ÿþ <HTML> <HEAD> <STYLE> BODY {background-color:#FBFFFF; margin:0.25in; font-size:10pt; font-family:Arial,sans-serif} H1 {margin-left:0.05in; position:relative; top:-6; text-align:center; font-weight:bold; font-size:18; font-family:Verdana,sans-serif; color:#006400} H2 {margin-left:0.25in; position:relative; top:-16; text-align:center; font-size:13; font-family:Verdana,sans-serif; color:#006400} TABLE {position:relative; top:-10; valign:top; table-layout:fixed; border-collapse:collapse} TD {text-align:center} TD {font-weight:bold; font-size:11pt; border-color:#6495ED} .tsel {color:#FFFFFF; background-color:#6495ED} .tun {color:#00008B; background-color:#B8DEFA} .tover {color:#0000CD; background-color:#B8E6FF; cursor:hand} .f {background-color:#FFFFFF; border:'1.5pt solid #6495ED'; position:relative; top:-10} .ph1 {color:#2E8B57; font-weight:bold; cursor:} .ph2 {margin-left:0.2in; color:#2E8B57; font-weight:bold; cursor:} .pover1 {color:#006000; font-weight:bold; cursor:hand} .pover2 {margin-left:0.2in; 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The final report can be accessed at http://ecosystems.alachuacounty.us/ppwse/ppwse.php (see links below).</PRE></SPAN><BR /> <SCRIPT>fix(original)</SCRIPT> </DIV> </DIV> <DIV CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Purpose <DIV ID="Purpose" CLASS="pe2" STYLE="display:"> <SPAN CLASS="lt"><PRE ID="original">The data were developed to provide quantitative area calculations for the plant community types occurring on the PPWSE Special Area Study project site.</PRE></SPAN><BR /> <SCRIPT>fix(original)</SCRIPT> </DIV> </DIV> <DIV CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Supplementary Information <DIV CLASS="pe2" STYLE="display:"> <SPAN CLASS="lt"><PRE ID="original">The Paynes Prairie West community type dataset contains descriptive data of 60 plant community association polygons delineated on the Paynes Prairie West Strategic Ecosystem (PPWSE) Special Area Study project site. The 60 polygons consist of 19 different plant communities associations and one (1) recreational land use category. To delineate the plant communities occurring on the site, a series of pedestrian transects were traversed. As in most ecological surveys, this was a time-limited survey and a budget-limited survey. All areas of the site were visited; however, more time was spent in areas considered to be critical for conservation. The total project site consisting of ±784 acres was surveyed in 15 days, indicating an average daily survey of 53 acres. The dominance of laurel oak (Quercus hemisphaerica Bartr.) over most of the study site made photointerpretation of plant association boundaries on recent aerial photographs almost impossible. Historic aerials were used to confirm the distribution of old-growth versus successional communities, but were not used in delineation of community boundaries. The lack of well-defined aerial signatures on recent aerial photographs necessitated a very extensive data collection effort to delineate the areal extent of the existing plant associations. To facilitate production of as accurate of a community map as possible, observations of plant species occurrences were recorded at 1,841 locations throughout the site. At 89 data points distributed throughout the site, data consisting of plant community descriptions, photographs, species names, parcel numbers, and other additional information were compiled on data forms. Photographs were taken at these stations to document the existing conditions of the designated community type. GPS locations were established along distinct plant community boundaries as well as within each plant community type. The plant community boundaries map was produced by using the data points collected as well as interpolation of aerial photography, where appropriate. The Alachua County 2001 LIDAR 1-ft topography was used to further interpolate boundaries between data points, where appropriate. This was accomplished by matching data points of known community boundaries with specific elevations, followed by interpolation of the boundary using the known elevation contour. The accuracy of the map produced is affected by many factors. First, all community boundaries could not be traversed with this level of effort. Surveys through dense, impassable areas were limited. Second, the accuracy of the GPS unit varies from ±9 ft to ±30 ft at this site. Third, since laurel oak is cosmopolitan in occurrence across this site, interpretation of boundaries using aerial photography proved to be of limited value in most areas. Accuracy is also dependent upon the criteria used to differentiate community types. For example, ERC distinguished six (6) different types of laurel oak communities occurring on the site. The delineation of boundaries among these types was performed based on subtle changes in density, diversity, and