -9 P 13 -9 0 Y 2 NONE NA NA 156b NA -8 3 NA S HIGH -8 LOW D LOW HIGH 13 P Y 156b NA -9 -9 NA 0 2 -8 NA -8 S HIGH LOW NA HIGH LOW -9 -9 0 NA 2 HIGH LOW HIGH LOW NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL766 766051 COMPLEX, - LAWNWOOD sl WAVELAND 6 51 FL766 766052 sl 52 11 766054 FL766 54 sl 6 766055 FL766 766056 FL766 55 sl 7 56 sl 7

E-183 Appendix E Soil Classification Database WATE R 8 NO DATA JUPITER FINE SAND ARCHBOLD SAND, 5 PCT 0 TO SLOPES QUARTZIPSAMMENTS, PCT SLOPES 5 TO 0 KESSON MUCK EAUGALLIE EAUGALLIE SAND FINE FINE SAND FINE COMPPCT 19595959595950100 S SNAM 1S5ID COMPPCT 1SURFTEXT SHWT HIGH LOWSHWT BEGSHWT FL0067 ENDSHWT FS DURSHWT 0.5HYDRIC 1.5HYDROGRP FL0154DRAINAGE JUNECOLCOMM SEP FSMLRA 4MUKINDSSSM FL0274 0.5 DANFLOOD FREQ 1.5 N JUNANFLOOD BEG FL0437 P 6 SEPANFLOOD END NONE HIGHROCKDEPTH MUCK LOWROCKDEPTH 4 NA 0.0 -8SLOPE LOW 155 NA 0.5 D JAN FS -8 HIGHSLOPE N DEC NONE LOWPANDEPTH P 6 HIGHPANDEPTH 2.0PANHARD JUN 8.0 0 -9 NA FL0434OTHERPH NOV 12 2 -9 155 -8 NA FREQLEACH D -8RUNOFF YCORCON VP NONE 19CORSTEEL 6 NA JAN NA -9 155 0 DEC B -9 -8 2 S N MW FL0053 -8 LOW NA HIGH NA HIGH MED 3.5 155 NA JUN NA NOV 6.0 NA -8 NA -9 0 -8 -9 LOW HIGH 1 NONE MED DC003 HIGH NA -9 6 NA FS 0 -9 HIGH MED 5 A MW LOW HIGH N JUN 0.5 NOV 3 NA NA 1.5 155 LOW NA NA MED NONE LOW HIGH NA -8 NA NA -8 -9 -9 NA NA NA NA 6 P -9 -9 D NA -9 -9 0 N NA 12 5 155 NA LOW NA HIGH MED LOW NA -9 20 NA 8 NA NA NA NA NA NA -9 NA NA NA -9 NA NA -9 NA -9 NA 0 HIGH HIGH -9 1 NA LOW HIGH NA -9 -9 -9 NA NA -9 NA NA -9 NA -9 NA NA NA -9 -9 NA NA NA -9 -9 NA MUIDSTSSAIDMUSYMCNTYABBRLSPOSCODEMAPUNIT NAME FL766 766057 sl OLDSMAR 8 57 FL766 766058 sl 58 8 766059 FL766 766060 FL766 59 sl 2 60 sl 9 766061 FL766 766062 61 FL766 sl 766098 9 766099 FL766 FL766 62 sl 8 98 sl 12 99 sl 1

E-184