<?xml version="1.0" encoding="UTF-8" standalone="no"?><metadata>
    <idinfo>
        <citation>
            <citeinfo>
                <origin>Jones &amp; Stokes</origin>
                <pubdate>Novemb06</pubdate>
                <title>land_cover_update</title>
                <edition>First</edition>
                <geoform Sync="TRUE">vector digital data</geoform>
                <onlink>withheld</onlink>
                <ftname Sync="TRUE">land_cover_update_20120305_Current</ftname>
            </citeinfo>
        </citation>
        <descript>
            <abstract>May 14, 2013These data were downloaded by Greg Bazhaw from ICF Website. According to Terah Donovan, these data are a repost of the same data updated and redistributed on March 8, 2013.=========================================================================Land Cover in the Santa Clara Valley HCP/NCCP study area. There is a domain in the geodatabase to map from the numerical code to a land cover type. Exported data will often show the domain number, not the actual land cover type. **The domain values are NOT the same as the Land Cover Code** 10/15/2008 - Field Land_Cover_Name added. This field contains the full land cover type for each polygon. You can use this field instead of veg_type for any analysis/symbology for the land cover.The lookup table for the veg_types table was joined to the dataset. This field was then calculated with the text values of the land cover type.Updated 3/5/2012 - Data was updated with new serpentine grassland and land cover mapping from the Young Ranch project. </abstract>
            <purpose>Land-Cover Mapping
One of the primary data sources for this Plan is a detailed GIS-based map of land-cover types within the study area.  A land-cover type is defined as the dominant character of the land surface discernible from aerial photographs, as determined by vegetation, water, or human uses.  Land-cover types are the most widely used units in analyzing ecosystem function, habitat diversity, covered natural communities, wetlands and streams, and covered species habitat.  Data sources, mapping standards, and the classification and interpretation of land-cover types are discussed below.
Section 3.3.2 of the HCP/NCCP Admin Draft:   
3.1.1 Methods
Data Collection
Sources used to map and describe the physical setting of the study area are listed below. 
n U.S. Geological Survey (USGS) data on topography and hydrology.
n Geologic maps of the area (California Department of Conservation 1990, U.S. Geological Survey 1994). 
n Geologic map, Santa Clara County, California.  California Division of Mines and Geology, scale 1:62,500 (Brabb and Dibblee 1974).
n Preliminary map of Santa Clara Valley serpentines (unpublished), scale 1:50,000 (Dibblee 1972, 1973, 1977).
n Preliminary geologic map of the Mt. Madonna quadrangle, Santa Clara and Santa Cruz Counties, California.  U.S. Geological Survey Open-File Report [OF-73-59], scale 1:24,000 (Dibblee 1973).
n Soil survey information (U.S. Soil Conservation Service 1977). 
n Other published information (Hickman 1993, Alt and Hyndman 2000, Santa Clara Valley Water District 2006). 
n Springs and rainfall data from USGS (Casil 1997).
n Watershed data from California Interagency Watershed Map, 1999. 
Topography, hydrology, and soil data were downloaded from agency websites and imported into ArcInfo, where files were clipped and converted into the projection for the study area.  
Land-Cover Mapping
One of the primary data sources for this Plan is a detailed GIS-based map of land-cover types within the study area.  A land-cover type is defined as the dominant character of the land surface discernible from aerial photographs, as determined by vegetation, water, or human uses.  Land-cover types are the most widely used units in analyzing ecosystem function, habitat diversity, covered natural communities, wetlands and streams, and covered species habitat.  Data sources, mapping standards, and the classification and interpretation of land-cover types are discussed below.
Data Sources
The following are the primary sources of information for the land-cover mapping in the study area.
n True-color aerial photographs (resolution of 2 feet ) flown in December 2003 (acquired from AirPhoto USA). 
n True-color aerial photographs for non-urban portion of the study area (resolution of 9 inches) flown in March 2001(provided by Santa Clara Water District).
n Serpentine soils and serpentine geology digitized from the map sources listed above.
