rr_av_42.shp: Alexander Valley Reach, 1942
rr_av_93.shp: Alexander Valley Reach, 1990
rr_me_40.shp: Mendocino County Reach, 1940
rr_me_92.shp: Mendocino County Reach, 1990
rr_mr_42.shp: Middle Reach, 1942
rr_mr_93.shp: Middle Reach, 1990
Each of the .shp files listed above is intended to be linked
to a .dbf using the 'ACADTEXT' attribute column. The .dbf files
were created as a part of the original Enhancement Plan, not the
Russian River Watershed GIS. An explanation of the database files
is included in the supplemental section below. A brief sysnopsis
of how to utilize these tables with the .shp files is:
hab1_90.dbf - Link this file with rr_me_92.shp for landuse/landcover
information.
hab2_42.dbf - Link this file with rr_av_40.shp for landuse/landcover
information.
hab2_90.dbf - Link this file with rr_av_93.shp for landuse/landcover
information.
hab3_42.dbf - Link this file with rr_mr_42.shp for landuse/landcover
information.
hab3_90.dbf - Link this file with rr_mr_93.shp for landuse/landcover
information.
rip1_90.dbf - Link this file with rr_me_92.shp for riparian habitat
successional status information.
rip2_90.dbf - Link this file with rr_av_93.shp for riparian habitat
successional status information.
rip3_90.dbf - Link this file with rr_mr_93.shp for riparian habitat
successional status information.
The database filenames for each study area consist of abbreviations referring to the type of data, the first digit of the study area code, the year of aerial photography or field work completion; and a filename extension designating the file format. For example, Hab3_90.dbf is the name of the file containing habitat data for Study Area 300000 (Middle Reach), based on 1990 aerial photos, and stored in dbf file format.
I. INTRODUCTION:
The purpose of this data dictionary is to document the contents of the GIS attribute databases that were developed for the Russian River Resource Enhancement Plan, including information on GIS data set file names, item names in each database file, item definitions, data sources, and codes. Since a data dictionary must change and grow along with the database itself, the code changes that are inevitable in any on-going project have also been recorded here.
The project's three study areas (Mendocino Study Area, Alexander Valley Study Area, and Middle Reach Study Area) were assigned codes of 100000, 200000, and 300000, respectively. Two attribute databases (Land Use and Habitat, Riparian Vegetation and Gravel Bar) were developed for each study area. These attribute databases were originally created in Lotus 1-2-3 spreadsheet format, then translated into dBase III+ format ("dbf" filename extension) for use with the ArcCAD GIS program.
The database filenames for each study area consist of abbreviations referring to the type of data, the first digit of the study area code, the year of aerial photography; and a filename extension designating the file format. For example, Hab3_42.dbf is the name of the file containing habitat data for Study Area 300000 (Middle Reach), based on 1942 aerial photos, and stored in dbf file format.
Each individual map polygon or sub-polygon in the database was assigned a composite ID number derived by summing up the values of the codes for Decade, Study Area, Zone, Bank, Polygon, and Sub-Polygon, as given below. For example, the ID number 9358159.1 designates a specific 1990-decade Middle Reach polygon in the Channel Zone on the Right-hand side, with Polygon Number 159 and Sub-Polygon Number 0.1.
DECADE
Code 4000000 = data was obtained from1940s aerial photos
Code 9000000 = data was obtained from1990s aerial photos (actually
1988 in the case of the Mendocino Reach study area)
STUDY_AREA
Code 100000 = Mendocino Reach
Code 200000 = Alexander Valley Reach
Code 300000 = Middle Reach
ZONE
Code 50000 = Zone "C": The river channel and all areas
covered by riparian vegetation along the Russian River's "main
stem", including the wetted channel, active channel, vegetated
channel, channel banks, and that portion of the floodplain between
the top of the channel bank and the outer limit of "typical"
riparian vegetation. This zone supports various seral stages of
riparian vegetation, and it is assumed to be subject to relatively
frequent flooding wherever there are no artificial flood control
structures.
Code 60000 = Zone "U": Upper or "historical" floodplain terraces along the main stem; i.e., all lowland areas between the outer limit of the main stem riparian vegetation and the study area boundaries, including the channels, riparian areas, and floodplains of tributary creeks. The relatively level terrace areas are nevertheless high enough that they are assumed to be only rarely subject to flooding by the river (as mapped in the present study this zone may include some small areas that are actually within the river's active floodplains and some other small areas that are actually above the historical flood elevations).
Code 70000 = Zone "K": Uplands within the study area boundaries that are higher than the general level of the upper floodplain terraces along the main stem or its major tributaries, and which are separated from the floodplains by a distinct break in slope. It is assumed for the purposes of the present study that these upland areas are never subject to flooding by streamwaters.
BANK
Code 7000 = Mid-Channel
Code 8000 = Right Bank (facing downstream).
Code 9000 = Left Bank (facing downstream).
POLYGON
The identification code for an individual polygon is a whole number
having from one to three digits within the range 1 to 999, inclusive.
