
Content
Chapter Title Page
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1.3 EM&A
Requirements on Ecological impact 2.3 Monitoring of Herpetofauna 2.4 Monitoring of Dragonflies and Butterflies 3.1 Ecological
Issues/Management Activities 3.2 Implications
to the WRA Design |
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Table
1.1:__ Summary
of ecological Impact EM&A Requirements |
Figure 1.1 Survey Area
and Transect Walked
List of Appendices
Appendix A Schedule of Ecological Monitoring
Appendix B Summary of bird surveys
Appendix C Summary of herpetofauna monitoring, mammals and insects surveys
In March 2005, the Project Proponent, Profit
Point Enterprises Limited, acquired the development site in Yuen Long at
Wo Shang Wai. An Environmental Impact Assessment (EIA) was carried out under the
EIA Ordinance (EIAO) since then and the Environmental Permit (EP-311/2008B) for
construction of the comprehensive development in Wo Shang Wai was granted by
EPD on 29 July 2010. The Project involves the residential development and associated
infrastructure and wetland restoration area and linear
landscape area. The construction works under the Environmental Permit commenced
on 12 May 2010.
Mott MacDonald Hong Kong Ltd. (“MMHK”) has been commissioned by the Contractor, Heng Shung Construction Co. Ltd., to undertake the Environmental Team (ET) services to carry out environmental monitoring and audit (EM&A) for both pre-construction and construction phases of the Proposed Comprehensive Development at Wo Shang Wai, Yuen Long.
According to the EP Condition 4.6, the EM&A results on ecological aspects during the construction phase should be reported to the EIA Subcommittee of the ACE, EPD and AFCD on a biannual basis. This is the 1st Biannual EM&A report and it summarises the findings on EM&A results of ecological aspects during the period from 12 May to 31 October 2010.
Surveys were conducted within 500
m of the Project area. The Wetland
Restoration Area (hereafter WRA) was surveyed starting September 2010 as the
area was accessible since early September. The survey transect is provided in Figure 1.1.
The EM&A programme requires environmental monitoring of ecology as specified in the approved EM&A Manual. A summary of ecological impact EM&A requirements is presented in Table 1.1:
Table 1.1: Summary of ecological Impact EM&A Requirements
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Descriptions |
Locations |
Frequencies |
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Birds |
Within the Project Area and Assessment Area of 500m |
Weekly |
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Dragonflies and Butterflies |
Within the Project Area and Assessment Area of 500m |
Once per month during Mar and Sep to November, and twice per month during Apr to Aug |
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Herpetofauna |
Within the Project Area and Assessment Area of 500m |
Once per month during Apr to Nov |
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Water quality of WRA |
Wetland Restoration Area |
After filling of WRA with water, monthly for in situ water quality and every size months (end of wet season and end of dry season) for laboratory testing |
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Site Inspections |
Within the Project Area and Assessment Area of 500m |
Weekly |
In
accordance with the EM&A requirements, monitoring of birds, dragonflies and
butterflies, and herpetofauna was carried out during the reporting period.
In addition, monitoring of mammals was also conducted
concurrently with other surveys and the results were reported although it is
not required by the EM&A manual. The dates of surveys are summarised in Appendix A.
Monitoring was undertaken following the
survey methodology in the EM&A Manual. In addition, low intensity
monitoring of the WRA was undertaken (on a monthly basis) to monitor faunal
usage of the newly formed cells since September 2010; monitoring intensity will
follow that outlined in the EM&A Manual at the completion of the WRA. All
bird species of conservation importance and/or wetland dependent were
identified and enumerated. Flying birds were not recorded unless they were
foraging and/or associated with the habitat (such as swifts). Further, notable
bird observations during other surveys were also recorded.
Bird surveys were conducted on a weekly
basis. A total of 49 bird species of conservation importance and/or
wetland-dependence were recorded within 500 m of the Project area in the survey
period. This number includes all bird of prey species recorded and any locally
uncommon or rare species. A summary of survey data is provided in Appendix B.
A total of 25 bird species were recorded in
the Wetland Restoration Area (WRA) between September and October 2010. Of these
25 species, 14 of these bird species of conservation importance and/or
wetland-dependence. Bird species of conservation importance recorded so far
included four species of ardeids (two of which are target species Little Egret
Egretta garzetta and Chinese Pond Heron Ardeola bacchus), three species of bird
of prey and other species of conservation importance such as Black-winged Stilt
Himantopus himantopus, Little Ringed Plover Charadrius dubius, Red-necked Stint
Calidris ruficollis and Buff-bellied Pipit Anthus rubescens. A summary of
survey data is provided in Appendix B.
Species and numbers recorded in this survey period are typical of fish pond areas during the period indicating that birds in the area are not presently being adversely affected by the construction of the WRA. These findings indicate that the WRA is already starting to support wetland-dependent birds and other species of conservation importance.
Monitoring was undertaken following the survey methodology in the EM&A Manual. Day-time herpetofauna surveys were conducted monthly between May and October 2010 and while night-time herpetofauna surveys were conducted once per month between May and August. Further, notable herpetofauna observations during other surveys were also recorded.
A total of five amphibian species and two reptiles species were recorded using the ponds within 500 m of the Project area in the survey period. A summary of survey data is provided in Appendix C.
No herpetofauna were recorded in the WRA in the surveys conducted in September and October 2010.
Other significant herpetofauna observations include sightings of Chinese Soft-shelled Turtle Pelodiscus sinensis in bird survey on 29 July 2010 and 24 August 2010 in the ponds within 500 m of the Project area. One Common Rat Snake Ptyas mucosus was also recorded in the same area on 24 August 2010. Chinese Soft-shelled Turtle is listed as vulnerable in the IUCN red list and the China Red Data Book, while Common Rat Snake is listed as endangered in the China Red data book.
Monitoring
of dragonflies and butterflies was conducted on a twice-monthly basis between
May and August 2010 and on a monthly basis between September and October 2010.
Further, notable dragonfly and butterfly observations during other surveys were
also recorded.
A total of
17 dragonfly species and 14 butterfly species were recorded using the ponds
within 500 m of the Project in the survey period. While ten dragonfly species
and three butterfly species were recorded in the WRA. A summary of the survey
findings is provided in Appendix C.
Other
significant sightings of dragonflies and butterflies include a record of one
Dancing Dropwing (Trithemis pallidinervis) in the WRA on 29 September 2010
during ad hoc site visit. This is an uncommon dragonfly species that occurs in
marshes and still waters in
Monitoring of mammals was conducted concurrently
with other surveys but no mammal was recorded during the reporting period.
No
ecological issues or management activities were identified.
There were no additional
implications to the WRA design from the survey findings.
Ecological monitoring between 12 May and 31 October
2010 was carried out following the survey methodology and frequency outlined in
the EM&A Manual.
A total of 49 bird species, 5 amphibian
species, 2 reptile species, 17 dragonfly species and 14 butterfly species were
recorded in the ponds within 500 m of the Project area in the survey period.
Survey findings indicate that the ponds within the Survey Area supported
numbers and diversity of wetland-dependent birds and other species of
conservation importance typical of fish pond areas in the autumn months.
25 bird species, 10 dragonfly species and 3
butterfly species were recorded in the WRA, including 14 bird species of
conservation importance and/or wetland-dependence, while all dragonfly species
are wetland-dependent. These findings indicate that the WRA is already starting
to support wetland-dependent birds and other species of conservation
importance.
Chan, S. K.F., K.S. Cheung, C.Y. Ho, F.N Lam &
W.S. Tam, 2005. A Field Guide to the Amphibians of
Fellowes et al., 2002. Wild Animals to Watch:
Terrestrial and Freshwater Fauna of Conservation Concern in
Karsen, S., M.W.N. Lau & A.