The ancillary data sources listed below were used to obtain information not available in the primary sources and to check the mapped information for accuracy.
n True-color aerial photographs (resolution 1.5 foot) flown in December 2005 (acquired from AirPhoto USA) .
n National Wetlands Inventory Maps (scale 1:65,000) from the U.S. Fish and Wildlife Service for a portion of the study area based on color-infrared photographs taken in 1982-1987.
n Streams (USGS digital line graph data-various dates). 
n Local roads (Santa Clara County data set).
n Coyote Valley Specific Plan vegetation data (City of San Jos 2004).
n Soil survey mapping (U.S. Soil Conservation Service 1977).
n Historical locations of valley oak, GIS layer digitized from the 1:62,500 Wieslander Vegetation Type Map, a dataset of photos, species inventories, and plot maps compiled in the 1920s and 1930s (California Department of Forestry and Fire Protection year?).
n Vegetation maps of open space preserves adjacent to the western portion of the study area (Midpeninsula Regional Open Space District 2006). 
n Vegetation map of the Coyote Creek Parkway County Park (Santa Clara County Parks and Recreation Department 2004).
n Land-cover map for the San Francisco Public Utilities Commission's Alameda Watershed lands in Santa Clara and Alameda Counties, adjacent to the northern edge of the study area (Jones &amp; Stokes 2005).
n Historical tideline data from Coyote Creek Historic Ecology Report (Grosslinger et al, 2006).
In addition to using existing data sets, Jones &amp; Stokes biologists conducted extensive field visits in the study area.  An initial field visit was conducted on December 15, 2005 to develop the land-cover classification and to perform preliminary verification of aerial photograph signatures.  Other field visits were conducted on April 20-21, May 3-5, May 11-12, and May 24-25, 2006 to verify land-cover types and consistency of mapping, and to collect additional data for land-cover type descriptions.  Initial mapping was verified by visual inspection from locations accessible by public roads and roads on state-owned and private lands for which access permission had been obtained.  Areas were selected for field verification on the basis of the land-cover types present and accessibility.  
Access was difficult in many parts of the study area due to extensive private lands and few public roads.  Access in the western portion of the study area was sufficient to verify the different vegetation types that occurred there.  Access in the central eastern portion of the study area was more limited, but also allowed most vegetation types to be visited.  Access to the extreme northeast, east, and area south of SR 152 in the eastern portion of the study area was not possible.  Once field visits were conducted, land-cover mapping was revised on the basis of field findings.
Land-Cover Type Classification 
A classification system for land-cover types (Tables 3-1 and 3-3) was developed for the study area based primarily on the widely used classification system of the CDFG (California Department of Fish and Game 2003), which in turn is based on the vegetation classification system developed for the Manual of California Vegetation (Sawyer and Keeler-Wolf 1995).  Additional input was obtained from the sources listed below. 
n Holland (1986) and Mayer and Laudenslayer (1988, 1999). 
n Current regional and local mapping projects such as Coyote Ridge (California Native Plant Society 2003), Sierra Azul Open Space Preserve (Midpeninsula Regional Open Space District 2006), and the land-cover map for the San Francisco Public Utilities Commission's Alameda Watershed lands in Santa Clara and Alameda Counties, adjacent to the study area (Jones &amp; Stokes 2005).
n Field visits by Jones &amp; Stokes senior biologists.  
The proposed system has been adapted to incorporate classification systems used by the Local Partners with input from vegetation and wildlife specialists familiar with the study area.  The land-cover classification was developed with the criteria listed below.
n Each land-cover type must be distinguishable on the digital aerial photography based on a unique and consistent signature, or with the use of ancillary data such as soil types or geologic substrate.
n Each land-cover type should be useful to the Plan in terms of defining the location and extent of an important vegetation type, habitat for covered species, or a distinct type of development.  
n The land-cover type classification should be compatible with existing local, regional, and national land-cover classification schemes when possible.
A list of land-cover types is given in Table 3-1.  An accuracy assessment for urban and agricultural land-cover types is provided in Table 3-2.  A comparison ("cross-walk") between land-cover types and common vegetation classification systems is presented in Table 3-3.
Mapping Procedures
ArcGIS 9.0 software was used to create a GIS dataset of land-cover types.  The land-cover classification also defined the minimum mapping unit that was used for each land-cover type.  Minimum mapping units are the smallest area mapped for each type.  Minimum mapping units range from 0.25 acre for wetland and riparian land-cover types to 10 acres for most other land-cover types.  This range of minimum mapping units is sufficient for regional conservation planning and balances the need for high resolution (lower minimum mapping unit) with schedule and budget limitations (higher minimum mapping unit).  Minimum mapping units are also limited by the resolution of the imagery and the distinctiveness of the land-cover signature relative to adjacent land cover.