These numbers are unique within the same bank and zone, but are
not necessarily unique among different zones.
SUB_POLYGON
Some polygons have been divided by a river mile marker into two
or more parts. The sub-units of such a polygon are designated
by decimal numbers.
Note: On the field sheets the sub-polygons were originally designated by lower-case letters. In the present decimal-number system, sub-polygon 0.1 corresponds to the former sub-polygon a, sub-polygon 0.2 to the former sub-polygon b, etc.
A "missing data" code of either "xxxx" (for text fields) or "9999" (for numerical fields) was assigned when data for a given map polygon was unavailable, in order to differentiate such cases from legitimate "blank" fields in the database.
II. RIPARIAN VEGETATION AND GRAVEL BAR DATABASES
dBASE III+ filenames: RIP1_90.dbf, RIP2_90.dbf, RIP3_90.dbf
Item (1). Item Name: ACAD_TEXT\Field Width: 14\Data Type: Number
A numerical field containing the unique user-assigned identification
number for each map polygon (it was called ACAD_TEXT for reasons
having to do with the ArcCAD GIS program). This item serves as
the principal "key" for sorting database records and
relating them to the map polygons. Due to additions and deletions
of polygons during the map editing process, these ID numbers were
not necessarily sequential.
Item (2). Item Name: R_MILE\Field Width: 7\Data Type: Number
The upstream "river mile" closest to the location of
a polygon.
Item (3). Item Name: AREA_HA\Field Width: 12\Data Type: Number
The area of a given polygon in hectares. Area_Ha is the result
of multiplying the area in square meters (as calculated by the
GIS) by a conversion factor of 0.0001.
Item (4). Item Name: AREA_AC\Field Width: 12\Data Type: Number
The area of a given polygon in acres. Area_Ac is the result of
multiplying the area in square meters (as calculated by the GIS)
by a conversion factor of 0.000247.
Item (5). Item Name: N_SIZE_CL\Field Width: 10\Data Type: Number
A rough visual estimate of tree diameter at breast height (inches)
for "... the stand's main, largest trees, excluding the occasional
tree of exceptional size" (Northen 1991). Used for tree-dominated
and mixed vegetation types only; not used for polygons with <
10% cover. Codes and size class categories for dbh follow Northen's
classification system (Northen 1991; 1992):
Code 1 = Seedlings: <1" dbh
Code 2 = Saplings: 1"-6" dbh
Code 3 = Small: 7"-11" dbh
Code 4 = Medium: 12"-24" dbh
Code 5 = Large: >24" dbh
Note: Although Northen's dbh class names are different from those used in the WHR system, his categories nevertheless correspond exactly to the first five WHR size classes (i.e., seedling, sapling, pole tree, small tree, medium/large tree).
Item (6). Item Name: AV_HEIGHT\Field Width: 9\Data Type: Number
A rough visual estimate of the height class (in feet) of the average
overstory trees (i.e., dominants and co-dominants) within the
polygon. Used for tree-dominated and mixed vegetation types only;
not used for polygons with <10% cover. Codes for height categories
were assigned according to the following scheme:
Code 1 = <3'
Code 2 = 3'-15'
Code 3 = 16'-30'
Code 4 = 31'-65'
Code 5 = 66'-115'
Code 6 = >115'
Item (7). Item Name: N_COVER\Field Width: 9\Data Type: Character
A rough visual estimate of the percentage of ground surface within
the entire polygon covered by vegetation of any type. Codes and
categories for cover followed Northen's terminology (Northen 1991;
1992):
Code u = "unvegetated" (<10% cover)
Code s = "sparsely vegetated" (11% - 50% cover)
Code c = "well vegetated" (> 50% cover)
Item (8). Item Name: N_VEGTYPE\Field Width: 10\Data Type: Character
A rough visual estimate of the predominant "vegetation type"
(i.e., plant life form) within the polygon. Codes and categories
for vegetation type follow Northen's classification system (Northen
1991; 1992):
Code f = Forbs, Grasses, and/or "Shrubs" (interpreted
here as woody plants 3'-15' tall)
Code r = Giant Reed (Arundo)
Code t = trees
Code m = mixed type (No obvious predominance of any one of
the above three vegetation types).
Item (9). Item Name: AV_DBH\Field Width: 10\Data Type: Character
A rough visual estimate (in inches) of the diameter class at breast
height for the "average" or "typical" size
of tree within the entire polygon. Used for tree-dominated and
mixed vegetation types only; not used for polygons with <10%
cover:
Code A = Seedling to Sapling size (<1"-6"; WHR codes
1 and 2)
Code B = Pole to Small size (7"-24"; WHR codes 3 and
4)
Code C = Medium to Large size (>24"; WHR code 5)
Note: On our field sheets the "Size" category originally contained dbh size class information according to the standard WHR definitions (Mayer and Laudenslayer 1988). We subsequently modified our classification by lumping the five WHR size classes into the above three categories, and changing the name of this item to Av_dbh. Av_dbh differs from Item 2 above (N_Size_Class) in that the latter refers only to the dbh of "the stand's largest trees" (Northen 1991; 1992).
Item (10). Item Name: N_SPPTYPE\Field Width: 12\Data Type: Character
A rough visual determination of the predominant tree species within
a polygon (i.e., any tree species having an estimated cover >50%).
Used for tree-dominated and mixed vegetation types only; not used
for polygons with <10% cover. If no single tree species constituted
more than 50% of a stand, the code "ms" was recorded
to indicate a mixture of tree species:
Cottonwood = (fc) = PF
White Alder = (wa) = AR
Sandbar Willow = (sw) = SH
Arroyo Willow = (aw) = SL
Red and/or Yellow Willow = (rw) = SS
Oregon Ash = (oa) = FR
Boxelder = (be) = AN
Black Walnut = (bw) = JH
Valley Oak = (vo) = QL
Coast Live Oak = (co) = QA
Bay = (ba) = UC
Note: The species codes shown in parentheses above are taken from Northen (1991; 1992). We originally used these codes on our fieldsheets, but they were later changed to upper-case letters matching the codes used in Items (13) and (14) below.
Item (11). Item Name: N_STATUS\Field Width: 8\Data Type: Number
A rough visual estimate of "successional status" based
on presence, size class, and abundance of late successional tree
species within a polygon. Categories for successional status follow
Northen's classification system (Northen 1991; 1992):
Code 0.1 = Vegetation either "absent" or largely so
(less than 10% cover) or "sparse" (less than or equal
to 50% cover).
Code 1 = Greater than 50% cover, late successional trees absent,
or present only as seedlings (= WHR seedling size) or an occasional
larger individual.
Code 2 = Greater than 50% cover, late successional trees present
in "evident numbers" and of WHR sapling size.
Code 3 = Greater than 50% cover, late successional trees present
in "evident numbers" and of "small" size (=
WHR pole size)
Code 4 = Greater than 50% cover, late successional trees present
in "evident numbers" and of "medium" size
(= WHR small size)
Code 5 = Greater than 50% cover, late successional trees present
in "evident numbers" and of "large" size (=
WHR med/large size)
Note: In his previous work in the riparian zone of the Russian River, Northen (1991; 1992) designated "... Hind's Black Walnut and Box Elder, and to a lesser extent Oregon Ash", as the late successional or "climax" species in this plant community. He noted that he "... did not include White Alder as such, even though it may be when adjacent to an old, stable channel".
Note: Northen did not specify what he meant by "evident numbers" in the above classification scheme; we interpreted it to mean "Individuals of late successional species abundant enough to be seen frequently without having to make a special search for them".
Note: The "sub-status" category originally appearing
on our field sheets was subsequently discarded.
Item (12). Item Name: N_BARTYPE\Field Width: 12\Data Type: Character
A rough visual estimate of the dominant particle size (i.e., gravel
or fines) on the surface of point bars or alternate bars; also
indicates the stage of geomorphological development of the bar,
based on the presence, size, and degree of coalescence of hummocks.
Codes and categories for bar type follow Northen's classification
system (Northen 1991; 1992):
Code lgr = Level or rounded cross-section; mainly gravel
Code lvf = Level or rounded cross-section; mainly fines
Code sh = Hummocks beginning to form (to 3' high)
Code mh = Hummocks medium size (to 6' high)
Code lh = Hummocks large size (>6' high)
Code ch = Hummocks large and coalescing into a terrace
Item (13). Item Name: OVERSTORY\Field Width: 36\Data Type: Character
A rough visual determination and listing of the commonest overstory
tree species within a polygon (i.e., the "dominants"
and co-dominants), chosen from the following species list (* indicates
"late successional" species). For sites lacking any
real "overstory", but containing scattered trees or
scrubby growth, the commonest woody species were listed:
Code, Tree Species, Common Name
AN, Acer negundo, Boxelder *
AC, Aesculus californica, Buckeye
AR, Alnus rhombifolia, White Alder
JH, Juglans californica *var. hindsii , Black Walnut
QA, Quercus agrifolia, Coast Live Oak
QL, Quercus lobata, Valley Oak
QD, Quercus dumosa, Calif. Scrub Oak
QK, Quercus kellogii, Calif. Black Oak
QW, Quercus wislizenii, Interior Live Oak
EU, Eucalyptus spp., Eucalyptus
FR, Fraxinus latifolia, Oregon Ash *
PF, Populus fremontii, Cottonwood
SM, Sambucus mexicana, Elderberry
UC, Umbellularia californica, California Bay
PM, Pseudotsuga menziesii, Douglas Fir
SS, Salix spp., mainly Red Willow (S. laevigata
and/or Yellow Willow (S. lucida ssp. lasiandra)
SH, Salix exigua, Sandbar Willow
SL, Salix lasiolepis, Arroyo Willow
Item (14). Item Name: UNDERSTORY\Field Width: 36\Data Type: Character
A rough visual determination and listing of the commonest understory
tree species within a polygon (if an understory was present),
chosen from the same species list and codes given in Item (13)
above.
Item (15). Item Name: VINES\Field Width: 21\Data Type: Character
A rough visual determination and listing of the commonest vine
species within a polygon, chosen from the same species list and
codes given in Item (16) below.
Item (16). Item Name: SHRUBS\Field Width: 36\Data Type: Character
A rough visual determination and listing of the commonest "shrub"
or large herbaceous species (i.e., plants 3'-15' tall) within
a polygon, chosen from the CRP species list and codes below (*
indicates non-native species):
Code, Shrub/Vine/Gd.Cover/Aquatic, Common Name:
RS, Rubus spp., Blackberry
BV, Baccharis salsifolia (=viminea),
Mulefat
BP, Baccharis pilularis, Coyotebush
TD, Toxicodendron diversiloba, Poison Oak
SY, Symphoricarpos spp., Snowberry
RC, Rosa californica, Wild Rose
AS, Arctostaphylos spp., Manzanita
CO, Calycanthus occidentalis, Spicebush
MU, Artemisia douglassii, Mugwort
VC, Vitis californica, Wild Grape
AA, Aristolochia californica, Dutch-man's Pipe
RP, Rubus procerus, Himalaya Berry *
AD, Arundo donax, Giant Reed *
CM Conium maculatum, Poison Hemlock *
BS, Brassica spp., Mustard *
VS, Vinca spp., Periwinkle *
CS, Centaurius solstitialis, Star Thistle *
ES, Eremocarpus setigerus, Dove Weed *
LS, Ludwigia spp., Water primrose *
FV, Foeniculum vulgare, Fennel *
RU, Juncus spp.; Cyperus spp., Rush
SE, Eleocaris spp.; Carex spp., Sedge
TS, Typha spp., Cattail
TU, Scirpus spp., Tule
U, Urtica spp., Nettle
Item (17). Item Name: GR_COVER\Field Width: 62\Data Type: Character
A rough visual estimate and listing of the commonest "ground
cover" species (i.e., plants <3' tall) within a polygon,
chosen from the same species list and codes given in Item (16)
above.
Item (18). Item Name: PC_GR_COV\Field Width: 10\Data Type: Number
A rough visual estimate of the per cent ground cover, using the
following four classes:
Code 1 = 0% - 25%
Code 2 = 26% - 50%
Code 3 = 51% - 75%
Code 4 = 76% - 100%
III. LAND USE AND HABITAT DATABASES
dBASE III+ filenames: HAB2_42.dbf, HAB3_42.dbf, HAB1_90.dbf, HAB2_90.dbf, HAB3_90.dbf
Item (1). Item Name: Acad_Text; Data Type: Number; Field Width:
14
The same item described in Section II above.
Item (2). Item Name: R_MILE\Field Width: 7\Data Type: Number
The same item described in Section II above.
Item (3). Item Name: AREA_HA\Field Width: 12\Data Type: Number
The same item described in Section II above.
Item (4). Item Name: AREA_AC\Field Width: 12\Data Type: Number
The same item described in Section II above.
Item (5). Item Name: LANDFORM\Field Width: 10\Data Type: Character
Zone "K": Uplands
Code H = Hill (as defined here, does not include riparian
vegetation and wetted channels of tributary streams that occur
in hilly areas)
Zone "U": Upper Terraces and Tributary Streams
Code S = Riparian Vegetation along tributary stream or artificial
drainage channel
Code W = Wetted Channel of tributary stream, or an artificial
drainage channel (only shown where large enough to be mapped as
a separate polygon)
Code T = Upper Terraces; i.e., relatively level lowland areas
between the edge of the mainstem riparian vegetation and the break
in slope which indicates the beginning of the uplands.
Note: Ground truth was not obtained for the tributary streams, hence these habitats were not subdivided further into bar types or vegetation types.
Zone "C": Main Stem River Channel
Code I = Immediate Bank: a narrow bank which makes an abrupt transition
between the wetted channel and the upper terrace, with no intervening
in-channel terrace or gravel bar.
Code Tc = In-Channel Terrace: areas of intermediate elevation
located between a gravel bar and the outer channel bank/upper
terrrace. In-channel terraces may be in various stages of hummock
formation, or they may be more-or-less level if the hummocks have
already coalesced.
Code P = Point Bar or Alternate Bar: gravel bars formed at bends
in a stream's thalweg that follow bends in the stream channel
are called point bars; bars formed where there is a meandering
thalweg within a straight stream channel are called alternate
bars. There is a gradation between the two types of bars which
often makes them difficult to distinguish; they are therefore
lumped together here.
Code Wc = Wetted channel: that portion of the river's main channel
(or a back channel connected to the mainchannel) in which surface
water is visible.
Code M = Mid-Channel Island, or emergent "riffle bar".
Item (6). Item Name: LANDUSE\Field Width: 9\Data Type: Character
and
Item (7). Item Name: LANDCOVER\Field Width: 10\Data Type: Character
Code A (Land Use) = Agricultural Land
Code v (Land Cover) = Vineyard
Code or (Land Cover) = Orchard
Code rc (Land Cover) = Row Crops
Code w (Land Cover) = Small Farm Pond (< 5 acres)
Code ot (Land Cover) = Other areas of presumed agricultural land
use in which the cover type is uncertain; e.g., harvested crops,
fallow fields, pastures, hayfields, etc.
