3.2 Ware
4. CONCLUSIONS
The conditions at the Ware site were different in that
landfill gas was migrating laterally and affecting both
forested and agricultural areas adjacent to the site. Thus
there was not the same degree of inherent variation in
soil conditions present at the Panshanger site which
could induce variations in plant growth and mask the
effects of landfill gas.
Damage classification of the forested area was carried out
on a crown-by-crown basis using the colour infrared
aerial photographs and a classification system (Table 2)
developed from several sources (Murtha, 1976; Ciesla et
al , 1985; Groves, 1989). An obvious pattern of
damage was present with those trees situated between the
site and agricultural fields to the west of the site
showing damage symptoms most frequently. High
levels of landfill gas had been recorded in this wooded
area.
Supervised classification of the woodland was also
attempted, using the results of the manual classification
to identify training areas. To date, this approach has not
shown much success.
The agricultural fields to the west of the site were
examined using the band combinations given above.
Dead and unhealthy vegetation was observed to exist in a
pattern generally parallel to the edge of the site and
known to have high concentrations of landfill gas in the
subsurface.
3.3 Future Work
The next step in the work is the supervised calssification
of both Daedalus ATM and video imagery, followed by
correlation of aerial imagery and gas concentration data.
The usefulness of the aerial video data for this type of
application will be assessed and the performance of the
two systems compared.
The results to date suggest that, under certain conditions,
remote sensing may provide a useful and timely means
of detecting and monitoring the environmental impact of
landfill gas. However, due to the fact that the effects of
gas on vegetation growth may be masked by a number of
other environmental variables, each situation must be
assessed individually. The likelihood of remote sensing
techniques being successful depends on sufficient
spectral variation existing between healthy and unhealthy
vegetation, and on the ability to distinguish between
stress caused by landfill gas and that induced by other
factors. In summary:
1. Sufficient quantities of gas must exist in the root zone
such that the plants are stressed, and that this stress is
manifested as a change in the spectral properties of the
plant.
2. Relatively homogeneous ground cover must exist.
Variations in soil type or qualitiy, agricultural practices,
etc., may result in variations in vegetation health that are
unrelated to landfill gas.
Initial comparison of ATM and video data indicate that
the Daedalus scanner provides additional spectral
information, particularly in the middle infrared.
Although the initial costs of data collection are high
compared with the video system, this may be partially
offset against the time involved in preprocessing of the
video data. The cost of video data collection is mush
reduced; additional advantages are the lower cost of data
processing, improved spatial resolution, and increased
convenience of data collection.
Manual interpretation of large scale colour infrared
photographs will continue to find use in this type of
study, although due to the time and skill involved in
undertaking this type of analysis, its use may be
somewhat restricted.
In conclusion, in the light of recent legislation in Great
Britain there is an urgent need for a cost-effective and
timely method of collecting information about the lateral
extent of migration of landfill gas. The initial results
indicate that remote sensing has a role to play; the
important conclusion will be which system can fulfill the
required role in the most cost-effective manner.
Classification Rating
Textural Properties of Crown
Spectral Properties of Crown
0 (Healthy)
Irregular perimeter, inner crown
not visible, branches not visible
Even colour, deep red
1 (Sickly)
Sparse crown periphary
May be some mottling at
edges, colour pink-red
2 (Sick)
Thinning of crown, inner crown
and ends of branches visible
Uneven colouring, lighter
pink hue, pale ’flags' of
acutely chloritic foliage
3 (Very sick)
Sparse crown, inner crown clearly
visible, rough crown form
Light pink, may be increased
numbers of flags
4 (Dead)
Skeleton
Grey - white
TABLE 2. Tree Crown Damage Classification System for Hardwoods on
Colour Infrared Aerial Photographs
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