A 10-acre minimum mapping unit was used for all land-cover types, except for the land-cover types noted below.
n Serpentine bunchgrass grassland and mixed serpentine chaparral, which were mapped at a 1-acre minimum mapping unit.
n All riparian, wetland, and aquatic types, which were mapped at a 0.25-acre minimum mapping unit.
n Serpentine seeps and rock outcrops, which had no minimum mapping unit. 
The mapping process involved digitizing polygons on screen (a process known as "head-up digitizing") from the primary aerial photographs described above, followed by field verification and a formal accuracy assessment. 
Polygons were digitized for areas with distinct image signatures (Table 3-4) that met minimum mapping unit requirements.  Digitizing was completed on-screen by botanists familiar with the study area, and well trained and experienced with this mapping procedure from other HCPs and NCCPs in northern California.  Digitizing was conducted while viewing the aerial imagery at mapping scales of 1:4,800 to 1:6,000.  The botanists were provided with grids of 0.25 acre and 10 acres to assist in maintaining the minimum mapping units during digitization.  Once digitized, polygons were assigned to land-cover types on the basis of the criteria in the land-cover type definitions (Table 3-4).
During the mapping process, polygons with uncertain land-cover types were flagged for future field verification.  Once the mapping was complete, the botanists verified these ambiguous polygons in the field where access was available.  
Serpentine bunchgrass grassland and serpentine chaparral were mapped based on the intersection of annual grassland and chaparral, respectively, with the serpentine soils layer, and verified in the field where possible.  Boundaries of aquatic features (ponds, reservoirs) were digitized based on the March 2001 photograph when water levels were higher than in the December 2003 image.  Recent urban and agricultural development was updated based on the December 2005 aerial photography.  
Ancillary information was used to supplement the land-cover information acquired by aerial photograph interpretation.  National Wetlands Inventory maps were used to check the wetlands mapping, especially for isolated ponds.  USGS data (2001) were used to complete the stream coverage for most of the area.  Mapped signatures for specific land-cover types were also compared with vegetation maps of the Sierra Azul Open Space Preserve (Midpeninsula Regional Open Space District 2006) to verify the accuracy of the current mapping effort.  
Accuracy Assessment
A field accuracy assessment was performed to quantify the reliability of the mapping of urban and agricultural land-cover type.  (A formal accuracy could not be conducted for all land-cover types due to the inaccessibility of large areas of the study area.)  For land-cover types with fewer than 30 polygons, all accessible polygons were field verified.  For land-cover types with more than 30 polygons, a random sample of 30-40 polygons was selected and verified if accessible.  A total of 306 polygons were field verified during this accuracy assessment.  A polygon was classified in one of three ways.  The first classification was "no change", meaning the polygon was mapped correctly.  The second classification was "error", indicating a misinterpretation from the aerial imagery.  The third classification was "change," indicating a land use change that occurred after the aerial photographs were taken.  The resulting map accuracy was 73% when calculated by number of polygons.  The map accuracy was 89% when calculated by polygon area (31,258 acres were checked) .
Table 3-2a indicates the accuracy of the land-cover mapping by polygon.  Table 3-2b indicates mapping accuracy by acreage of land-cover type.</purpose>
            <supplinf>
Entitlement Parcels were included as being developed in this land cover layer, as the projects on them were planned and approved before the start date of the HCP.  Actual level of development might vary by parcel.  Updated on July 28, 2008.

Fields:

veg_type "Land Cover":  This field lists the land cover type of each polygon.  There is a domain associated with this field.  Not all values in the domain were mapped.

Comment:  Comments about the polygon

natural_comm "Natural Communities":  Natural Community Classification of the land cover type. There are nine different values in all.

natural_comm_code "Natural Community Code":  A code field for the natural communities.  Each value represents a natural community.

land_cover_code:  A classification scheme based on the predominant table format for listing the land covers.  The first number is the natural community code, while the second represents the order that the land cover types are listed in the tables.  Also used for the tables in impact analysis.