Code G (Land Use) = Gravel Extraction Pit (excluding
pit margin)
Code w (Land Cover) = Gravel pit filled with water
Code Gmo (Land Use) = Gravel Pit Margin, "open" (i.e., <10% cover)
Code Gmv (Land Use) = Gravel Pit Margin, "vegetated"
(i.e., >10% cover)
Code fs (Land Cover) = Forbs and Shrubs predominate, although
scattered small trees may be present (use
of this category is restricted to relatively early successional
vegetation in habitats that are normally tree-dominated).
Code rf (Land Cover) = Riparian Forest, Woodland, and/or
Scrub
Code Ig (Land Use) = Industrial Land (gravel processing facilities; mainly un-vegetated)
Code Iot (Land Use) = Industrial Land (all other types of heavy industrial facilities; mainly un-vegetated)
Code Iw (Land Use) = industrial-related water features (e.g. sewage treatment ponds)
Code R (Land Use) = Rural Residential, Rural Public Facilities
(e.g. schools), Rural Commercial Land, or Rural Golf Courses and
other landscaped areas with 10-75% tree and/or grass cover
Code w (Land Cover) = rural artificial reservoir (other
than gravel pit or small farm pond)
Code U (Land Use) = Urban Residential, Urban Public Facilities,
Urban Commercial Land, Urban Parks
Code b (Land Cover) = urban built-up or "barren" areas
with <10% tree cover
Code t (Land Cover) = areas with 10-75% tree and/or grass cover
within a zone of primarily urban land uses (e.g., residential
areas; urban parks, golf courses, cemetaries, or other landscaped
areas)
Code f (Land Cover) = urban woodlot; isolated wooded area with
>75% tree cover within a zone of primarily urban land uses
Code w (Land Cover) = artificial reservoir in urban area
Code C (Land Use) = Major Transportation Infrastructure (e.g., multi-lane freeways or other limited-access highways; airport runways and facilities - including pavement and rights-of-way). Smaller roads (whether paved or unpaved) are not shown unless they form part of a polygon boundary.
Code O (Land Use) = Open Land (i.e., mainly unvegetated
land that is not presently in agricultural, industrial, residential,
commercial, transportation, or urban use, with <10% cover by
herbs, shrubs, and/or trees).
Code h (Land Cover) = areas (other than gravel bars or gravel
pit margins) in which open condition is clearly the result of
recent human disturbance by cutting, bulldozing, heavy vehicle
traffic, etc.
Code sc (Land Cover) = a gravel bar which has recently been "scraped"
or "skimmed" to obtain aggregate.
Code N (Land Use) = Non-Cultivated Vegetated Land (i.e.,
cultural, semi-natural, or natural vegetation - see definitions
in report glossary), with >10% cover by herbs, shrubs, and/or
trees.
Code eu (Land Cover) = Eucalyptus Forest
Code df (Land Cover) = Douglas-Fir Forest
Code fs (Land Cover) = Forbs and Shrubs predominate, although
scattered small trees may be present. Use of this category is
restricted to relatively early successional vegetation in habitats
normally dominated by trees; it is not applied to chaparral, marsh,
or grassland)
Code gr (Land Cover) = Grassland or "Savanna" (i.e.,
grassland with widely-spaced shrubs and/or trees)
Code mf (Land Cover) = Mixed Upland Forest (a varied mixture of
broadleaf evergreen, conifer, and broadleaf deciduous trees)
Code ow (Land Cover) = Oak/Hardwood Woodland or Forest (may include
all oak species found in study area)
Code rf (Land Cover) = Riparian Forest, Woodland, and/or Scrub
Code rw (Land Cover) = Redwood Forest
Note: The land form/land use/land cover classification scheme given in the preceding three items is a greatly modified and expanded version of a system developed by Philip Northen (see Northen 1991; 1992). CRP initially attempted to use a classification scheme identical to Northen's, but this turned out not to be feasible due to the smaller scale of our aerial photos (i.e., 1:6,000 instead of 1:2,400).
For example, Northen's "Outer Bank" landform category was not mapped at our photo scale because its narrow width made it very difficult to interpret; it is included in our category of "In-channel Terrace". We also did not find it feasible to map dry secondary channels occurring on point bars as separate units, therefore Northen's "Open Secondary Channel" landform category was not used. If a wet secondary channel was connected to the main river channel at both ends and surface water was visible throughout its length, then it was mapped as a side loop of the main wetted channel. Backwater ponds (isolated wet areas in an otherwise dry secondary channel) or "lagoons" (wet, shallow embayments located where an otherwise dry secondary channel meets the main stem) were also mapped as wetted channel.
Note: Urban forest was originally coded w (for "woods") in the data entry sheets, and the artificial reservoir category was not at first used for urban areas.