Bogadek, 1998.
Lo, P. Y. F.
and W.L. Hui, 2004.
Mott, 2008. WSW Environmental
Monitoring and Audit Manual (March 2008).
Mott, 2008. WSW Environmental
Impact Assessment Report Volumes 1 to 3 (March 2008)
Shek, C. T.
2006. A Field Guide to the Terrestrial
Mammals of
Young, J.J. & Yiu, V., 2002. Butterfly Watching In
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Note:
*
Light grey cells indicated public holidays or Sundays.
One herpetofauna, dragonfly & butterfly survey was conducted within
the WRA only on the 6th October 2010. The other survey was conducted in the
wider Survey Area (excluding WRA) only on the 8th October 2010. Hence, one
complete herpetofauna, dragonfly & butterfly survey was conducted in
October.
Table B1. Summary of
bird monitoring within the Study Area
|
Species
Name |
Scientific
Name |
Conservation
Status (2) |
Mean(4) |
|||||
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May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||
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Little Grebe |
Tachybaptus ruficollis |
LC, (1) |
14.7 |
11.8 |
15.2 |
27.8 |
13.8 |
41.3 |
|
Great Cormorant |
Phalacrocorax carbo |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
3.0 |
|
Grey Heron |
Ardea cinerea |
PRC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
3.5 |
17.8 |
|
Great Egret |
Egretta alba |
PRC, (1) |
26.3 |
30.5 |
13.0 |
12.0 |
40.0 |
34.3 |
|
Intermediate Egret |
Egretta intermedia |
RC, (1) |
0.3 |
0.0 |
0.0 |
0.0 |
2.8 |
2.5 |
|
Little Egret |
Egretta garzetta |
PRC, (1) |
71.7 |
56.3 |
46.0 |
47.8 |
108.8 |
131.5 |
|
Cattle Egret |
Bubulcus ibis |
(LC), (1) |
2.0 |
0.5 |
0.8 |
1.2 |
8.3 |
11.5 |
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Chinese Pond Heron |
Ardeola bacchus |
PRC, (1) |
23.7 |
25.0 |
34.6 |
48.0 |
42.5 |
48.0 |
|
Striated Heron |
Butorides striatus |
(LC), (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
0.0 |
|
Black-crowned Night Heron |
Nycticorax nycticorax |
LC, (1) |
3.0 |
10.8 |
5.4 |
3.6 |
2.8 |
0.3 |
|
Yellow Bittern |
Ixobrychus sinensis |
(LC), (1) |
0.0 |
0.3 |
0.0 |
0.2 |
0.3 |
0.5 |
|
Black-faced Spoonbill |
Platalea minor |
PGC, EN, (1) |
0.0 |
0.0 |
0.0 |
0.4 |
0.0 |
0.0 |
|
Black Kite |
Milvus migrans |
(RC) |
0.3 |
0.0 |
0.2 |
0.0 |
0.8 |
0.3 |
|
Common Kestrel |
Falco tinnunculus |
- |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
|
Japanese Quail |
Coturnix japonica |
LC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
|
White-breasted Waterhen |
Amaurornis phoenicurus |
(1) |
4.3 |
5.8 |
5.2 |
4.2 |
4.0 |
8.8 |
|
Common Moorhen |
Gallinula chloropus |
(1) |
0.0 |
0.0 |
0.0 |
0.4 |
0.8 |
7.0 |
|
Black-winged Stilt |
Himantopus himantopus |
RC, (1) |
0.7 |
0.0 |
0.0 |
0.0 |
0.8 |
11.8 |
|
Little Ringed Plover |
Charadrius dubius |
LC, (1) |
5.3 |
10.8 |
3.2 |
6.0 |
2.0 |
12.3 |
|
Kentish Plover |
Charadrius alexandrinus |
RC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Spotted Redshank |