Domain Value;  	Land Cover; 				Land Cover Code
01	California Annual Grassland				10
02	Northern Mixed Chaparral / Chamise Chaparral		20
03	Northern Coastal Scrub / Diablan Sage ScrUB		22
04	Mixed Serpentine Chaparral				21
05	Canyon Live Oak Forest &amp; Woodland			X
06	Mixed Oak Woodland and Forest			31
07	Mixed Evergreen Forest				35
08	Blue Oak-Foothill Pine / Grass				X
09	Blue Oak Woodland				32
10	Foothill Pine - Oak Woodland				34
11	Valley Oak Woodland				30
12	Redwood Forest					50
13	Ponderosa Pine Woodland				51
14	Cottonwood Riparian				X
15	Willow Riparian Forest and Scrub			40
16	Mixed Riparian Forest and Woodland			42
17	White Alder Forests and Woodland			X
18	Coast Live Oak Forest and Woodland			33
19	Exotic Riparian Woodland				X
20	Himalayan Blackberry Scrub				X
21	Giant Reed (Arundo)				X
22	Meadow and Seeps - Baltic Rush Riparian Grassland	X
23	Coastal and Valley Freshwater Marsh			60
24	Coastal Brackish Marsh				X
25	Natural Lake					X
26	Pond						65
27	Reservoir						66
28	Riverine						X
29	Canal / Ditch					X
30	Coyote Brush Scrub					23
31	Orchard						70
32	Vineyard						71
33	"Grain, Row-crop, Hay &amp; Pasture, Disked/short-term fallow"	72
34	Eucalyptus					X
35	Ornamental Woodland				83
36	Agriculture developed / Covered Ag			85
37	Seasonal Wetland					61
38	Vernal Pool Complex				X
39	Serpentine Seep					62
40	Serpentine Bunchgrass Grassland			15
41	Serpentine Rock Outcrop / Barrens			16
42	Rock Outcrop					17
43	Urban - Suburban					80
44	Rural - Residential					81
45	Barren						86
46	Landfill						84
47	Golf Courses / Urban Parks				82
48	Ruderal						X
49	Purple Needlegrass Grassland (not mapped)		X
50	Knobcone Pine Forest				52
51	Central California Sycamore Alluvial Woodland		41

Natural Communites

1.  Grasslands
2.  Chaoarral &amp; Northern Coastal Scrub
3.  Oak Woodland
4.  Riparian Forest and Scrub
5.  Conifer Woodland
6.  Wetland
7.  Open Water (Aquatic)
8.  Irrigated Agriculture
9.  Developed
</supplinf>
            <langdata Sync="TRUE">en</langdata>
        </descript>
        <timeperd>
            <timeinfo>
                <sngdate>
                    <caldate>Novemb06</caldate>
                    <time>unknown</time>
                </sngdate>
            </timeinfo>
            <current>publication date</current>
        </timeperd>
        <status>
            <progress>Complete</progress>
            <update>None planned</update>
        </status>
        <spdom>
            <bounding>
                <westbc Sync="TRUE">-122.038760</westbc>
                <eastbc Sync="TRUE">-121.206828</eastbc>
                <northbc Sync="TRUE">37.490409</northbc>
                <southbc Sync="TRUE">36.888398</southbc>
            </bounding>
            <lboundng>
                <leftbc Sync="TRUE">6115200.873879</leftbc>
                <rightbc Sync="TRUE">6354963.501174</rightbc>
                <bottombc Sync="TRUE">1785480.541345</bottombc>
                <topbc Sync="TRUE">2001820.374379</topbc>
            </lboundng>
        </spdom>
        <keywords>
            <theme>
                <themekt>ESRI Geography Network Thesaurus</themekt>
                <themekey>None</themekey>
            </theme>
            <place>
                <placekt>None</placekt>
            </place>
        </keywords>
        <accconst>This data may not be redistributed without the consent of the participating partners in the Santa Clara Valley Habitat Conservation Plan/Natural Community Conservation Plan.  The partners are:  Santa Clara County, the Cities of San Jose, Morgan Hill, and Gilroy, Santa Clara Valley Water District, and the Santa Clara Valley Transportation Authority.</accconst>
        <useconst>This dataset was created/compiled by ICF Jones &amp; Stokes for useage for the Santa Clara Valley HCP/NCCP only.  Every reasonable effort has been made to ensure the accuracy of the provided data.  Neither ICF Jones &amp; Stokes and the Santa Clara Valley HCP/NCCP partners assume any liability arising from the usage of this data.  THE DATA IS PROVIDED AS IS WITHOUT ANY KIND OF WARRANTY, either expressed or implied, including, but not limited to, the implied warranties of merchantability and fitness for a particular purpose.  This data should be used for planning purposes only.</useconst>
        <ptcontac>
            <cntinfo>
                <cntperp>
                    <cntorg>Jones &amp; Stokes</cntorg>
                </cntperp>
                <cntaddr>
                    <addrtype>mailing</addrtype>
                    <address>268 Grand Ave</address>
                    <city>Oakland</city>
                    <state>CA</state>
                    <postal>94610</postal>
                    <country>USA</country>
                </cntaddr>
                <cntvoice>510-433-8962</cntvoice>