Note: It sometimes happened that ground truth personnel estimated the cover in some polygons of the Open land use category to be greater than 10%. In such cases the ground truth estimate was given more weight than the airphoto estimate, because: a) a scattered cover of grasses, forbs and/or shrubs was often difficult to detect on the imagery used in this project, and b) the ground truth data was acquired more recently than the photo data.
******************************************************************************
NOTE: THE FOLLOWING ITEMS (8, 9, 10, 11, and 12) were originally
included in the Habitat databases, but were later dropped because
there was insufficient funding to complete the Wildlife Habitat
Relationships (WHR) analysis for any of the study areas. However,
a WHR analysis for the Middle Reach Study area was subsequently
completed by CRP during a separate project funded by the Ukiah
Cooperative Extension Office of the University of California at
Davis. This involved a series of educational workshops for "grass
roots" groups on the use of GIS and WHR methods in wildlife
habitat analysis. For the sake of completeness, the WHR/CNDDB
categories as used in these workshops are included here.
******************************************************************************
Item (8). Item Name: CNDDB\Field Width: 12\Data Type: Number
and
Item (9). Item Name: WHR\Field Width: 10\Data Type: Character
The California Natural Diversity Data Base (CNDDB) and the Wildlife
Habitat Relationships (WHR) system are used by the Department
of Fish and Game to classify vegetation communities and wildlife
habitats throughout the state (see Airola 1988; Holland 1986;
Mayer and Laudenslayer 1988). In the present study, CRP used both
of these systems to classify polygons, in addition to the land
use/land cover classification scheme presented above. The approximate
correspondences among these three classification systems is given
in the following table, for those land cover units that may occur
in the three study areas:
-----------------------------------------------------------------------------------------------------------Land
Cover Units Used in this Study, and Their Approximate Correspondence
to Units in the WHR
Habitat Type and CNDDB Natural Community Type Classification Systems1
------------------------------------------------------------------------------------------------------------
Land Cover Units (Used In This Study), WHR Codes,WHR Habitats,
CNDDB Codes
Forbs and Shrubs (successional)*2,
CSC, Coastal Scrub, 32100
Grassland/Savanna*3, PGS, Perennial Grassland,
41200
Grassland/Savanna*3, AGS, Annual Grassland,
42200
Freshwater Marsh, FEW, Fresh Water Emergent Wetland, 52400
Vernal Pool, FEW, Fresh Water Emergent Wetland, 52500
Riparian Forest and/or Scrub*4, VRI, Valley-Foothill
Riparian, 61400 & 63400
Oak/Hardwood Woodland*5, (No General Oak
Habitat Classification), 71100
Oak/Hardwood Woodland*5, COW, Coastal Oak
Woodland, 71160, 71120, 71150, 71200
Oak/Hardwood Woodland*5, VOW, Valley Oak
Woodland, 71130, 71210, 81300, 81600
Oak/Hardwood Woodland*5, BOW, Blue Oak Woodland,
71140
Oak/Hardwood Woodland*5, BOP, Blue Oak-Digger
Pine, 71410, 71310, 71320
Oak/Hardwood Woodland*5, MHW, Montane Hardwood,
81320
Mixed Upland Forest*6, MHC, Montane Hardwood-Conifer,
81000, 81100, 81200, 81300
Douglas-Fir Forest, DFR, Douglas-Fir, 81500
Redwood Forest*7, RDW, Redwood, 61120, 82300,
82310, 82320
Wetted Channel of Stream, RIV, Riverine, None
Eucalyptus Forest, VOW*8, Eucalyptus, None
Orchard or Vineyard, OVN, Orchard or Vineyard, None
Row Crops, CRP, Crops, None
Other Agricultural Land, PAS, Pasture, None
Gravel Pits, Reservoirs, Ponds, LAC, Lacustrine, None
Comm./Indust./Urban, URB, Urban, None
R. Resid., Open, BAR, Barren, None
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Notes:
*1 CNDDB codes are generally based on R. F. Holland (1986), and R. F. Holland's WHR-CNDDB correlations in the "Crosswalk Table" on pp. 23-39 in Mayer and Laudenslayer (1988). WHR Habitat names and codes are those listed in Mayer and Laudenslayer (1988) and the California Department of Fish and Game's WHR Computer Database (version 5.0). Since the intention of the WHR system is to classify major vegetative complexes at a scale sufficient to predict wildlife habitat relationships, most of its categories are at the association level of a vegetation classification or higher. A WHR habitat is generally broader than a "natural Community" type in the CNDDB system; i.e., a WHR habitat often encompasses more than one CNDDB community type.
Where disturbance has removed a pre-existing tree cover and tree
species have not yet re-colonized a site to any significant degree,
the WHR system allows the coding of such units as the "seedling
stage" of a tree-dominated habitat. In this project we preferred
not to make assumptions regarding potential vegetation development;
all such units were coded on the basis of their presently existing
cover (e.g., "Open", "Grassland", or "Forbs
and Shrubs").
*2 Areas of forbs and shrubs that represent
early successional stages of tree-dominated habitats in this part
of Sonoma County frequently include dominants (e.g., Baccharis
pilularis) typical of WHR Coastal Scrub habitat (CNDDB Northern
[Franciscan] Coastal Scrub, 32100). Since the study areas are
at the inland fringes of the distribution of Coastal Scrub, this
habitat was used as an approximation of early successional stands.
*3 All Grassland/Savanna cover units were assumed to be WHR Annual Grassland, unless determined by ground truth to be Perennial Grassland.
*4 In the CNDDB system, Riparian Forest is 61400 and Riparian Scrub is 63400, but only the 61400 code was used here.
*5 "Oak/Hardwood Woodlands" in this geographic area are very variable in composition and structure. The CNDDB code 71100 refers to all vegetation types dominated by oaks and other hardwoods, but unfortunately the WHR system does not contain a comparably general designation. The WHR code VOW (Valley Oak Woodland) was therefore used to represent all oak woodlands in the lower-elevation parts of the study area and COW (Coastal Oak Woodland) was used for all hillside oak woodlands, since those appeared to be the most common types. However, in any area where ground-truth data was not obtained it should be realized that stands labeled VOW or COW may actually comprise some of the other oak-and hardwood-dominated types listed in this table.
*6 "Mixed Upland Forest" is a complex mixture of subtypes, most of which contain some percentage of Douglas-Fir. These subtypes vary from mixed hardwood woodlands with California Bay or oaks, to Mixed Evergreen and Redwood Forests, to forests strongly dominated by Douglas Fir. The WHR Douglas-Fir Habitat type (DFR) is broad enough to include all these local variants, but the CNDDB types are more restrictive. It should be noted that the CNDDB type called Douglas-Fir Forest (82400) actually refers to a Douglas-Fir/Sitka Spruce/Western Hemlock assemblage that does not occur within the project area. Most mixed upland forests containing Douglas-Fir in this area were therefore classified in the more general CNDDB category of "Broad-Leaved Upland Forest" (81000), and were correlated to WHR Montane Hardwood-Conifer Habitat (MHC). However, when the estimated canopy cover by Douglas-Fir exceeded 50% the stand was assigned to CNDDB Mixed North Slope Forest (81500) and correlated to WHR Douglas-Fir Habitat (DFR).
*7 On the western side of the river basin in our study areas, the general distribution of Douglas-Fir Habitat given in Mayer and Laudenslayer (1988) completely overlaps that of Redwood Habitat. Where ground truth was lacking it was not always feasible to separate the two types on our aerial imagery. In doubtful cases, alluvial stands that appeared to be dominated by conifers were coded as WHR Redwood Habitat (RDW) and CNDDB Alluvial Redwood Forest (61120/82310); or as CNDDB Upland Redwood Forest (82320) if they occurred in canyon or moist upland sites.
On the eastern side of the river basin, the overlap in Douglas-Fir and Redwood distributions is much smaller; any upland conifer-dominated stands in this area would be coded as WHR Douglas-Fir Habitat (DFR) and CNDDB Mixed North Slope Forest (81500), unless they were located in canyon sites judged to be more appropriate for CNDDB Upland Redwood Forest (82320).
*8 Although Eucalyptus Forest is listed as a habitat type in Mayer and Laudenslayer (1988), iot is not included as a habitat type in version 5.0 of the CWHR database. For lack of a better designation, the few stands of Eucalyptus that were mapped in the present project were coded as VOW on the assumption that their wildlife habitat values are somewhat similar to oaks (although they do not provide the same food resources).
Item (10). Item Name: P_CLOSE\Field Width: 10\Data Type: Character
Canopy closure as estimated from aerial photos ("Photo-Closure")
was classified into three categories:
Code L = Low; from "10"% (i.e., 5-15%) up to "40"%
(i.e., 35-45%)
Code M = Medium; from > "40"% up to "70"%
(i.e., 65-75%)
Code H = High; from > "70"% up to 100%
Note: The standard WHR system uses four classes for percent canopy
closure (i.e., 10-24%, 25-39%, 40-59%, 60-100%). In the present
project it was not feasible to distinguish such narrowly-defined
categories because of the less-than-optimum quality of the available
aerial photos; we therefore used the three broad classes defined
above. In effect our scheme combined the first two WHR categories
("Sparse" and "Open") into a single class,
while retaining classes similar to the WHR's "Moderate"
and "Dense" categories.
Note: Our class boundaries for percent canopy closure were deliberately "fuzzy"; i.e., instead of a class boundary being a single percentage value, our threshold criteria spanned a range of values. The dividing line between canopy closure classes was drawn by eye where there was a "noticeable change" in canopy density that fell within these ranges on the photos; the actual location of the line was therefore a matter of the judgement of the photo-interpreter. According to Thompson (1987) a similar procedure is used by USGS to produce vegetation cover information on 7.5 minute quad maps.
Note: Within Zone C in Sonoma County, percent closure of the riparian vegetation canopy was visually estimated from 1:2,400 (1" = 200') prints of aerial photos flown in 1991 for the County Planning Department's Aggregate Monitoring Program. Aerial photos at 1:2,400-scale were not available outside Zone C in Sonoma County or for any part of the study area in Mendocino County; 1:6,000-scale photos were used in these areas to make canopy closure estimates.
