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Proposed Comprehensive Development |
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Biannual
EM&A Report on Ecology for May 2011 – Oct 2011 (Rev. A) |
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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
Appendix D Summary of Water Monitoring
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 3rd Biannual EM&A report and it summarises the findings on EM&A results of ecological aspects during the period from 1 May 2011 to 31 October 2011.
Surveys were conducted within 500
m of the Project area. The Wetland
Restoration Area (hereafter WRA) was surveyed since early September 2010. 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
|
Descriptions |
Locations |
Frequencies |
|
Birds |
Within the Project Area and Assessment Area of 500m |
Weekly |
|
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 |
|
Herpetofauna |
Within the Project Area and Assessment Area of 500m |
Once per month during Apr to Nov |
|
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 |
|
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).
Bird
surveys were conducted on a weekly basis throughout the period. A total of 44[1] bird species of conservation importance and/or
wetland-dependence were recorded in the Survey Area (excluding WRA). A
summary of survey data is provided in Appendix B.
A total of
361 bird species were recorded in the
WRA in the survey period. Of these, 33 of were bird species of conservation
importance and/or wetland-dependence. All three target species (i.e. Little
Egret Egtretta garzetta, Cattle Egret
Bubulcus ibis and Chinese Pond Heron Ardeola bacchus) were recorded in the
WRA, including maximum daily counts of 42 Cattle Egret, 13 Chinese Pond Heron
and 3 Little Egret, a high count for the site in the reporting period. The
reporting period covers the first season of the WRA after site formation works
and filling with water. During this period, several bird species were recorded
breeding on-site, including five to six pairs of Little Ringed Plover Charadrius dubius, a minimum of three
pairs of Little Grebe Tachybaptus
ruficollis and two breeding pairs of Zitting Cisticola Cisticola juncidis. Other notable records included regular
sightings of Collared Crow Corvus
torquatus, a near threatened species (IUCN 2010), Black-naped Oriole Oriolus chinensis and
Purple Heron Ardea purpurea, Pallas’s Grasshopper Warbler Locustella
certhiola and
Lanceolated Warbler Locustella lanceolata, and Yellow Bittern Ixobrychus
sinensis). A
summary of survey data is provided in Appendix B.
Notable records observed in the WRA outside
surveys included Black-winged Kite Elanus caeruleus, Eurasian Hobby Falco subbuteo, Savanna
Nightjar Caprimulgus affinis, Cinnamon
Bittern Ixobrychus sinensis,
and Pheasant-tailed Jacana Hydrophasianus chirurgus.
The site
continues to attract uncommon bird species of conservation importance,
including many species which were not previously recorded on site, indicating
that the site has provided additional habitats for these species. Hence, the
WRA has not only provided a buffer against potential disturbance during the
construction phase, it is also functioning as a valuable habitat for bird
species of conservation importance.
Monitoring
was undertaken following the survey methodology in the EM&A Manual. Day-time
herpetofauna surveys were conducted monthly from May to October 2011, while
night-time herpetofauna surveys were conducted twice per month from May to
August 2011.
4
amphibian species and 2 reptile species were recorded in the survey (excluding
WRA), while 3 amphibian species and 2 reptile species were recorded in the WRA
in the surveys conducted in the reporting period. A summary of survey data is provided
in Appendix
C.
One
Chinese Soft-shelled Turtle Pelodiscus
sinensis and an Indo-Chinese Rat Snake Ptyas
korros were recorded in the Survey Area outside of routine herpetofauna
surveys, while one Chinese Soft-shelled Turtle and a Checkered Keelback were recorded within the WRA outside
surveys. Chinese Soft-shelled Turtle is listed as vulnerable in both the IUCN
red list and the China Red Data Book and as of “Global Concern” in Fellowes et al. (2002). This is the first record
of the species in the WRA. Both snake species are listed as endangered in the
China Red Data Book and listed as “Potential Regional Concern” in Fellowes et al. (2002).
Monitoring
of dragonflies and butterflies was conducted on a twice-monthly basis from May
to August 2011 and on a monthly basis during September and October 2011.
Further, notable dragonfly and butterfly observations during other surveys were
recorded.
A total of
14 dragonfly
species and 13 butterfly species were recorded using the ponds in the survey
area (excluding WRA), and 18 dragonfly species and 8 butterfly species were
recorded in the WRA. One dragonfly species of conservation importance, Coastal
Glider Macrodiplax cora, was recorded
in the survey area. This species is considered to be uncommon and of “Local
Concern” in
Monitoring
of mammals was conducted concurrently with other surveys. 3 mammal species were
recorded in the Survey Area while no mammals were recorded in the WRA. No
species of conservation importance were recorded. A summary of the survey
findings is provided in Appendix C.
Monthly
water quality monitoring commenced in June following filling of ponds.
Monitoring parameters followed that in the EM&A Manual. The action level
exceedance of DO was observed at Cell 1 and 2 in July, August and September
respectively. No measures were proposed, but the condition was monitored. DO in
both cells had improved in October. The action level exceedance of salinity in
May (Cell 1 – 4), June (Cell 2 – 4) and July (Cell 4) was observed. As it was
expected to be improved with the on-set of rainfall events in the following
months, therefore no measures were proposed.
Monitoring
data are presented in Appendix D.
Landscape and establishment works of
the WRA undertaken in the reporting period included the following:
¡
Reed
transplantation from the reedbed nursery to Cells 2, 3 and 4;
¡
Planting
and post-planting maintenance of whip trees, shrubs, wetland plants and
hydroseeding of grasscrete and bunds;
¡
Fish
and shrimp stocking
Species and quantities of fish
stocking and plants stocked/planted followed that outlined in the approved WCRS
(AEC 2011). