THE STUDY AREA & SURVEY METHOLOLOGY
3.1.1 The Study Area
The area chosen for the fieldwork was in the
Wirral peninsula, which lies between the estuaries of the Dee and the Mersey
(Map 1). This area
was chosen for the following reasons: Firstly it contained a reasonable
population of hedgerow oak trees, a reasonable population being one of
sufficient size to give a good sample accuracy (Hetherington, 1975). Secondly
it was uniform in topography, climate, geology and soil type. Thirdly, as
transport was a limiting factor, it was within cycling distance of my home.
Tables 2a and
2b show the mean monthly temperatures and rainfall
recorded at Bidston Observatory which is located in the north of the Wirral.
Table 2a: Mean Monthly
Temperature For Bidston Observatory (Hewitt, 1922).
|
January |
July |
Mean monthly temperature |
4 º C |
15.7 º C |
Table 2b: Rainfall
Information For Bidston Observatory (from Hewitt, 1922).
Annual Range |
Annual Average |
No. of Rainy Days |
536 mm |
760 mm |
190 days |
3.1.3 Geology and soils
The solid geology of the Wirral peninsula
consists of sandstones and marls belonging to the Triassic formation. The only
exception to this is a small area of Carboniferous sandstone and shales near
Neston on the side of the Dee estuary.
Table 3 : Sub-divisions
of The Triassic Sandstone Series
Division |
Sub-Division |
Keuper |
Red marl
Keuper sandstone |
Bunter |
Upper Bunter formation
Middle Bunter formation
Lower Bunter formation |
All the sub-divisions of the Triassic sandstone
series (Table 3) are found on the surface or in exposed
cuttings in some part of the Wirral, but for the most part they are hidden
under superficial glacial ueposits (Hewitt, 1922). Due to the action of the
glaciers the Wirral is extremely flat, its hignest point being about 200 metres
above sea level.
Gould et al (1982) surnmarises the
physical and climatic factors on the Wirral as follows: Within
Merseyside, an area with an equable climate ana unspectacular topography, the
principal determinant of land capability is soil type. Medium to heavy
clay soils (Map 2)
dominate the farmland. Much of the land is under permanent grassland, with
dairy farming the principal enterprise. Despite some limitations in the
flexibility of cropping, the inherent soil fertility is high and aue to a
comparatively long growing season it supports highly productive grassland. Most
of the glacial till is classed as agricultural grade 3, but one area of blown
sand in North Wirral is grade 2 (Map 3).
3.2.1 Survey
Methodology
Using a 1:10 000 scale Ordnance Survey map of
the farmland area shown in map 1, six 200 metre wide transects were marked out
using the East-West grid lines (see Map 4). This would give a 20 percent sample which would
be sufficient to facilitate further analysis.
As the transects crossed private farmland,
belonging to the Lever-Hulme Estate, the Estate manager was contacted and his
permission sought in order to carry out the survey. After receiving the
necessary permission, every tenant farmer on the estate was contacted by
letter. Most did not reply, but it was assumed from this that they had no
objection.
An initial survey of roadside trees was carried
out in order to identify any problems involved in sampling, and to determine if
there was any difference in their condition compared with other hedgerow trees.
As the roadside trees were all on public property they were easy to get to and
no permission had to be sought in order to measure them. The trees measured in
the roadside tree survey were not included in the transepts.
3.2.2 Fieldwork
Methodology
A
booking form was
drawn up from which sufficient information could be derived to find the
trees total and timber volumes. A number of descriptive categories were
included to determine the potential timber quality. A young tree
was simply defined as any tree with a dbh less than 20 cm. A tree was
over-mature if it had: a timber height of 0 m, due to disease or
decay; miscoloured or sparse foliage (note the luxuriant green of the tree in
Photograph 1 compared with the pale sparse foliage of that
in Photograph 2); very large decayed or dead. limbs or
slime fluxes exuding from the bole. Dead trees also included trees
that were only just alive, often referred to as ruins. Any tree
which did not fit into any of the above categories was recorded as being
mature.
Photograph 1: Tree With
Healthy Crown
Photograph 2: Oak Tree
With Poor Crown
To count as a sample tree, an oak had to lie
within the 200 m transect or the road boundary, have no obstruction around it
(such as a dense hedge or heavy growth of ivy) which would prevent the dbh
being measured, and be either free-standing or part of a group of less than 0.1
hectare in area.
3.3.1 Fieldwork
Detail
The fieldwork was carried out during
September 1986. On arriving at a sample tree, the total height and the timber
height were measured or estimated, at first using a hipsometer, but after a few
days the total height could be estimated to the nearest metre by eye. The
timber height was estimated to the nearest 0.5 m. The dbh was then measured
using a girth-diameter tape. Standing back from the tree, a visual assessment
was made as described in section 3.2.2.
3.3.2 Method Of
Timber Volume Calculation
This was derived using Hubers formula:
Formula 1: V = L(gm)
where:
V = Volume (m3)
L = Timber Height (m)
gm = Cross-sectional area at the
middle of the log.
The timber height (L) was defined as the
length of clean bole (to 7 cm top diameter) which would be suitable for sale as
a sawlog. This was usually up to the lowest major limb. Trees with obvious stem
rot, stem damage and twisted or deformed butts were given a timber height of
zero (Forestry Commission, 1984).
An average taper for open grown oak trees of
1:150 was assumed and the theoretical value for gm calculated. In
all cases there was no significant difference between this theoretical value
for gm and the trees basal area.
So simply by converting dbh to Basal Area
and multiplying this value by the timber height, the approximate timber volume
was found.
3.3.3 Method Of Total
Volume Calculation
The calculation of the estimated total
volume of the tree was slightly more complicated. Cannell (1984) suggests the
following approximations for trees with heavy crowns:
Formula 2: VT = 0.59 (HG)
where:
VT = Total wood volume (m3)
0.59 = Form factor (estimated)
H = Mean tree height (for each sample)
G = Basal area
This provides a reasonable estimate of the
average total tree volume, out is unreliable for the total volume of individual
trees.
3.3.4 Analysis of
Results
The data collected from the 515 trees sampled
was fed into the Universities DEC-2020 computer and analysed using the MINITAB
statistics package. Output of the raw data files are contained in
Tables 18,
19, 20,
21, 22 &
23.
©
1987 Robert I. Bradshaw
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