The significance of larger remnants at retaining local bio-diversity in an essentially cleared and fragmented
bio-diversity. This was highlighted by our comprehensive survey of vascular flora of Jingaring Nature Reserve,
which included every season over a two-year period. The exceptionally diverse flora of this relatively undis-
turbed wheatbelt remnant identified six distinct communities encompassing heaths and woodlands. Over 260
vascular species were recorded, including two rare, five priority and a number of species of special interest from
51 families. Weeds accounted for 27 species, but the extent of invasion is relatively low. The known limit of many
species’ distributions occur near or at the reserve and this may be an evolutionary artefact of significant impor-
tance. Higher species diversity per unit area was recorded compared to other unpublished surveys of larger areas
Several management issues are of concern for Jingaring Nature Reserve including protection of rare and
priority flora, weed invasion, fire management and damage caused by unauthorised access. Eradication of
rabbits and localised weed control around rabbit warrens in the reserve should result in regeneration of these
Journal of the Royal Society of Western Australia, 84 (2), June 2001
54
Methods
The vegetation communities of Jingaring Nature Re-
serve were interpreted from a 1996 aerial photograph and
confirmed in the field during 1999. Classification of these
vegetation communities is based on Muir (1977b). This
classification assesses vegetation structure by taking meas-
ures of lifeform/height class and canopy cover/density
class to produce a vegetation type. For example, trees 15-
30 m with a 10-30% canopy cover were designated
woodlands, while the same trees with a canopy cover of 2-
10% would be designated as open woodlands. To a
significant extent this classification also reflects species
compositional differences. Additionally, brief investiga-
tions were made of the soils in each vegetation community.
This included taking soil samples (~3 cm depth) to nomi-
nally assess soil texture and colour.
The flora survey and collections were accomplished
by walking along transects (spaced 150 m apart) which
spanned the full width of the reserve in a north-south
orientation. The first transect began at approximately 50
m in from the reserve’s south-west corner, in the vicinity
of Sandplain Creek. Every vegetation type was traversed
several times using this technique. This transect survey
was undertaken during late spring 1998, but various addi-
tional surveys were also carried out during mid autumn,
early and late winter, early and mid spring, and early
summer over 1998 and 1999. On these occasions a tech-
nique known as ‘randomized stratified walk’ (Hopper et
al. 1997) was employed. As the name suggests, this method
involves specimen collections via random walks in each
habitat type. The purpose of this intensive surveying was
to obtain a good flowering specimen of each species and
to compile a more complete vascular flora list (i.e. as a
benchmark survey).
The authors identified most specimens with some as-
sistance from specialist staff of the WA Herbarium. All
specimens were submitted for incorporation at the WA
Herbarium. Species names follow WACENSUS (WA Her-
barium census of Western Australian vascular plants),
while conservation status of species is according to De-
partment of Conservation and Land Management’s
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