Tringa erythropus |
RC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
|
Marsh Sandpiper |
Tringa stagnatilis |
RC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
7.5 |
|
Common Greenshank |
Tringa nebularia |
(1) |
0.3 |
1.0 |
0.0 |
0.0 |
0.0 |
3.3 |
|
Green Sandpiper |
Tringa ochropus |
(1) |
0.0 |
0.0 |
0.0 |
3.0 |
4.0 |
9.0 |
|
Wood Sandpiper |
Tringa glareola |
LC, (1) |
0.0 |
0.0 |
0.4 |
1.8 |
1.0 |
11.8 |
|
Common Sandpiper |
Actitis hypoleucos |
(1) |
5.7 |
0.0 |
1.8 |
9.2 |
12.0 |
22.3 |
|
Pintail/Swinhoe's Snipe(3) |
Gallinago stenura/ megala |
LC, (1) |
0.0 |
0.0 |
0.0 |
0.2 |
0.3 |
0.0 |
|
Common Snipe |
Gallinago gallinago |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
2.3 |
|
Temminck’s Stint |
Calidris temminckii |
LC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
2.3 |
|
Whiskered Tern |
Chlidonias hybridus |
(1) |
3.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
White-winged Tern |
Chlidonias leucopterus |
(1) |
14.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Pied Kingfisher |
Ceryle rudis |
(LC), (1) |
0.3 |
1.0 |
0.2 |
0.8 |
0.0 |
0.3 |
|
Common Kingfisher |
Alcedo atthis |
(1) |
3.3 |
3.3 |
4.8 |
8.2 |
10.8 |
12.0 |
|
White-throated Kingfisher |
Halcyon smyrnensis |
(LC) |
0.0 |
0.0 |
1.4 |
2.2 |
1.3 |
2.8 |
|
Red-rumped Swallow |
Hirundo daurica |
- |
0.0 |
1.3 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Yellow Wagtail |
Motacilla flava |
(1) |
12.7 |
0.0 |
0.0 |
0.6 |
5.0 |
13.8 |
|
Grey Wagtail |
Motacilla cinerea |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.5 |
|
Richard’s Pipit |
Anthus richardi |
(1) |
0.0 |
0.0 |
0.2 |
0.0 |
0.0 |
1.0 |
|
Red-throated Pipit |
Anthus cervinus |
LC |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Pallas’s Grasshopper Warbler |
Locustella certhiola |
LC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
0.0 |
|
Black-browed Reed Warbler |
Acrocephalus bistrigiceps |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
2.5 |
|
Oriental Reed Warbler |
Acrocephalus orientalis |
(1) |
0.3 |
0.0 |
0.0 |
0.0 |
0.3 |
6.0 |
|
Zitting Cisticola |
Cisticola juncidis |
LC |
1.3 |
0.8 |
1.2 |
1.2 |
0.5 |
2.5 |
|
Red-billed Starling |
Sturnus sericeus |
GC |
0.0 |
0.0 |
0.0 |
7.8 |
0.0 |
7.5 |
|
White-cheeked Starling |
Sturnus cineraceus |
PRC |
0.0 |
0.0 |
0.0 |
1.6 |
0.0 |
0.3 |
|
White-shouldered Starling |
Sturnus sinensis |
(LC) |
3.7 |
5.5 |
9.2 |
7.2 |
0.8 |
0.0 |
|
Collared Crow |
Corvus torquatus |
LC, NT |
0.0 |
0.0 |
0.4 |
3.6 |
0.3 |
0.8 |
|
No. of Species Recorded |
21 |
15 |
18 |
24 |
29 |
39 |
||
(1)
indicates wetland-dependant or
-associated species.
(2) conservation
status follows that of Fellowes et al.
(2002) and BirdLife International listing (2010).
(3) includes one species pair, Swinhoe’s/Pintail Snipe,
not distinguishable in the field.
(4) equals the average number of individual species
surveyed in each month (i.e. total counts in all surveys divided by number of
surveys in that month).
Table B2. Summary of bird monitoring in the WRA
|
Species
Name |
Scientific
Name |
Conservation
Status (2) |
Mean(3) |
Records
outside survey(4) |
|
|
Sep |
Oct |
||||
|
Grey Heron |
Ardea cinerea |
PRC, (1) |
0 |
0 |
ü |
|
Great Egret |
Egretta alba |
PRC, (1) |
0 |
0 |
ü |
|
Little Egret |
Egretta garzetta |
PRC, (1) |
0 |
0 |
ü |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (1) |
0 |
0 |
ü |
|
Black Kite |
Milvus migrans |
(RC) |
0 |
0 |
ü |
|
Common Kestrel |
Falco tinnunculus |
- |
0 |
0 |
ü |
|
Peregrine Falcon |
Falco peregrinus |
- |
0 |
0 |
ü |
|
Black-winged Stilt |
Himantopus himantopus |
RC, (1) |
8 |
0 |
ü |
|
Little Ringed Plover |
Charadrius dubius |
LC, (1) |
3 |
0 |
ü |
|
Common Sandpiper |
Actitis hypoleucos |
(1) |
1 |
0 |
|
|
Red-necked Stint |
Calidris ruficollis |
LC, (1) |
3 |
0 |
|
|
Spotted Dove |
Spilopelia chinensis |
- |
0 |
0 |
ü |
|
Little Swift |
Apus affinis |
- |
10 |
0 |
|
|
Barn Swallow |
Hirundo rustica |
- |
25 |
0 |
|
|
Yellow Wagtail |
Motacilla flava |
(1) |
0 |
0 |
ü |
|
White Wagtail |
Motacilla alba |
(1) |
3 |
0 |
|
|
Richard's Pipit |
Anthus richardi |
(1) |
0 |
0 |
ü |
|
Red-throated Pipit |
Anthus cervinus |
LC |
0 |
2 |
|
|
Buff-bellied Pipit |
Anthus rubescens |
LC |
0 |
1 |
|
|
Common Stonechat |
Saxicola torquata |
- |
0 |
3 |
ü |
|
Plain Prinia |
Prinia inornata |
- |
0 |
0 |
ü |
|
Dusky Warbler |
Phylloscopus fuscatus |
- |
0 |
0 |
ü |
|
Scaly-breasted Munia |
Lonchura punctulata |
- |
20 |
0 |
|
|
Eurasian Tree Sparrow |
Passer montanus |
- |
20 |
0 |
ü |
|
Crested Myna |
Acridotheres cristatellus |
- |
3 |
0 |
|
|
No. of Species Recorded |
10 |
3 |
16 |
||
(1)
indicates wetland-dependant or
-associated species.
(2) conservation
status follows that of Fellowes et al.
(2002) and BirdLife International listing (2010).
(3)
equals the average number of individual species surveyed in each month (i.e.
total counts in all surveys divided by number of surveys in that month).
(4) includes
observations during other surveys and/or site visits.
Table C1. Summary of herpetofauna monitoring within the Study Area
|
Species
Name |
Scientific
Name |
Conservation
Status (1) |
Mean(42 |
|||||
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||
|
Asian Common Toad |
Bufo melanostictus |
- |
0.0 |
0.0 |
0.5 |
1.5 |
0.0 |
0.0 |
|
Asiatic Painted Frog |
Kaloula pulchra |
- |
0.0 |
0.0 |
25.5 |
0.0 |
0.0 |
0.0 |
|
Ornate Pigmy Frog |
Microhyla ornata |
- |
0.0 |
0.5 |
15.0 |
0.0 |
0.0 |
0.0 |
|
Günther's Frog |
Rana guentheri |
- |
9.5 |
2.0 |
1.0 |
3.5 |
0.0 |
0.0 |
|
Brown Tree Frog |
Polypedates megacephalus |
- |
0.0 |
0.0 |
1.0 |
1.0 |
0.0 |
0.0 |
|
No. of Species Recorded |
1 |
2 |
5 |
3 |
0 |
0 |
||
|
Species Name |
Scientific Name |
Conservation Status (1) |
Mean(2) |
|||||
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||
|
Bowring’s Gecko |
Hemidactylus bowringii |
- |
0.0 |
1.0 |
3.0 |
3.0 |
0.0 |
0.0 |
|
Checkered Keelback |
Xenochrophis piscator |
- |
0.0 |
0.0 |
0.0 |
0.5 |
0.0 |
0.0 |
|
No. of Species Recorded |
0 |
1 |
1 |
2 |
0 |
0 |
||
Notes:
(1) conservation status
follows that of Fellowes et al. (2002) and Shek (2006).
(2) equals the average number of individual species
surveyed in each survey (i.e. total counts in all surveys divided by number of
surveys in that month).
(3) there was no record of herpetofauna in the WRA in
September and October 2010.
Table C2. Summary of mammal monitoring within the Study Area
|
Species
Name |
Scientific
Name |
Conservation
Status (1) |
Max(2) |
|||||
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||
|
No record |
- |
- |
- |
- |
- |
- |
- |
- |
Notes:
(1) conservation status
follows that of Fellowes et al.
(2002), Chan et al. (2005) and Karsen
et al. (1998).
(2) refers to the maximum number of individuals
recorded in each month
Table C3. Summary of dragonfly and butterfly monitoring conducted within
the Study Area
|
Species
Name |
Scientific
Name |
Conservation
Status (1) |
Mean(2) |
|||||
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||
|
Odonate |
||||||||
|
Orange-tailed Midget |
Agriocnemis femina |
- |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
0.0 |
|
Orange-tailed Sprite |
Ceriagrion auranticum |
- |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Common Bluetail |
Ischnura senegalensis |
- |
4.5 |
2.0 |
1.0 |
0.5 |
4.0 |
1.0 |
|
Pale-spotted Emperor |
Anax guttatus |
- |
0.0 |
0.5 |
0.5 |
0.0 |
0.0 |
0.0 |
|
Common Flangetail |
Ictinogomphus pertinax |
- |
0.5 |
0.0 |
3.5 |
1.5 |
1.0 |
0.0 |
|
Golden Flangetail |
Sinictinogomphus clavatus |
- |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Regal Pond Cruiser |
Epopthalmia elegans |
- |
0.0 |
0.0 |
0.5 |
0.0 |
0.0 |
0.0 |
|
Blue Dasher |
Brachydiplax chalybea |
- |
0.5 |
0.0 |
0.5 |
0.0 |
0.0 |
0.0 |
|
Asian Amberwing |
Brachythemis contaminata |
- |
10.0 |
6.0 |
33.5 |
9.0 |
47.0 |
25.0 |
|
Crimson Darter |
Crocothemis servilia |
- |
0.5 |
0.0 |
1.5 |
1.0 |
0.0 |
1.0 |
|
Amber-winged Glider |
Hydrobasileus croceus |
- |
0.5 |
0.0 |
1.0 |
0.0 |
0.0 |
0.0 |
|
Coastal Glider |
Macrodiplax cora |
LC |
2.5 |
14.0 |
11.0 |
16.0 |
64.0 |
14.0 |
|
Green Skimmer |
Orthetrum sabina |
- |
3.5 |
5.0 |
7.5 |
9.5 |
11.0 |
12.0 |
|
Wandering Glider |
Pantala flavescens |
- |
1.5 |
0.5 |
2.5 |
3.5 |
59.0 |
47.0 |
|
Variegated Flutterer |
Rhyothemis variegata |
- |
4.0 |
12.5 |
13.5 |
6.0 |
2.0 |
1.0 |
|
Saddlebag Glider |
Tramea virginia |
- |
3.5 |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Scarlet Basker |
Urothemis signata |
LC |
0.0 |
1.5 |
2.5 |
0.5 |
0.0 |
0.0 |
|
No. of Species Recorded |
13 |
9 |
13 |
9 |
8 |
7 |
||
|
Butterfly |
||||||||
|
Dart Species |
Potanthus sp. |
- |
0.0 |
0.0 |
0.0 |
0.5 |
0.0 |
0.0 |
|
Common Bluebottle |
Graphium sarpedon |
- |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
Common Mormon |
Papilio polytes |
- |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
Spangle |
Papilio protenor |
- |
0.0 |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
Papilio paris |
- |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Red-base Jezebel |
Delias pasithoe |
- |
0.5 |
1.0 |
0.5 |
0.0 |
0.0 |
0.0 |
|
Indian Cabbage White |
Pieris canidia |
- |
1.5 |
7.0 |
1.5 |
0.0 |
0.0 |
0.0 |
|
Mottled Emigrant |
Catopsilia pyranthe |
- |
1.0 |
1.5 |
0.0 |
0.5 |
0.0 |
1.0 |
|
Common Grass Yellow |
Eurema hecabe |
- |
0.0 |
2.5 |
3.5 |
1.0 |
3.0 |
6.0 |
|
Pale Grass Blue |
Zizeeria maha |
- |
3.0 |
1.5 |
0.0 |
2.5 |
1.0 |
4.0 |
|
Lesser Grass Blue |
Zizina otis |
- |
0.0 |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Dark-brand Bush Brown |
Mycalesis mineus |
- |
1.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Common Tiger |
Danaus genutia |
- |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
2.0 |
|
Blue-Spotted Crow |
Euploea midamus |
- |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
0.0 |
|
No. of Species Recorded |
6 |
7 |
3 |
4 |
3 |
6 |
||
Notes:
(1) conservation status
follows that of Fellowes et al.
(2002), Lo & Hui (2004), Wilson (2004) and Young & Yiu (2002).
(2) equals the average number of individual species
surveyed in each survey (i.e. total counts in all surveys divided by number of
surveys in that month)
Table C4. Summary of dragonfly and butterfly monitoring conducted in the
WRA
|
Species
Name |
Scientific
Name |
Conservation
Status (1) |
Mean(2) |
|
|
Sep |
Oct |
|||
|
Odonate |
||||
|
Common
Bluetail |
Ischnura
senegalensis |
- |
1.0 |
12.0 |
|
Pale-spotted
Emperor |
Anax
guttatus |
- |
1.0 |
0.0 |
|
Common
Flangetail |
Ictinogomphus
pertinax |
- |
1.0 |
0.0 |
|
Asian
Amberwing |
Brachythemis
contaminata |
- |
27.0 |
58.0 |
|
Blue
Percher |
Diplacodes
trivialis |
- |
0.0 |
2.0 |
|
Coastal
Glider |
Macrodiplax
cora |
LC |
28.0 |
14.0 |
|
Green
Skimmer |
Orthetrum
sabina |
- |
19.0 |
11.0 |
|
Wandering
Glider |
Pantala
flavescens |
- |
198.0 |
38.0 |
|
Variegated
Flutterer |
Rhyothemis
variegata |
- |
0.0 |
1.0 |
|
Saddlebag
Glider |
Tramea
virginia |
- |
6.0 |
0.0 |
|
No. of Species Recorded |
8 |
7 |
||
|
Butterfly |
||||
|
Tailed
Jay |
Graphium
agamemnon |
- |
0.0 |
1.0 |
|
Mottled
Emigrant |
Catopsilia
pyranthe |
- |
2.0 |
0.0 |
|
Common
Grass Yellow |
Eurema
hecabe |
- |
2.0 |
2.0 |
|
No. of Species Recorded |
2 |
2 |
||
Notes:
(1) conservation status
follows that of Fellowes et al.
(2002), Lo & Hui (2004), Wilson (2004) and Young & Yiu (2002).
(2) equals the average number of individual species
surveyed in each survey (i.e. total counts in all surveys divided by number of
surveys in that month)