Item (11). Item Name: CROWN_SIZE\Field Width: 12\Data Type: Character
We used 1:2,400-scale and 1:6,000-scale aerial photos to classify
vegetation in terms of the average crown diameter of overstory
trees. However, we modified the criteria of the WHR system (Mayer
and Laudenslayer 1988) by dropping the "multi-layered"
class (because it combines layering and cover criteria rather
than just tree size), and lumping the remaining five WHR classes
into three categories, as follows:
Code A = Seedling to Sapling size (<15'; WHR codes 1 and 2)
Code B = Pole to Small size (15'-45'; WHR codes 3 and 4)
Code C = Medium to Large size (>45'; WHR code 5)
The use of these three broad size classes was a deliberate tradeoff, intended to improve the accuracy of classification by accepting some loss of precision.
Note: The WHR system assumes that there is a consistent relationship between crown diameter and dbh which can be applied to all species of conifers on the one hand and all species of hardwoods on the other. No doubt this is an over-simplification, but it enables the user of the WHR system to obtain a rough estimate of average tree dbh from aerial photos in areas or time periods for which ground truth data may be unavailable.
The table below gives the correspondences among size class, conifer
crown diameter, hardwood crown diameter, and dbh class that are
assumed in the WHR system (Mayer and Laudenslayer 1988). Also
shown are the actual sizes of tree crown images as they appear
on aerial photos at the scales which were used in this project:
WHR Code, WHR Size Class, WHR Conifer Crown Diam., WHR Hardwood
Crown Diam., WHR dbh Class, Hdwood Crown Diam. on 1:6,000 Aerial
Photos, Hdwood Crown Diam. on 1:2,400 Aerial Photos
1, Seedling, n/a, n/a, < 1", n/a, n/a
2, Sapling, n/a, < 15', 1-6", < 0.8 mm, < 1.9 mm
3, Pole, < 12', 15-30', 6-11", 0.8 - 1.5 mm, 1.9 - 3.8
mm
4, Small, 12-24', 30-45', 11-24", 1.5 - 2.3 mm, 3.8 - 5.7
mm
5, Med/Large, > 24', > 45', > 24", > 2.3 mm,
> 5.7 mm
Note: The structural condition of an entire stand, i.e., its particular
combination of average tree size and canopy closure, is called
the "habitat stage" in WHR terminology. A concept similar
to that of the WHR habitat stage (albeit at a coarser resolution)
can be expressed in our system by combining the codes for our
three crown size classes with the codes for our three canopy closure
classes.
For example, in our terminology the single habitat stage "BL" (consisting of "Pole to Small" size class trees with "Low" canopy closure) could include up to four of the WHR habitat stages: Pole/Sparse (3S), Pole/Open (3P), Small/Sparse (4S), and Small/Open (4P).
Item (12). Item Name: ELEMENTS\Field Width: 160\Data Type: Character
"Special Habitat Elements" are specific microhabitat
components which are thought to be of importance to wildlife.
The following set of elements was selected from the WHR list (see
definitions in Mayer and Laudenslayer 1988); during the ground
survey, a special effort was made to note the presence within
a map polygon of any of these elements, regardless of quantity.
Other elements that occurred frequently were also noted:
Physical Elements:
Code cl = cliff
Code ba = bank
Code po = pond
Dead or Decadent Vegetation Elements:
Code sn = snags (sound, rotten, small, medium, or large)
Code st = stumps (sound, rotten, or hollow)
Code sl = slash (small or large)
Code br = brush pile: slash that has been moved into a pile
Code lo = logs (medium or large)
Live Vegetation Elements:
Code tt = trees with broken tops
Code tb = trees with loose bark
Code tc = trees with cavities
Code as = aquatic plants, submerged
Code ae = aquatic plants, emergent
Food Resources:
Code fr = fruits
Code se = seeds
Code ac = acorns
Code gr = grain
Code be = berries
Code co = cones
Code fl = flowers
Code ne = nectar
REFERENCES CITED:
Airola, D. 1988. Guide to the California Wildlife Habitat Relationships System. California Dept. of Fish and Game, Rancho Cordova, CA.
Holland, R. F. 1986. Preliminary description of the terrestrial natural communities of California. California Natural Diversity Data Base, California Dept. Fish and Game.
Mayer, K. and Laudenslayer, W. 1988. A guide to the wildlife habitats of California. California Dept. Forestry and Fire Protection. 166 pp.
Northen, Philip. 1991. Classification Scheme for Landforms, Land Uses, and Vegetation Types in the Planning Area for Sonoma County Aggregate Resources, July 1991.
Northen, P. 1992. Draft Technical Report to Sonoma County Planning Dept. on biological studies for the ARM Plan Update.
Thompson, M. 1987. Maps for America: Cartographic products of the U.S. Geological Survey and others. U.S.G.S., Reston, VA. 265 pp.