7. MANAGEMENT
PRIORITIES FOR PLANT COMMUNITIES
The purpose
of gap analysis is to identify land-cover types and vertebrate species
in need of additional protection before they become critically threatened.
The gap analysis approach uses management intent expressed in legislation,
designation, or plans as indicators of the kinds of activities that
may be permitted and hence of the potential impact on biodiversity.
The previous two chapters summarized the management status of California's
land-cover types, wildlife habitats, and vertebrate species. Here
we identify the highest p riority elements based in part on management
status and partly on other factors such as their rarity and endemism,
their condition, the historical loss estimated to have occurred,
and additional information about the kinds of activities that are
likely to occur in each type. Table 7-1 lists the highest priority
plant communities, organized into seven categories, from the statewide
assessment and the vulnerable communities in the ten Jepson regions
of California (Hickman 1993; see Appendix
for details on regional assessments).
Within the set
of plant communities, we distinguish seven categories. The first
two categories include all those rated as rare by the NHD (S1 or
S2 in Table 5-2). Of these, the highest priority (Group A in Table
7-1) is for rare communities with less than 20% level of status
1 and 2 management, while the second priority types have more than
20% (Group B).
For widespread
community types, priorities were set based on a combination of two
factors: percentage of status 1 and 2 lands and an index of threat.
The threat index was calculated as a sum of roadedness (Chapter
4) and projected population growth (Chapter
5), normalized by their mean values, and rescaled so that absence
of threat is equal to zero as shown in Figure 7-1. The first group
(Group C) of common communities was characterized by a threat index
> 3.75, indicating a relatively high degree of either past disturbance
or future loss. Note that this threshold level was selected as a
natural break in the set of plant communities, not on any a priori
or theoretical basis. It had the further advantage of allowing us
to divide communities into approximately equal-sized groups. Virtually
all Group C community types were also relatively under-represented
(< 20% status 1 and 2). The remaining four groups all appear
relatively less threatened by roads or future development (threat
index < 3.75) and were categorized based on their level of protection
into roughly equal numbers of types in each group. We used the same
break points as shown in Table 5-2, i.e., 10%, 20%, and 50%, in
decreasing order of priority. Five exceptions were made to these
general rules. Four types that were rated as rare by NHD were mapped
over extensive areas by CA-GAP, perhaps due to differences in interpretation.
We therefore chose to assign Mojave Mixed Steppe, Upland Redwood
Forest, Westside Ponderosa Pine Forest, and Eastside Ponderosa Pine
Forest to groups G, E, E, and D respectively, as if they were not
rare types. Also, we assigned Tamarisk Scrub to group G because
it is not a native community type and in fact is generally considered
a pest species. The remaining urban, agricultural, and non-vegetated
land cover types were assigned to group H that has no conservation
priority for its vegetation values. There may still be important
habitats and other ecosystem values, however, in the non-vegetated
types (e.g., water bodies, sand dunes, rock outcrops, etc.).
Figure 7-1. Vulnerability
groups of widespread plant communities from the statewide gap analysis
based on a combination of current protection and threat.
Table 7-1. Statewide and regional conservation priorities of plant
community types based on gap analysis. Bullets indicate occurrence
of the type in the region >25 kmē, a plus sign '+' indicates
<25 kmē. Shading in the cell indicates the type is considered
vulnerable within that region (see regional gap analysis summaries
in the appendix for details).
An asterisk after the community name indicates a type described
for CA-GAP. Priorities decrease alphabetically; that is, "A" is
highest priority and "G" is lowest.
|
Priority Level |
CNDDB Code |
CNDDB Community Name (Holland 1986) |
SW |
CW |
NW |
GV |
CAS |
MOD |
ESN |
SN |
MOJ |
SON |
|
A |
21210 |
Northern
Foredunes |
|
+ |
+ |
|
|
|
|
|
|
|
|
A |
21310 |
Northern
Dune Scrub |
|
|
· |
|
|
|
|
|
|
|
|
B |
21320 |
Central
Dune Scrub |
|
+ |
|
|
|
|
|
|
|
|
|
F |
22000 |
Desert
Dunes |
|
|
|
|
|
|
|
|
· |
· |
|
B |
23300 |
Monvero
Residual Dunes |
|
|
|
+ |
|
|
|
|
|
|
|
B |
31100 |
Northern
Coastal Bluff Scrub |
|
· |
|
|
|
|
|
|
|
|
|
A |
31200 |
Southern
Coastal Bluff Scrub |
+ |
|
|
|
|
|
|
|
|
|
|
C |
32100 |
Northern
(Franciscan) Coastal Scrub |
|
· |
· |
|
|
|
|
|
|
|
|
C |
32200 |
Central
(Lucian) Coastal Scrub |
|
· |
|
|
|
|
|
|
|
|
|
C |
32300 |
Venturan
Coastal Sage Scrub |
· |
· |
|
|
|
|
|
|
|
|
|
C |
32500 |
Diegan
Coastal Sage Scrub |
· |
|
|
|
|
|
|
|
|
|
|
D |
32600 |
Diablan
Sage Scrub |
|
· |
|
· |
|
|
|
|
|
|
|
C |
32700 |
Riversidian
Sage Scrub |
· |
|
|
|
|
|
|
|
|
|
|
F |
33100 |
Sonoran
Creosote Bush Scrub |
|
|
|
|
|
|
|
|
· |
· |
|
F |
33200 |
Sonoran
Desert Mixed Scrub |
|
|
|
|
|
|
|
|
|
· |
|
F |
34100 |
Mojave
Creosote Bush Scrub |
· |
|
|
|
|
|
· |
+ |
· west only |
· |
|
G |
34210 |
Mojave
Mixed Woody Scrub |
|
|
|
|
|
|
· |
· |
· |
· |
|
G |
34220 |
Mojave
Mixed Steppe |
|
|
|
|
|
|
|
|
· |
|
|
G |
34240 |
Mojave
Mixed Woody and Succulent Scrub |
|
|
|
|
|
|
|
|
· |
· |
|
G |
34300 |
Blackbush
Scrub |
|
|
|
|
|
|
· |
· |
· |
|
|
D |
35100 |
Great
Basin Mixed Scrub |
· |
|
|
|
· |
· |
· |
· |
|
|
|
G |
35110 |
Salvia
dorri/ Chamaebatiaria scrub * |
|
|
|
|
|
· |
|
|
|
|
|
F |
35210 |
Big Sagebrush
Scrub |
· |
+ |
+ |
|
· |
· |
· |
· |
· |
|
|
D |
35211 |
Low Sagebrush
Scrub * |
|
|
|
|
+ |
· |
· |
· |
|
|
|
D |
35212 |
Silver
Sagebrush Scrub * |
|
|
|
|
|
· |
|
· |
|
|
|
G |
35213 |
Black
Sagebrush Scrub * |
|
|
|
|
|
|
|
|
+ |
|
|
E |
35220 |
Subalpine
Sagebrush Scrub |
|
|
|
|
· |
|
|
· |
|
|
|
D |
35400 |
Rabbitbrush
Scrub |
|
|
|
+ |
+ |
· |
+ |
· |
· |
|
|
E |
35500 |
Cercocarpus
ledifolius Woodland * |
+ |
|
|
|
· |
· |
· |
· |
|
|
|
C |
36110 |
Desert
Saltbush Scrub |
|
|
|
|
|
· |
· |
|
· west only |
· |
|
F |
36120 |
Desert
Sink Scrub |
|
|
|
|
|
|
· |
|
· west only |
+ |
|
D |
36130 |
Desert
Greasewood Scrub |
|
|
|
|
|
· |
· |
|
+ |
|
|
G |
36140 |
Shadscale
Scrub |
|
|
|
|
|
|
· |
|
· |
|
|
G |
36150 |
Desert
Holly Scrub * |
|
|
|
|
|
|
|
|
· |
|
|
A |
36210 |
Valley
Sink Scrub |
|
|
|
· |
|
|
|
|
|
|
|
A |
36220 |
Valley
Saltbush Scrub |
|
+ |
|
· |
|
|
|
|
|
|
|
A |
36320 |
Interior
Coast Range Saltbush Scrub |
|
|
|
