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As
indicated in TR2, in the final stages of the SUSDEV
21 Habitat Mapping Baseline Survey, ERM will use
available existing data, including species lists
derived from the HKU Biodiversity Survey, in addition
to the field survey data collected by the SUSDEV
21 Study Team, to recommend an ecological value ranking
for each habitat. Species data are accounted for
in the ranking system agreed in TR1; areas of high
biodiversity and areas which contain documented critical
habitat for rare species will be given a "high" ranking.
As analysis of the Biodiversity Survey dataset for
high biodiversity area (ie "biodiversity hot-spots")
by the HKU Study Team is still on-going and data
on their location are unlikely to be made available
to the SUSDEV 21 Study Team within the programme
for the SUSDEV 21 study. As a fall-back alternative,
data on "rare" species provided by the
database were therefore considered for usage in the
final ranking.
The
HKU Biodiversity Survey GIS database (CD-ROM, version
1) contains a number of layers of information showing
the locations of many species of plants and animals
throughout Hong Kong. While the CD-ROM database has
provided a wealth of interesting and important information
on biodiversity, the authors of this database have
stated that the database requires further validation
by them before using it for any interpretative work
(Dudgeon and Corlett 1999). Although the database
is a useful source of information on species, there
are several gaps and inconsistencies within the dataset
which has impeded usage of the data for the purposes
of upgrading the ecological ranking. For example,
column names are not consistent between files, species
information is incomplete and survey dates are not
provided for many records. In addition, many of the
data appear to have been generalised or recorded
to a level of accuracy ranging from 50
m to 1,000
m, with some of the terrestrial species records sighted
over the ocean. This generalisation of data has impeded
usage of the dataset as the level of accuracy is
outside the mapping range used for this study, ie 20
m (the accuracy level required by the Study Brief).
However,
records on the Rare Plants, Sedges and Fung Shui
Woods files were found to be comparatively more consistent
and thus were considered as a data source for final
ecological value ranking. Although there are a number
(863 of the 954 records) of the "Rare Plants" records
which lack information on date of sighting, all records
were used to locate "rare" plant species.
The
HKU Biodiversity CD-ROM contains a list of 348 rare
plants and their respective locations in Hong Kong.
A recent joint publication from HKU, Kadoorie Farm & Botanic
Garden and South China Institute of Botany (Corlett
et al 2000) has provided up-to-date information on
the existing status of vascular plants which have
been reliably recorded from Hong Kong. Among the
2130 listed plant species, 719 of them were regarded
as "rare" or "very rare". The
rare plant species list from the HKU Biodiversity
Survey was combined with the list from Corlett et
al (2000) (see Annex H). Among the 719 "rare" and "very
rare" species identified by Corlett et al (2000),
200 of them are also listed in the HKU Biodiversity
Survey CD-ROM Rare Plant file, 41 are found in the
Fung Shui Woods file and 14 are in the Sedges file.
Sighting records in the Sedges and Fung Shui Woods
files were extracted and added to the locations of "rare" plants
in the Rare Plants file.
As
one of the criteria for high ecological value habitat
is whether an area provides documented critical habitat
for rare species (see Section 3 of TR1), the intention
was to use the HKU Biodiversity Survey CD-ROM "rare" plant
data to adjust (upgrade) ecological value of those
habitat polygons which have one or more of the identified "rare" plant
species located within it. However, use of the HKU
CD-ROM data to perform the upgrade produced erroneous
results, as the co-ordinate locations of the rare
plant sightings are too general for this purpose.
Many of the positions of sightings are recorded in
an incompatible habitat type (see Figure
7.2a).
Use
of the HKU CD-ROM data increases the area of High
Ecological Value habitat by 16,821.9 ha, with 8,616.3
ha under the "Other" category. This is
considered very unlikely to reflect the situation,
and is believed to be a result of the aspects of
the HKU data discussed above. Table 7.2a shows the
area of each habitat type that was upgraded when
the HKU CD-ROM data were used.
Table
7.2a Area of Habitat Upgraded to High Ecological
Value when using HKU CD-ROM Data |
Data
Source
|
Habitat
Category |
No.
of Polygons |
Area
(ha)
|
HKU Biodiversity Study |
Baeckia Shrubland |
38
|
450.9
|
HKU Biodiversity Study |
Bare Rock or Soil |
8 |
6.9 |
HKU Biodiversity Study |
Cultivation |
19 |
107.6 |
HKU Biodiversity Study |
Fish Pond/ Gei Wai |
1 |
61.1 |
HKU Biodiversity Study |
Grassland |
69 |
7,155.3 |
HKU Biodiversity Study |
Other |
14 |
8,616.3 |
HKU Biodiversity Study |
Quarry |
1 |
37.4 |
HKU Biodiversity Study |
Sandy Shore |
3 |
18.3 |
HKU Biodiversity Study |
Shrubby Grassland |
43 |
368.1 |
Total:
|
196 |
16,821.9 |
Thus,
as the data location accuracies are so greatly incompatible,
the HKU CD-ROM data has been excluded as a source
for upgrading the ecological ranking of habitat.
The rare plant information is however a useful reference
and will be included with the map as a separate GIS
layer.
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