                <cntemail>dzippin@jsanet.com</cntemail>
                <hours>8:00 AM to 5:00 PM</hours>
                <cntinst>
Best Contacts:
Margaret Widdowson
Steve Citron-Pousty
Daniel Schiff
</cntinst>
            </cntinfo>
        </ptcontac>
        <datacred>ICF Jones &amp; Stokes, 2008</datacred>
        <native Sync="FALSE">ESRI ArcCatalog 9.3.1.4000</native>
        <natvform Sync="TRUE">Personal GeoDatabase Feature Class</natvform>
    </idinfo>
    <dataqual>
        <logic>ESRI feature type: Simple, Geometry: Polygon, Topology: </logic>
        <complete>Data set has been visually inspected.  All data produced strives to meet National Mapping Accuracy Standards (NMAS).</complete>
        <lineage>
            <procstep>
                <procdesc>Metadata imported.</procdesc>
                <srcused>withheld</srcused>
            </procstep>
            <procstep>
                <procdesc Sync="TRUE">Metadata imported.</procdesc>
                <srcused Sync="FALSE">withheld</srcused>
                <procdate Sync="TRUE">20090708</procdate>
                <proctime Sync="TRUE">09153400</proctime>
            </procstep>
        </lineage>
    </dataqual>
    <spdoinfo>
        <direct Sync="TRUE">Vector</direct>
        <ptvctinf>
            <esriterm Name="LandCover">
                <efeatyp Sync="TRUE">Simple</efeatyp>
                <efeageom Sync="TRUE" code="4"/>
                <esritopo Sync="TRUE">FALSE</esritopo>
                <efeacnt Sync="TRUE">7950</efeacnt>
                <spindex Sync="TRUE">TRUE</spindex>
                <linrefer Sync="TRUE">FALSE</linrefer>
            </esriterm>
        </ptvctinf>
    </spdoinfo>
    <spref>
        <horizsys>
            <planar>
                <planci>
                    <plance Sync="TRUE">coordinate pair</plance>
                    <coordrep>
                        <absres Sync="TRUE">0.000256</absres>
                        <ordres Sync="TRUE">0.000256</ordres>
                    </coordrep>
                    <plandu Sync="TRUE">survey feet</plandu>
                </planci>
            </planar>
            <geodetic>
                <horizdn Sync="TRUE">North American Datum of 1983</horizdn>
                <ellips Sync="TRUE">Geodetic Reference System 80</ellips>
                <semiaxis Sync="TRUE">6378137.000000</semiaxis>
                <denflat Sync="TRUE">298.257222</denflat>
            </geodetic>
            <cordsysn>
                <geogcsn Sync="TRUE">GCS_North_American_1983</geogcsn>
                <projcsn Sync="TRUE">NAD_1983_StatePlane_California_III_FIPS_0403_Feet</projcsn>
            </cordsysn>
        </horizsys>
        <vertdef>
            <altsys>
                <altres Sync="TRUE">0.000010</altres>
                <altenc Sync="TRUE">Explicit elevation coordinate included with horizontal coordinates</altenc>
            </altsys>
        </vertdef>
    </spref>
    <eainfo>
        <detailed Name="LandCover">
            <enttyp>
                <enttypl Sync="TRUE">LandCover</enttypl>
                <enttypt Sync="TRUE">Feature Class</enttypt>
                <enttypc Sync="TRUE">7950</enttypc>
            </enttyp>
            <attr>
                <attrlabl>OBJECTID</attrlabl>
                <attrdef>Internal feature number.</attrdef>
                <attrdefs>ESRI</attrdefs>
                <attrdomv>
                    <udom>Sequential unique whole numbers that are automatically generated.</udom>
                </attrdomv>
                <attalias Sync="TRUE">OBJECTID</attalias>
                <attrtype Sync="TRUE">OID</attrtype>
                <attwidth Sync="TRUE">4</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
            <attr>
                <attrlabl>SHAPE</attrlabl>
                <attrdef>Feature geometry.</attrdef>
                <attrdefs>ESRI</attrdefs>
                <attrdomv>
                    <udom>Coordinates defining the features.</udom>
                </attrdomv>
                <attalias Sync="TRUE">land_cover_code</attalias>
                <attrtype Sync="TRUE">SmallInteger</attrtype>
                <attwidth Sync="TRUE">2</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
            <attr>
                <attrlabl>SHAPE_Length</attrlabl>
                <attrdef>Natural community that the land cover belongs in</attrdef>
                <attrdefs>ESRI</attrdefs>
                <attrdomv>
                    <udom>Positive real numbers that are automatically generated.</udom>
                </attrdomv>
                <attalias Sync="TRUE">land_cover_name</attalias>
                <attrtype Sync="TRUE">String</attrtype>
                <attwidth Sync="TRUE">90</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
            <attr>