height of groundcover, which reflects elevation and moisture gradients. To the casual observer, these boundaries may go unnoticed. These subtle differences also require that judgement be used to establish the boundaries. Ecotones are not always sharp boundaries, but are often subtle. It would have been much easier to combine the six types of Laurel Oak communities into one category and term this habitat as Upland Oak Forest or Upland Hardwood Forest; however, these classifications offer no information regarding past disturbance or management history or the present, existing condition. In addition, the current classification attempts to delineate these communities based on historic management and existing environmental gradients such as soils, elevation, and hydrologic regime. </PRE></SPAN><BR /> <SCRIPT>fix(original)</SCRIPT> </DIV> </DIV> <DIV CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Links to graphics describing the data <DIV CLASS="pe2" STYLE="display:; position:relative; top:-15; margin-left:-0.05in"> <UL> <LI> Alachua County Department of Growth Management, GIS Division's "GeoGreen": <A TARGET="viewer" HREF="http://maps.alachuacounty.us/geogreen/">http://maps.alachuacounty.us/geogreen/</A> </LI> <LI> Paynes Prairie West Strategic Ecosystem Final Report: <A TARGET="viewer" HREF="http://ecosystems.alachuacounty.us/ppwse/ppwse.php">http://ecosystems.alachuacounty.us/ppwse/ppwse.php</A> </LI> <LI> Alachua County Department of Growth Management, GIS Division's Data Warehouse: <A TARGET="viewer" HREF="http://growth-management.alachua.fl.us/gis/warehouse.php">http://growth-management.alachua.fl.us/gis/warehouse.php</A> </LI> </UL> </DIV> </DIV> <DIV STYLE="text-align:center; color:#6495ED">_________________</DIV><BR /> <DIV CLASS="ph1" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Status of the data <DIV CLASS="pe2" STYLE="display:none"> Complete<BR /> <I>Data update frequency: </I> None planned<BR /> </DIV> </DIV> <BR /> <DIV CLASS="ph1" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Time period for which the data is relevant <DIV CLASS="pe2" STYLE="display:none"> <DIV> <I>Beginning date and time:</I> January 2007 </DIV> <DIV> <I>Ending date and time:</I> May 2007 </DIV> <DIV> <I>Description: </I> <SPAN CLASS="lt"><PRE ID="original">. The plant community association and specific composition may, in the future, change in an undetermined fashion in response to (1) natural succession, (2) climatic factors such as rainfall patterns, drought, disease and storms, (3) fire, and (4) man-made</PRE></SPAN><BR /> <SCRIPT>fix(original)</SCRIPT> </DIV> </DIV> </DIV> <BR /> <DIV CLASS="ph1" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Publication Information <DIV CLASS="pe2" STYLE="display:none"><SPAN CLASS="lt2"> <I>Who created the data: </I> Alachua County Department of Growth Management , in conjuction with Ecosystem Research, Inc. (by contract to Alachua County, served as consultant and field researcher in this project) <BR /> </SPAN> <DIV><I>Date and time: </I> 02/12/2008 </DIV> <DIV><I>Publisher and place: </I> Alachua County Department of Growth Management, Alachua County, Fl </DIV> </DIV> </DIV> <DIV STYLE="text-align:center; color:#6495ED">_________________</DIV><BR /> <DIV CLASS="ph1" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Data storage and access information <DIV CLASS="pe2" STYLE="display:none"> <I>File name: </I>Paynes_Prairie_West<BR /> <I>Type of data: </I>vector digital data<BR /> <DIV><I>Location of the data: </I></DIV> <DIV><LI STYLE="margin-left:0.2in">\\alachua\acdfs\Growth_GIS\Data\Shapefiles\Paynes_Prairie_West.shp</LI></DIV> <I>Data processing environment: </I><SPAN CLASS="lt">Microsoft Windows XP Version 5.1 (Build 2600) Service Pack 2; ESRI ArcCatalog 9.2.4.1420</SPAN><BR /> <DIV CLASS="ph1" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Accessing the data <DIV CLASS="pe2" STYLE="display:none"> <I>Size of the data: </I>0.065 MB<BR /> <I>Data transfer size: </I>0.002 MB<BR /> <BR /> </DIV> </DIV> <DIV CLASS="ph1" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Constraints on accessing and using the data <DIV CLASS="pe2" STYLE="display:none"> <I>Access constraints: </I> <SPAN CLASS="lt">No Constraints.<BR /></SPAN> <DIV> <I>Use constraints: </I> <SPAN CLASS="lt"><PRE ID="original">This dataset is based on interpretation of available information and should not be considered as the only source for making decisions. Datasets with no defined source, scale, or accuracy should be considered suspect. Make sure you are familiar with the data before using it for projects, analyses, or other actions. In addition, make sure you abide by the regulatory process which the dataset supports when using it. Scale is an important factor in data usage. Please be aware that some of our data sets are based on original data sources of different scales and a few are based on original data sources for which we have not inherited definitive scale information. For additional information regarding scale and accuracy see http://www.geoplan.ufl.edu/education.html.