· |
|
|
|
|
|
|
|
C |
37110 |
Northern
Mixed Chaparral |
· |
+ |
· |
|
· |
|
|
· |
|
|
|
C |
37120 |
Southern
Mixed Chaparral |
· |
|
|
|
|
|
|
|
|
|
|
E |
37200 |
Chamise
Chaparral |
· |
· |
· |
+ |
|
|
|
· |
· |
|
|
C |
37300 |
Red Shank
Chaparral |
· |
+ |
|
|
|
|
|
|
|
|
|
E |
37400 |
Semi-Desert
Chaparral |
· |
· |
|
· |
|
|
|
· |
· |
· |
|
F |
37510 |
Mixed
Montane Chaparral |
· |
+ |
· |
|
· |
|
|
· |
|
|
|
E |
37520 |
Montane
Manzanita Chaparral |
+ |
+ |
· |
|
· |
· |
|
· |
|
|
|
E |
37530 |
Montane
Ceanothus Chaparral |
· |
+ |
· |
|
· |
· |
|
· |
|
|
|
E |
37541 |
Shin Oak
Brush |
|
|
· |
|
· |
|
|
· |
|
|
|
F |
37542 |
Huckleberry
Oak Chaparral |
|
|
· |
|
|
|
|
· |
|
|
|
E |
37550 |
Bush Chinquapin
Chaparral |
|
|
+ |
|
· |
|
|
· |
|
|
|
A |
37610 |
Mixed
Serpentine Chaparral |
|
· |
· |
|
|
|
|
|
|
|
|
E |
37620 |
Leather
Oak Chaparral |
|
· |
|
|
|
|
|
+ |
|
|
|
E |
37810 |
Buck Brush
Chaparral |
· |
· |
· |
|
· |
· |
|
· |
|
|
|
E |
37820 |
Blue Brush
Chaparral |
|
· |
+ |
|
|
|
|
|
|
|
|
C |
37830 |
Ceanothus
crassifolius Chaparral |
· |
+ |
|
|
|
|
|
|
|
|
|
C |
37840 |
Ceanothus
megacarpus Chaparral |
· |
+ |
|
|
|
|
|
|
|
|
|
F |
37900 |
Scrub
Oak Chaparral |
· |
· |
+ |
+ |
|
|
|
· |
|
|
|
F |
37A00 |
Interior
Live Oak Chaparral |
· |
· |
|
· |
· |
|
|
· |
· |
|
|
F |
37B00 |
Upper
Sonoran Manzanita Chaparral |
· |
· |
|
|
|
|
|
· |
|
|
|
A |
37C10 |
Northern
Maritime Chaparral |
|
+ |
|
|
|
|
|
|
|
|
|
A |
37C20 |
Central
Maritime Chaparral |
|
· |
|
|
|
|
|
|
|
|
|
A |
37D00 |
Ione Chaparral |
|
|
|
|
|
|
|
+ |
|
|
|
F |
37E00 |
Mesic
North Slope Chaparral |
+ |
· |
· |
|
+ |
|
|
· |
|
|
|
C |
37G00 |
Coastal
Sage-Chaparral Scrub |
· |
· |
|
|
|
|
|
|
|
|
|
F |
39000 |
Upper
Sonoran Subshrub Scrub |
|
· |
|
· |
|
|
|
+ |
|
|
|
A |
41000 |
Coastal
Prairie |
|
· |
· |
|
|
|
|
|
|
|
|
C |
42110 |
Valley
Needlegrass Grassland |
+ |
|
|
+ |
|
|
|
|
|
|
|
B |
42120 |
Valley
Sacaton Grassland |
|
|
|
+ |
|
|
|
|
|
|
|
D |
42160 |
Desert
Native Grassland * |
|
|
|
|
|
|
|
|
· |
|
|
D |
42200 |
Non-Native
Grassland |
· |
· |
· |
· |
· |
· |
+ |
· |
· |
· |
|
A |
42300 |
Wildflower
Field |
|
|
|
|
|
|
|
|
+ |
|
|
A |
43000 |
Great
Basin Grassland |
|
|
|
|
+ |
· |
+ |
|
|
|
|
D |
44110 |
Northern
Hardpan Vernal Pool |
|
|
|
+ |
|
|
|
|
|
|
|
B |
44120 |
Northern
Claypan Vernal Pool |
|
|
|
+ |
|
|
|
|
|
|
|
A |
44131 |
Northern
Basalt Flow Vernal Pool |
|
|
|
|
|
+ |
|
|
|
|
|
F |
45100 |
Montane
Meadow |
|
|
· |
|
· |
+ |
· |
· |
|
|
|
F |
45200 |
Subalpine
or Alpine Meadow |
|
|
|
|
· |
|
|