                <attrlabl>land_cover_code</attrlabl>
                <attrdef>Code used for landcover in Figure 3-10</attrdef>
                <attrdefs>ESRI</attrdefs>
                <attrdomv>
                    <udom>Positive real numbers that are automatically generated.</udom>
                </attrdomv>
                <attalias Sync="TRUE">Natural Communties</attalias>
                <attrtype Sync="TRUE">String</attrtype>
                <attwidth Sync="TRUE">50</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
            <attr>
                <attrlabl>Shape_Length</attrlabl>
                <attrdef>Code for ordering the natural communities in analysis tables</attrdef>
                <attrdefs>ESRI</attrdefs>
                <attrdomv>
                    <udom>Positive real numbers that are automatically generated.</udom>
                </attrdomv>
                <attalias Sync="TRUE">veg_type</attalias>
                <attrtype Sync="TRUE">SmallInteger</attrtype>
                <attwidth Sync="TRUE">2</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
            <attr>
                <attrlabl>SHAPE_Area</attrlabl>
                <attrdef>GIS acres</attrdef>
                <attrdefs>ESRI</attrdefs>
                <attrdomv>
                    <udom>Positive real numbers that are automatically generated.</udom>
                </attrdomv>
                <attalias Sync="TRUE">SHAPE</attalias>
                <attrtype Sync="TRUE">Geometry</attrtype>
                <attwidth Sync="TRUE">0</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
            <attr>
                <attrlabl>natural_comm</attrlabl>
                <attalias Sync="TRUE">SHAPE_Area</attalias>
                <attrtype Sync="TRUE">Double</attrtype>
                <attwidth Sync="TRUE">8</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
                <attrdefs Sync="TRUE">ESRI</attrdefs>
                <attrdomv>
                    <udom Sync="TRUE">Positive real numbers that are automatically generated.</udom>
                </attrdomv>
                <attrdef Sync="TRUE">Feature geometry.</attrdef>
            </attr>
            <attr>
                <attrlabl Sync="TRUE">Documentation</attrlabl>
                <attalias Sync="TRUE">Area_Acres</attalias>
                <attrtype Sync="TRUE">Double</attrtype>
                <attwidth Sync="TRUE">8</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
            <attr>
                <attrlabl>Shape</attrlabl>
                <attrdef>Code used for ordering land cover in analysis results tables</attrdef>
                <attrdefs>ESRI</attrdefs>
                <attrdomv>
                    <udom>Coordinates defining the features.</udom>
                </attrdomv>
                <attalias Sync="TRUE">Natural Community Code</attalias>
                <attrtype Sync="TRUE">SmallInteger</attrtype>
                <attwidth Sync="TRUE">2</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
            <attr>
                <attrlabl>Shape_Area</attrlabl>
                <attrdef>Area of feature in internal units squared.</attrdef>
                <attrdefs>ESRI</attrdefs>
                <attrdomv>
                    <udom>Positive real numbers that are automatically generated.</udom>
                </attrdomv>
                <attalias Sync="TRUE">SHAPE_Length</attalias>
                <attrtype Sync="TRUE">Double</attrtype>
                <attwidth Sync="TRUE">8</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
            <attr>
                <attrlabl>natural_comm_code</attrlabl>
                <attrdef>The land cover type of the polgyon</attrdef>
                <attrdefs>ESRI</attrdefs>
                <attrdomv>
                    <udom>Positive real numbers that are automatically generated.</udom>
                </attrdomv>
                <attalias Sync="TRUE">Documentation</attalias>
                <attrtype Sync="TRUE">String</attrtype>
                <attwidth Sync="TRUE">150</attwidth>
                <atprecis Sync="TRUE">0</atprecis>
                <attscale Sync="TRUE">0</attscale>
            </attr>
        </detailed>
    </eainfo>
    <distinfo>
        <distrib>
            <cntinfo>
                <cntaddr>
                    <addrtype>mailing</addrtype>
                    <address>268 Grand Ave</address>
                    <city>Oakland</city>
                    <state>CA</state>
                    <postal>94610</postal>
                    <country>USA</country>
                </cntaddr>
                <cntvoice>510-433-8962</cntvoice>
                <cntemail>dzippin@jsanet.com</cntemail>
                <hours>8:00 AM to 5:00 PM</hours>
            </cntinfo>
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        <resdesc>Downloadable Data</resdesc>
