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This protocol pages provides a brief summary of the collection p=
rocess for FPC field data, which is largely taken from the ABARES ground cov=
er monitoring field manual (Muir et al. 2011).
The metric of overstorey vegetation cover adopted in many Australi=
an vegetation classification frameworks is Foliage Projective Cover (FPC). =
FPC is defined as the vertically projected percentage cover of photosynthet=
ic foliage of all strata, or equivalently, the fraction of the vertical vie=
w that is occluded by foliage. Overstorey FPC is defined as the vertically =
projected percentage cover of photosynthetic foliage from tree and shrub li=
fe forms greater than 2m height and was the definition of woody vegetation =
cover adopted by SLATS. Overstorey FPC is one minus the gap probability at a zenit=
h angle of zero and therefore it has a logarithmic relationship with effect=
ive leaf area index. Since Australian plant communities are dominated by tr=
ees and shrubs with sparse foliage and irregular crown shapes, overstorey F=
PC is a more suitable indicator of a plant community=E2=80=99s radiation in=
terception and transpiration than crown cover.
Ground cover is the non-woody vegetation (forbs, grasses and herbs), lit=
ter, cryptogamic crusts and rock in contact with the soil surface. Ground c=
over changes in response to climate variables, vegetation dynamics and land=
management. Factors such as grazing pressure, tillage and stubble practice=
s, drought and fire all affect ground cover. The quantity of ground cover a=
ffects water infiltration, runoff, erosion and carbon sequestration. It is =
a key indicator of land condition such as soil degradation, pasture product=
ion and biodiversity. Estimates of ground cover and changes in the quantity=
and spatial arrangement of ground cover over time provide land managers, p=
olicy-makers and scientists with valuable information for use in planning, =
monitoring and modelling applications.
FPC and Ground cover can be monitored using remote sensing. From a remot=
e sensing perspective, FPC is the woody green cover in the overstorey while=
ground cover is the fractional cover of the non-woody vegetation and litte=
r near the soil surface. The field measurement protocol described here is u=
sed to derive three categories of cover from satellite imagery=E2=80=94 pho=
tosynthetic vegetation (PV), non-photosynthetic vegetation (NPV) and bare s=
oil (BS).
Plot Selection=
strong>
Each 1 ha plot is a small homogenous area representative of a particular=
landscape. As many sites as possible are selected within the super s=
ite to ensure sampling of the major of landscapes present (determined by la=
ndform, vegetation, land surface, soil and other land features). Capt=
uring the variability at the site should also be a priority and the overall=
sampling strategy should include a range of soil colours and textures and =
vegetation compositions. Site selection can be informed by viewing satellit=
e imagery or aerial photography.
The following points need to considered when locating sites:
-
Plot areas should be homogeneous, minimising within site variation;
<=
/li>
-
The edge of a site should be at least 100 metres from roads, power lines=
or other features not characteristic of the plot;
-
Sites should be located away from water run-on areas as moisture can aff=
ect reflectance characteristics; and
-
Sites should be located on level or near level ground. If a sloped site =
is necessary, avoid western and southern slopes as these can be affected by=
shadow.
Plot Layout
Each plot should consist of three transects laid out in a star shape, wi=
th 100 observations along each (300 observations in total). The first=
transect runs from north to south, the second from 60=C2=BA to 240=C2=BA a=
nd the third from 120=C2=BA to 300=C2=BA.
Data Collection =
Process
Basic Data Required<=
/h3>
The following data must be recorded for each =
plot, for data management purposes.
-
Geographic coordinates (easting, northing,zone) at plot centre
-
Operators: who collected the data
-
Date: consistent format (dd/mm/yyyy)
-
Time: consistent format (hh:mm)
-
Plot name: name of specific plot
Field Eq=
uipment Checklist
-
GPS (differential preferred)
-
3 x 100 m measuring tapes
-
Stake or star picket
-
Hammer
-
Compass
-
Clinometer - A clinometer measures inclination or slope.
-
Munsell charts and Water bottle (for wetting up samples)
-
Optical wedge prisms (factors 1.0 and 2.0)
-
Digital camera
-
Field sheets and clipboard
-
Electronic site forms and notebook computer (optional)
-
Vegetation identification books
-
Densitometer and telescopic pole for mounting densitometer
-
Laser pointer and tape for attaching to pole
-
Biomass images for estimation
Process
-
Lay out transect
-
Hammer stake into ground at centre of site.
-
Use compass to find 0=C2=B0 bearing and run a tape out at this bearing f=
or 50 metres. The tapes should be placed on the ground underneath vegetatio=
n and be straight and follow a constant bearing. The operator should sight =
from the centre of the tapes along the bearing, and choose a landmark like =
a tree, to walk towards. Avoid trampling along the transects where observat=
ions will be made.
-
Return to centre and twist tape once around the stake to secure in place=
. Run remaining 50 metres of tape out at 180=C2=B0.
-
Repeat for the second and third tapes, at 60=C2=B0-240=C2=B0 and 120=C2=
=B0-300=C2=B0 respectively.
-
Average GPS readings to obtain site centre coordinates.
2. Take Transect Measurements
Transect measurements are taken using a specialised measuring device con=
sisting of: a densitometer for measuring woody vegetation; a laser pointer =
for measuring the ground cover and low woody vegetation; and a telescopic p=
ole to which the laser pointer and densitometer are attached. The densitome=
ter is attached to the top of the telescopic pole, while the laser pointer =
is attached to the same pole near the bottom, pointing downward.
Transect measurements are recorded in three vegetation categories: non-w=
oody and ground cover; woody <2 m; and woody >2 m. An observation, us=
ing the measuring device, is made every metre starting at the 1 metre point=
of each transect. Observations are completed north to south on the first t=
ransect, 60 to 240 degrees on the second transect and 120 to 300 degrees on=
the third transect. A measurement is always recorded for the ground =
cover category. Measurements for the other two categories are only recorded=
if they are visible.
Measuring ground cover
This category includes non-woody vegetation (such as grasses, forbs and =
herbs), litter, cryptogams, soil and rock. There is no height restriction f=
or the non-woody vegetation.
-
Position the pole with the laser pointer attached vertically next to the=
metre mark on the measuring tape. Use level in densitometer to ensure pole=
is vertical.
-
Press the power button of the laser pointer.
-
Record the first intercept of the laser beam when looking downwards in t=
he appropriate category from the list below:
-
Crust=E2=80=94the hard surface layer of soil.
-
Disturbed soil=E2=80=94cracks in a soil crust, ant nest=
s or other disturbances in the natural surface e.g. by animal hoof prints. =
In ploughed agricultural sites most soil recordings will be disturbed.
<=
/li>
-
Rock/lag=E2=80=94rock includes all stones and rock mate=
rial greater than 2 cm. Lag includes all single grains that can be differen=
tiated by the naked eye, approximately 2 mm to 2 cm.
-
Cryptogam=E2=80=94a biological crust composed of lichen=
, moss and algae.
-
Green leaf=E2=80=94a leaf with green pigmentation (one =
that is actively photosynthesising) attached to the plant. Sometimes the le=
af in this state may appear more yellow than green. In this case a judgemen=
t call must be made as to whether it is placed in the green or dry category=
.
-
Dry leaf=E2=80=94a leaf with non-green pigmentation (on=
e that is not actively photosynthesising). This can include senescent (aliv=
e) vegetation as well as dead vegetation. It must be attached to the ground=
or plant.
-
Litter=E2=80=94dead plant material that is not attached=
to the ground. Includes branches, leaves or fallen tree trunks.
Measuring woody vegetation less than 2 metres in heigh=
t
All vegetation with a woody component and a height of less than 2 metres=
. These are generally shrubs and small trees.
-
Maintain the pole in the same position as where the ground cover measure=
ment was taken.
-
Determine if there is an intercept of woody vegetation <2 m with the =
pole directly above the point recorded for the ground cover.
-
Record the intercept in the appropriate category=E2=80=94green leaf, dry=
leaf, branch.
-
Green leaf=E2=80=94a green leaf attached to a plant.
-
Dry leaf=E2=80=94a dead or dry leaf attached to a plant=
.
-
Branch=E2=80=94woody component of the plant (branch or =
trunk).
Measuring woody vegetation taller than 2 metres<=
/strong>
All woody vegetation with a height of 2 metres or more=E2=80=94trees and=
tall shrubs.
-
Maintain the pole and densitometer in the same position as used for the =
ground cover and woody vegetation <2 m measurements.
-
The observer checks visually to determine if the pole is positioned belo=
w a live tree crown or a dead/defoliated tree, or neither. If it is difficu=
lt to determine if the tree is completely dead, assume it is live.
-
If within a live tree crown the densitometer is positioned vertically us=
ing the spirit levels and the observer peers through the mirror sight to de=
termine the first intercept directly above the viewpoint.
-
when in canopy gap (no intercept), record as "In Crown" only
-
when there is an interception with a canopy element record as "In Crown"=
AND one of "green leaf" OR "dry leaf" OR "branch=E2=80=9D
-
If the tree is completely dead or defoliated:
-
If the pole is not positioned below a live tree crown or dead tree then =
no recording is made for any category in the woody vegetation >2 m.
<=
/li>
=
Site Description
To adequately describe the site a description of topography, vegetation =
structure, erosion characteristics, deposited materials, soil and rock colo=
ur, and tree basal area is recorded. Most of the data required is assumed k=
nowledge or sufficiently described within the field data forms and data ent=
ry templates. Further information for some of data elements is descri=
bed below.
Hillslope
To measure hillslope an observer faces in the direction of the slope, an=
d levels the sight of the clinometer at a point in the distance which is ap=
proximately the same height as their own height The slope is recorded in pe=
r cent (0 =E2=80=93 100%).
Soil and Rock Colour
The Munsell Soil Colour Charts are used to record soil, rock and lag col=
our. Three readings are taken: hue, value and chroma. To obtain the reading=
a small amount of soil is held under the colour chart, to find the closest=
match. Both wet and dry recordings for soil crust (hard compacted surface =
soil) and disturbed soil (loose soil) are taken. A bottle is used to carry =
water to the site, to dampen the soil for the wet recordings.
Basal Area
To calculate the site tree basal area, 7 readings (one at plot centre, 6=
at the halfway point of each arm of star transect). using the optical wedg=
e prisms are taken and averaged. To use the optical wedge prism it is held =
at arms=E2=80=99 length and the observer looks through the prism at the tre=
e being counted. If the tree trunk appears to overlap the tree viewed witho=
ut the wedge prism the tree is counted (Figure 5a). If the trunk does not o=
verlap the tree is not counted (Figure 5b). In cases where the trunk just t=
ouches, the tree is given a 1/2 count (Figure 5c). With the prism kept at a=
fixed point, the observer rotates 360 degrees around the prism and counts =
all trees that are =E2=80=98in=E2=80=99. The basal area is the number of =
=E2=80=98in trees=E2=80=99 multiplied by the basal area factor of the wedge=
prism or gauge. In Australia only optical wedge prisms with a basal area f=
actor of 1.0 or greater are available from suppliers. Count all trees when =
using the wedge prism at sites with average tree diameter less than 0.3 met=
res.
Data Recording=
and Storage
Recording
Data in the field will either be directly entered into specially prepare=
d ODK forms, or into field sheets =
and then transcribed later.
Data Storage
The SLATS star transect data is collated by the Remote Sensing Centre, Q=
ueensland Department of Environment and Science, and stored in an in-house =
PostgreSQL database and file storage system. It is then published out to TE=
RN through the SLA=
TS star transect metadata, and the JRSRP https://field.jrsrp.com/.
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