</PRE></SPAN><BR /> <SCRIPT>fix(original)</SCRIPT> </DIV> </DIV> </DIV> </DIV> </DIV> <BR /> <DIV CLASS="ph1" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Details about this document <DIV CLASS="pe2" STYLE="display:none"> Contents last updated: 20080725 at time 15411500 <DIV CLASS="ph1" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Who completed this document <DIV CLASS="pe2" STYLE="display:none"> Peter M. Wallace <BR /> ECOSYSTEM RESEARCH CORPORATION <BR /> <I> mailing address :</I> <BR /> <DIV STYLE="margin-left:0.3in"> <DIV CLASS="lt"> <PRE ID="original"> 2906 NW 142nd Avenue </PRE> <SCRIPT> fix(original) </SCRIPT> </DIV> <DIV> Gainesville, FL 32609 </DIV> <DIV> USA </DIV> </DIV> <BR /> 386-462-5005 (voice) <BR /> 352-538-0755 (voice) <BR /> 386-462-7748 (fax) <BR /> ecores@alltel.net <BR /> <BR /> <DIV> <I>Hours of service:</I> 8 am - 9 pm EST </DIV> <BR /> </DIV> </DIV> <DIV CLASS="ph1" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Standards used to create this document <DIV CLASS="pe2" STYLE="display:none"> <I>Standard name: </I>FGDC Content Standards for Digital Geospatial Metadata<BR /> <I>Standard version: </I>FGDC-STD-001-1998<BR /> <I>Time convention used in this document: </I>local time<BR /> Metadata profiles defining additonal information <LI STYLE="margin-left:0.2in"> ESRI Metadata Profile: <A TARGET="viewer" HREF="http://www.esri.com/metadata/esriprof80.html ">http://www.esri.com/metadata/esriprof80.html </A> </LI> <LI STYLE="margin-left:0.2in"> ESRI Metadata Profile: <A TARGET="viewer" HREF="http://www.esri.com/metadata/esriprof80.html ">http://www.esri.com/metadata/esriprof80.html </A> </LI> </DIV> </DIV> </DIV> </DIV> <BR /> </DIV> <DIV ID="Spatial" class="pv" STYLE="display:none"><BR /> <DIV CLASS="pn">Horizontal coordinate system</DIV> <DIV STYLE="margin-left:0.2in"><I>Projected coordinate system name: </I>NAD_1983_StatePlane_Florida_North_FIPS_0903_Feet</DIV> <DIV STYLE="margin-left:0.2in"><I>Geographic coordinate system name: </I>GCS_North_American_1983</DIV> <DIV CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Details <DIV CLASS="pe2" STYLE="display:none"> <DIV CLASS="sr1"> <SPAN CLASS="pn">Map Projection Name:</SPAN> Lambert Conformal Conic </DIV> <DIV CLASS="sr2"> <I>Standard Parallel:</I> 29.583333 <BR /> <I>Standard Parallel:</I> 30.750000 <BR /> <I>Longitude of Central Meridian:</I> -84.500000 <BR /> <I>Latitude of Projection Origin:</I> 29.000000 <BR /> <I>False Easting:</I> 1968500.000000 <BR /> <I>False Northing:</I> 0.000000 <BR /> </DIV> <BR /> <DIV CLASS="sr1"> <SPAN CLASS="pn">Planar Coordinate Information</SPAN> </DIV> <DIV CLASS="sr2"> <I>Planar Distance Units:</I> survey feet </DIV> <DIV CLASS="sr2"> <I>Coordinate Encoding Method:</I> coordinate pair </DIV> <DIV CLASS="srh2">Coordinate Representation</DIV> <DIV CLASS="sr3"> <I>Abscissa Resolution:</I> 0.000000 </DIV> <DIV CLASS="sr3"> <I>Ordinate Resolution:</I> 0.000000 </DIV> <BR /> <DIV CLASS="srh1">Geodetic Model</DIV> <DIV CLASS="sr2"> <I>Horizontal Datum Name:</I> North American Datum of 1983 </DIV> <DIV CLASS="sr2"> <I>Ellipsoid Name:</I> Geodetic Reference System 80 </DIV> <DIV CLASS="sr2"> <I>Semi-major Axis:</I> 6378137.000000 </DIV> <DIV CLASS="sr2"> <I>Denominator of Flattening Ratio:</I> 298.257222 </DIV> </DIV> </DIV> <DIV STYLE="text-align:center; color:#6495ED">_________________</DIV><BR /> <DIV CLASS="pn">Bounding coordinates</DIV> <DIV STYLE="margin-left:0.2in" CLASS="pn">Horizontal</DIV> <DIV STYLE="margin-left:0.4in" CLASS="pn">In decimal degrees</DIV> <DIV STYLE="margin-left:0.6in"><I>West: </I> -82.412534 </DIV> <DIV STYLE="margin-left:0.6in"><I>East: </I> -82.390509 </DIV> <DIV STYLE="margin-left:0.6in"><I>North: </I> 29.584589 </DIV> <DIV STYLE="margin-left:0.6in"><I>South: </I> 29.557597 </DIV> <DIV STYLE="margin-left:0.4in" CLASS="pn">In projected or local coordinates</DIV> <DIV STYLE="margin-left:0.6in"><I>Left: </I>2632173.528711</DIV> <DIV STYLE="margin-left:0.6in"><I>Right: </I>2638998.458634</DIV> <DIV STYLE="margin-left:0.6in"><I>Top: </I>218677.442564</DIV> <DIV STYLE="margin-left:0.6in"><I>Bottom: </I>208985.072679</DIV> <DIV STYLE="text-align:center; color:#6495ED">_________________</DIV><BR /> <DIV CLASS="pn">Spatial data quality</DIV> <DIV CLASS="ph2" STYLE="margin-left:0.2in" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">Horizontal positional accuracy <DIV CLASS="pe2" STYLE="margin-left:0.2in; display:none"> <SPAN CLASS="lt"><PRE ID="original">Horizontal accuracy is limited by the GPS's positional accuracy, which is reported to be between 9-30ft, aerial resolution identifying trees along habitat boundaries, and also habitat boundaries themselves which were often subject to judgement by the field consultant according to soils, elevation, and hydrologic regime.</PRE></SPAN> <SCRIPT>fix(original)</SCRIPT> </DIV> </DIV> <DIV STYLE="text-align:center; color:#6495ED">_________________</DIV><BR /> <DIV CLASS="pn">Spatial data description</DIV> <DIV CLASS="pn" STYLE="margin-left:0.2in">Vector data information</DIV> <DIV STYLE="margin-left:0.4in" CLASS="pn">ESRI description</DIV> <DIV CLASS="ph2" STYLE="margin-left:0.6in" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)"> Paynes_Prairie_West <DIV CLASS="pe2" STYLE="display:none"> <I>ESRI feature type: </I>Simple<BR /> <I>Geometry type: </I>Polygon<BR /> <I>Topology: </I>FALSE<BR /> <I>Feature count: </I>60<BR /> <I>Spatial Index: </I>FALSE<BR /> <I>Linear referencing: </I>FALSE<BR /> </DIV> </DIV> <BR /> <DIV CLASS="ph2" STYLE="margin-left:0.4in" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)">SDTS description <DIV CLASS="pe2" STYLE="display:none"> <DIV>Feature class: SDTS feature type, feature count</DIV> <DIV STYLE="margin-left:0.2in"> <LI> Paynes_Prairie_West: G-polygon, 60 </LI> </DIV> </DIV> </DIV> <BR /> </DIV> <DIV ID="Attributes" class="pv" STYLE="display:none"><BR /> <DIV CLASS="pn">Details for Paynes_Prairie_West</DIV> <DIV STYLE="margin-left:0.2in"> <I>Type of object:</I> Feature Class </DIV> <DIV STYLE="margin-left:0.2in"> <I>Number of records:</I> 60 </DIV> <DIV STYLE="margin-left:0.2in" CLASS="pn"> Attributes <DIV STYLE="margin-left:0.25in" CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)"> FID <DIV CLASS="pe2" STYLE="display:none"> <I>Alias:</I> FID <BR /> <I>Data type:</I> OID <BR /> <I>Width:</I> 4 <BR /> <I>Precision:</I> 0 <BR /> <I>Scale:</I> 0 <BR /> <SPAN CLASS="lt"> <I>Definition:</I> <PRE ID="original"> Internal feature number. </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <SPAN CLASS="lt"> <I>Definition Source:</I> <PRE ID="original"> ESRI </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <BR /> </DIV> </DIV> </DIV> <DIV STYLE="margin-left:0.2in" CLASS="pn"> <DIV STYLE="margin-left:0.25in" CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)"> Shape <DIV CLASS="pe2" STYLE="display:none"> <I>Alias:</I> Shape <BR /> <I>Data type:</I> Geometry <BR /> <I>Width:</I> 0 <BR /> <I>Precision:</I> 0 <BR /> <I>Scale:</I> 0 <BR /> <SPAN CLASS="lt"> <I>Definition:</I> <PRE ID="original"> Feature geometry. </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <SPAN CLASS="lt"> <I>Definition Source:</I> <PRE ID="original"> ESRI </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <BR /> </DIV> </DIV> </DIV> <DIV STYLE="margin-left:0.2in" CLASS="pn"> <DIV STYLE="margin-left:0.25in" CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)"> ACRES <DIV CLASS="pe2" STYLE="display:none"> <I>Alias:</I> ACRES <BR /> <I>Data type:</I> Number <BR /> <I>Width:</I> 19 <BR /> <I>Number of decimals:</I> 2 <BR /> <SPAN CLASS="lt"> <I>Definition:</I> <PRE ID="original"> GIS Calculated Acreage </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <BR /> </DIV> </DIV> </DIV> <DIV STYLE="margin-left:0.2in" CLASS="pn"> <DIV STYLE="margin-left:0.25in" CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)"> REFID <DIV CLASS="pe2" STYLE="display:none"> <I>Alias:</I> REFID <BR /> <I>Data type:</I> Number <BR /> <I>Width:</I> 2 <BR /> <SPAN CLASS="lt"> <I>Definition:</I> <PRE ID="original"> Reference ID. Unique ID which may be referenced in the special area study report. </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <SPAN CLASS="lt"> <I>Definition Source:</I> <PRE ID="original"> Ecosystems Research, Inc. </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <BR /> </DIV> </DIV> </DIV> <DIV STYLE="margin-left:0.2in" CLASS="pn"> <DIV STYLE="margin-left:0.25in" CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)"> Habitat <DIV CLASS="pe2" STYLE="display:none"> <I>Alias:</I> HABITAT <BR /> <I>Data type:</I> String <BR /> <I>Width:</I> 100 <BR /> <I>Precision:</I> 0 <BR /> <I>Scale:</I> 0 <BR /> <SPAN CLASS="lt"> <I>Definition:</I> <PRE ID="original"> Habitat or Vegative Community </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <SPAN CLASS="lt"> <I>Definition Source:</I> <PRE ID="original"> Ecosystems Research, Inc. </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <BR /> <FONT color="#0000AA"> <B>Attribute domain values:</B> </FONT> <BR /> <BR /> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Laurel Oak, Type1 <BR /> <B>Definition:</B> The Laurel Oak - Type 1 community type is characterized as having a laurel oak(Quercus hemisphaerica Bartr.)-dominated canopy, which is generally greater than 90 to 95% of the total density and cover. The groundcover within this community type is very dense and typically consists of woody species dominated by saplings and seedlings of laurel oak (Quercus hemisphaerica Bartr.), live oak (Quercus virginiana Mill.), muscadine grape (Vitis rotundifolia Michx.), Virginia creeper (Parthenocissus quinquefolia [L.] Planch.), and trumpet creeper (Campsis radicans [L.] Seemann ex Bureau). Many of the areas are impassable to pedestrian traffic, requiring pathway enhancement with machetes. Density of the groundcover varies, which appears to reflect the hydrologic regime of the location. This community type typically occurs along the slopes between the drier ridges and more mesic depressions on the site. However, there are exceptions where Laurel Oak - Type 1 is found in ridge and valley areas. Groundcover decreases in density and height at the top of the slopes and increases in height, density, and cover moving downhill. This is also a characteristic of the size of canopy trees. The trees tend to be much smaller (diameter at breast height [dbh]) on the top of the slopes with a substantial increase in size occurring as elevation decreases within the area. These relationships occur with exception; however, are visually apparent in the majority of areas of this community type. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Laurel Oak, Type 2 <BR /> <B>Definition:</B> The Laurel Oak - Type 2 plant community association is primarily found on the ridges and broad, flat areas of the landscape. Historically, the majority of the areas presently mapped as this community type were most probably Sandhill communities dominated by long-leaf pine (Pinus palustris Mill.) and xeric oaks to include scrub live oak (Quercus geminata Small), sand-post oak (Quercus margaretta Ashe), and southern red oak (Quercus falcata Michx.). These species are common in the canopy of small areas within this community type; however, laurel oak (Quercus hemisphaerica Bartr.) is the dominant canopy species in areas characterized by the Laurel Oak - Type 2 plant community nomenclature. The plant community association encompasses many areas that may be described as "former Sandhill." However, the plant associations, as mapped, contain very few areas with common Sandhill groundcover, such as wiregrass (Aristida stricta Michx.), gopher apple (Licania michauxii Prance.), and Florida greeneyes (Berlandiera subacaulis [Nutt.] Nutt), etc. In areas where wiregrass survives, it is very sporadic in occurrence. The dominant deterministic factor for this plant community association is the laurel oak (Quercus hemisphaerica Bartr.) canopy and subcanopy. The laurel oak in this community tend to be small trees (2" to 8" dbh) and extremely dense in many areas. The groundcover is very sparse, typically being dominated by laurel oak. However, herbaceous species such as tread-softly (Cnidoscolus stimulosus [Michx.] Engelm. &amp; A. Gray), needleleaf witchgrass (Dichanthelium aciculare [Desv. exPoir.] Gould &amp; C. A. Clark), retrorse flatsedge (Cyperus retrorsus Chapm.), wiregrass (Aristida stricta Michx.), golden aster (Pityopsis graminifolia [Michx.] Nutt.), bahiagrass (Paspalum notatum Fluegge.), and white wild indigo (Baptisia alba [L.] Vent.) are common. Many of the areas within this community type appear park-like, being very easy to traverse and very open. However, this community has a very low diversity of plant species cover and invariably laurel oak is dominant. There were gopher tortoise (Gopherus polyphemus) burrows found within this community type; however, habitat quality is very poor. The tortoise burrows occur in small areas where the canopy is sparse and sunlit areas are more prevalent. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Laurel Oak, Type 3 <BR /> <B>Definition:</B> The Laurel Oak - Type 3 community is a variety of the Type 1 community; however, the groundcover has been seriously disturbed by cattle. The dominant canopy species are laurel oak (Quercus hemisphaerica Bartr.), but southern red oak (Quercus falcata Michx.), water oak (Quercus nigra L.), scrub live oak (Quercus geminata Small), flowering dogwood (Cornus florida L.), loblolly pine (Pinus taeda L.), and longleaf pine (Pinus palustris Mill.) are scattered throughout the area. Groundcover species include American beautybush (Callicarpa americana L.), tread-softly (Cnidoscolus stimulosus [Michx.] Engelm. &amp; A. Gray), muscadine grape (Vitis rotundifolia Michx.), and calloose grape (Vitis shuttleworthii House). Common shrub species include yellowleaf hawthorn (Crataegus flava Aiton), sparkleberry (Vaccinium arboreum Marsh.), with American holly (Ilex opaca Ait.) and flowering dogwood (Cornus florida L.) found in the understory. Evidence of recent cattle activity is apparent throughout the area. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Laurel Oak, Type 4 <BR /> <B>Definition:</B> The Laurel Oak - Type 4 community is a variant of the Type 1 association; however, the canopy contains greater numbers of species such as live oak (Quercus virginiana Mill.), scrub live oak (Quercus geminata Small), sweetgum (Liquidambar styraciflua L.), slash pine (Pinus elliottii Engelm.), American basswood (Tilia americana L.), and southern magnolia (Magnolia grandiflora L.). Common subcanopy and shrub species include crossvine (Bignonia capreolata L.), American beautybush (Callicarpa americana L.), poison ivy (Toxicodendron radicans [L.] Kuntze), Matelea species, Carolina holly (Ilex ambigua* [Michx.] Torr.), flatwoods plum (Prunus umbellata Elliott),partridgeberry (Mitchella repens L.), red bay (Persea borbonia [L.] Spreng.),and laurel cherry (Prunus caroliniana Ait.). This community type may not be considered significantly different than the Laurel Oak - Type 1 community by many ecologists. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Laurel Oak, Type 5 <BR /> <B>Definition:</B> The Laurel Oak - Type 5 community is a Laurel Oak - Type 1 area in which the canopy has been removed or altered either by disease, wind damage, or logging. In these areas, there are large expanses of dense, vine-covered, laurel oak-groundcover dominated areas. The areas are very dense where the tangle of vines and briars often precluded economical pedestrian travel. The canopy is absent in areas, but, when present, is dominated by laurel oak (Quercus hemisphaerica Bartr.), in which many are damaged as evidenced by top bole death and branch death. The groundcover is a tangle of muscadine grape (Vitis rotundifolia Michx.), poison ivy (Toxicodendron radicans [L.] Kuntze), Virginia creeper (Parthenocissus quinquefolia [L.] Planch.), and trumpet creeper (Campsis radicans [L.] Seemann ex Bureau) mixed with a cover of very small laurel oak (Quercus hemisphaerica Bartr.) seedlings. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Laurel Oak, Type 6 <BR /> <B>Definition:</B> The Laurel Oak - Type 6 communities are disturbed oldfield areas in which laurel oak is common and will, in the future, be the dominant species. The canopy in these areas is sparse with bare ground and sunlit areas being common. Common subcanopy and shrub size class species include cabbage palm (Sabal palmetto [Walt.] Lodd. ex J. &amp; J. Schultes), black cherry (Prunus serotina Ehrh.), yellowleaf hawthorn (Crataegus flava Aiton), sparkleberry (Vaccinium arboreum Marsh.), chickasaw plum (Prunus angustifolia Marshall), winged sumac (Rhus copallina L.), red cedar (Juniperus virginiana L.), Carolina buckthorn (Rhamnus caroliniana Walter), live oak (Quercus virginiana Mill.),and scrub live oak (Quercus geminata Small). The area supports a more diverse groundcover than most forested areas as might be expected. The area within polygon 58 is an excavated borrow area surrounded by a mix of laurel oak - oldfield species. Based on review of historic aerials, the area is shown to flood during periods of high rainfall. However, flooding is not frequent enough to create wetland conditions as determined by Chapter 62-340 FAC, Delineation of the Landward Extent of Wetlands and Surface Waters. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Sandhill <BR /> <B>Definition:</B> There are many areas within the project site that historically would have been Sandhill and dominated by longleaf pine (Pinus palustris Mill.) and turkey oak (Quercus laevis Walt.) with a predominantly wiregrass (Aristida stricta Michx.) understory. There are Sandhill areas that are dominated by turkey oak (Polygon 6), mixed xeric oaks (turkey oak, southern red oak, sand-post oak; Polygon 7), and sand live oak (Polygon 35). There is a Sandhill area (designated as Polygon 5) that is dominated by a longleaf pine and mixed xeric oak canopy and subcanopy; however,bahiagrass (Paspalum notatum Fluegge.) is the dominant groundcover in many areas. Despite the bahiagrass cover and grazing activity, this area displays the best association of canopy, subcanopy, and groundcover flora of any Sandhill area located within the Special Area Study project site.The Sandhill Communities occur along the broad ridges on the project site and are characterized by a low diversity, sparse understory. Gopher tortoises (Gopherus polyphemus) are found throughout this habitat type. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Mixed Pine-Laurel Oak <BR /> <B>Definition:</B> The Mixed Pine - Laurel Oak communities are areas in which laurel oak is the dominant species within the canopy, subcanopy, and groundcover size classes; however, large pines are a notable component of the canopy. In some areas, one pine species may be dominant; however, in most areas, a mix of longleaf pine (Pinus palustris Mill.) and loblolly pine (Pinus taeda L.) are present with slash pine (Pinus elliottii Engelm.) generally being less common. The canopy typically has a dominant cover of laurel oak (Quercus hemisphaerica Bartr.) with a subcanopy dominated by laurel oak (Quercus hemisphaerica Bartr.). <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Mesic Hammock <BR /> <B>Definition:</B> The lower elevation valleys and depressions on the project site are characterized by diverse, high-quality Mesic Hammock and Live Oak Hammock plant communities. These are the least disturbed, most intact plant communities on the project site. The species composition of both community types is similar except that within the mapped Live Oak Hammock areas, large, sprawling, specimen individuals of live oak (Quercus virginiana Mill.) are the dominant feature of the canopy. The Mesic Hammock communities typically occurring immediately up-slope from Oak Hammock. The Mesic Hammock is almost always bordered by a Laurel Oak - Type 1 area, which is up-slope. Past management has altered this ecotonal relationship; however, in most areas it is visually apparent and predicable. Live oak occurs within the mapped Mesic Hammock areas and, in some areas, it is difficult to map the true boundary of these community types; however, the differences in the abundance of large live oaks is the differentiating criterion used. Canopy, subcanopy, and groundcover is varied. Particularly impressive areas include those having a dense subcanopy of American holly (Ilex opaca Ait.) or wild olive (Osmanthus americanus [L.] Benth. &amp; Hook. ex Gray). In addition, the dominance of the groundcover in many areas by devil's walkingstick (Aralia spinosa L.), Carolina holly (Ilex ambigua* [Michx.] Torr.), and smallfruited pawpaw (Asimina parviflora [Michx.] Dunal) is unique. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Oak Hammock <BR /> <B>Definition:</B> Same as Mesic Hammock, but canopy is dominated by live oak (Quercus virginiana Mill.) The live oak dominated areas are typically found in the lowest elevations of the on-site valleys. See Mesic Hammock. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Freshwater Marsh <BR /> <B>Definition:</B> Freshwater Marsh <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Mixed Hardwood Hydric Hammock <BR /> <B>Definition:</B> Mixed hardwood seepage area adjacent to marsh; dominated by live oak (Quercus virginiana Mill.), sweetgum Figure 33. Panoramic view of the Freshwater Marsh plant community association (GPS Point 1070). Special Area Study: Ecological Assessment of the Plant Communities &amp; Natural Resources Occurring within the Paynes Prairie West Strategic Ecosystem August 2007 56 (Liquidambar styraciflua L.), sugarberry (Celtis laevigata Willd.), swamp black gum (Nyssa sylvatica Marsh. var. biflora [Walt.] Sarg.), cabbage palm (Sabal palmetto [Walt.] Lodd. ex J. &amp; J. Schultes), and persimmon (Diospyros virginiana L.). Groundcover species include Spanish needles (Bidens bipinnata L.), coastalplain chaffhead (Carphephorus corymbosus [Nutt.] Torr. &amp; A. Gray), openflower witchgrass (Dichanthelium laxiflorum [Lam.] Gould), woodsgrass (Oplismenus hirtellus [L.] P.Beauv.), dimorphic chain fern (Woodwardia areolata [L.] Moore), and royal fern (Osmunda regalis* L.). <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Oldfield-Shrubs (Disturbed) <BR /> <B>Definition:</B> The Oldfield - Shrubs (Disturbed) community is a previously cleared, successional area with a host of ruderal groundcover species present. There is a mosaic of canopy and subcanopy size trees to include black cherry (Prunus serotina Ehrh.), slash pine (Pinus elliottii Engelm.), loblolly pine (Pinus taeda L.), red cedar (Juniperus virginiana L.), laurel oak (Quercus hemisphaerica Bartr.), scrub live oak (Quercus geminata Small), and cabbage palm (Sabal palmetto [Walt.] Lodd. ex J. &amp; J. Schultes). Common shrubs include dwarf hawthorn (Crataegus uniflora Munchh.), yellowleaf hawthorn (Crataegus flava Aiton), chickasaw plum (Prunus angustifolia Marshall), winged sumac (Rhus copallina L.), and saw palmetto (Serenoa repens [Bartr.] Small). Common groundcover species include bahiagrass (Paspalum notatum Fluegge.), sand blackberry (Rubus cuneifolius Pursh), muscadine grape (Vitis rotundifolia Michx.), broomsedge (Andropogon virginicus L.), pricklypear (Opuntia humifusa [Raf.] Raf.), camphorweed (Heterotheca subaxillaris [Lam.] Britton &amp; Rusby), and needleleaf witchgrass (Dichanthelium aciculare [Desv. ex Poir.] Gould &amp; C. A. Clark). The general appearance of the Old Field - Shrubs (Disturbed) plant community association is presented in Figure 35. The area has many pocket gophers and several gopher tortoise burrows were found. Based on review of the 1937 aerial, this area was probably historically a Sandhill community. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Improved Pasture <BR /> <B>Definition:</B> Improved Pasture with a dense cover of bahiagrass (Paspalum notatum Fluegge.) as the dominant community feature. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> Recreational Area <BR /> <B>Definition:</B> Recreational Area with small building and parking facilities. <BR /> <BR /> </DIV> </DIV> </DIV> </DIV> <DIV STYLE="margin-left:0.2in" CLASS="pn"> <DIV STYLE="margin-left:0.25in" CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)"> FLUCCs <DIV CLASS="pe2" STYLE="display:none"> <I>Alias:</I> FLUCCS <BR /> <I>Data type:</I> Double <BR /> <I>Width:</I> 13 <BR /> <I>Precision:</I> 12 <BR /> <I>Scale:</I> 11 <BR /> <SPAN CLASS="lt"> <I>Definition:</I> <PRE ID="original"> FLUCCs code classification (Florida Land Use, Cover, and Forms classification system. </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <SPAN CLASS="lt"> <I>Definition Source:</I> <PRE ID="original"> Ecosystems Research, Inc. </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <BR /> </DIV> </DIV> </DIV> <DIV STYLE="margin-left:0.2in" CLASS="pn"> <DIV STYLE="margin-left:0.25in" CLASS="ph2" onmouseover="doHilite()" onmouseout="doHilite()" onclick="hideShowGroup(this)"> Priority <DIV CLASS="pe2" STYLE="display:none"> <I>Alias:</I> PRIORITY <BR /> <I>Data type:</I> SmallInteger <BR /> <I>Width:</I> 4 <BR /> <I>Precision:</I> 4 <BR /> <I>Scale:</I> 0 <BR /> <SPAN CLASS="lt"> <I>Definition:</I> <PRE ID="original"> Priority in conservation value of the specific plant community. </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <SPAN CLASS="lt"> <I>Definition Source:</I> <PRE ID="original"> Alachua County Growth Management, GIS Division </PRE> </SPAN> <SCRIPT> fix(original) </SCRIPT> <BR /> <FONT color="#0000AA"> <B>Attribute domain values:</B> </FONT> <BR /> <BR /> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> 1 <BR /> <B>Definition:</B> PRIORITY 1 PLANT COMMUNITIES: These are the highest quality plant associations in which any disturbance would be detrimental to the integrity of the system. These areas represent climax plant associations and require little to no management. No type of development should occur in these habitats including roads, buildings, power line easements, or other utility easements. These areas include the following communities: Mesic Hammock, Live Oak Hammock, Freshwater Marsh, and Mixed Hardwood Hydric Hammock. These habitats are roughly defined as occurring below the 67-ft contour on the site. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> 2 <BR /> <B>Definition:</B> PRIORITY 2 PLANT COMMUNITIES: This category includes the Sandhill habitats, which are severely disturbed, however, still maintain a population of gopher tortoise burrows. These areas could potentially be regulated under Article 4, Listed Plant and Animal Species Habitat. These habitats may be substantially enhanced by a fire management program. These areas include the following community types Sandhill: Longleaf Pine - Xeric Oaks, Sandhill: Longleaf Pine - Xeric Oaks - Bahiagrass, Sandhill: Mixed Xeric Oaks, Sandhill: Sand Live Oak, and Sandhill: Turkey Oak - Longleaf Pine. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> 3 <BR /> <B>Definition:</B> PLANT COMMUNITIES: The Priority 3 areas are primarily the successional Laurel Oak regrowth areas represented by the Laurel Oak - Type 1 communities. Other areas included are two (2) Mixed Pine - Laurel Oak areas within the Live Oak Hammock community. These are low diversity habitats that have regenerated in areas previously cleared for agriculture. Plant community structure is highly variable within this community type, but the primary characteristic is the dominance of laurel oak (Quercus hemisphaerica Bartr.) in all levels of the community structure, e.g., canopy, subcanopy, and groundcover. The most significant value of this plant association is that it forms forested buffers around all Priority 1 areas. In addition, the Priority 1 areas are connected to one another via topographic valleys occurring between the 68- and 67-ft contour. Hence development within this habitat type should be prioritized based on elevation. <BR /> <BR /> </DIV> <DIV STYLE="margin-left:0.5in"> <B>Value:</B> 4 <BR /> <B>Definition:</B> PLANT COMMUNITIES: These are the lowest quality habitats on site and are mostly associated with historic Sandhill areas. Species diversity is low and there is minimal habitat structure as related to distribution and development of canopy, subcanopy, and groundcover species. This designation primarily includes the Laurel Oak - Type 2 habitats but also includes the Oldfield areas and disturbed Laurel Oak - Type 3, Type 5, and Type 6 habitats. These communities will require substantial restoration in addition to fire to develop into a high-quality natural system. Gopher tortoises do occur within this habitat, but tortoise habitat quality is poor. Movement of the tortoises to better habitat areas is recommended. <BR /> <BR /> </DIV> </DIV> </DIV> </DIV> <BR /> </DIV> </DIV> </BODY> </HTML>