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        <idAbs>&lt;DIV STYLE="text-align:Left;"&gt;&lt;DIV&gt;&lt;DIV&gt;&lt;P&gt;&lt;SPAN&gt;November 14, 2014 by Greg Bazhaw&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;After several IC Subcommittee meetings discussing GIS Layers and Geobrowser issues over the course of September 12, 13 and October 14, 22, 2014, reverted the value back in the field "land_cover_name" as follows:&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;Serpenting Rock Outcrop reverted back to Serpentine Rock Outcrop / Barrens&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;At these meetings were Greg Bazhaw, Kim Rook, Rob Eastwood (County Planning), Kathryn Gaffney, Dan Schiff (ICF), Don Arnold, Janell Hillman (SCVWD) and John Falkowski (County Parks).&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;=========================================================&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;September 6, 2013 by Greg Bazhaw&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;Several inconsistencies for some of the values in the field "land_cover_name" were updated to reflect the actual language in Table 3-1 of The Plan. These values are:&lt;/SPAN&gt;&lt;/P&gt;&lt;P STYLE="text-indent:20;margin:1 1 1 20;"&gt;&lt;SPAN&gt;Original Data Value &lt;/SPAN&gt;&lt;SPAN&gt;Updated values&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;Serpentine Rock Outcrop/Barrens Serpentine Rock Outcrop&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;Knobcone Pine Forest Knobcone Pine Woodland&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;Agriculture Developed / Covered Ag Agriculture Developed&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;Grain, Row-crop, hay &amp;amp; pasture, disked/ short-te Grain, Row-Crop, Hay and Pasture, Disked / Short-Term Fallowed&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN /&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;Also, a new field was added called "Documentation" and popoulated with the path to source documentation relating to the layer&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;=========================================================&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;May 14, 2013 by Greg Bazhaw&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;These data are a copy of the original ICF land cover data (land_cover_scvhcp, renamed to land_cover) downloaded on this day (updated and redistributed on March 8, 2013). The data were processed in the following manner:&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;1. Topology was created and two rules applied: (a) features must not overlap, and (b) features must not have gaps. After validation, no errors were found.&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;2. For each veg_type code, applied the tool Explode Multipart Feature from the Advanced Editing Toolbox. Compared the results to Table 3-7, which were very different, both in numbers of polygons and Acres for each Vegetation Type. &lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;3. Added a field called Area_Acres and calculaged geometry in acres.&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;4. Revalidated topology and found no errors.&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;======================================================&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;May 14, 2013 by Greg Bazhaw&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;These data were downloaded by Greg Bazhaw from ICF Website. According to Terah Donovan, these data are a repost of the same data updated and redistributed on March 8, 2013.&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;=========================================================================&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;Land Cover in the Santa Clara Valley HCP/NCCP study area. There is a domain in the geodatabase to map from the numerical code to a land cover type. Exported data will often show the domain number, not the actual land cover type. **The domain values are NOT the same as the Land Cover Code** 10/15/2008 - Field Land_Cover_Name added. This field contains the full land cover type for each polygon. You can use this field instead of veg_type for any analysis/symbology for the land cover.The lookup table for the veg_types table was joined to the dataset. This field was then calculated with the text values of the land cover type.&lt;/SPAN&gt;&lt;/P&gt;&lt;P&gt;&lt;SPAN&gt;Updated 3/5/2012 - Data was updated with new serpentine grassland and land cover mapping from the Young Ranch project. &lt;/SPAN&gt;&lt;/P&gt;&lt;/DIV&gt;&lt;/DIV&gt;&lt;/DIV&gt;</idAbs>
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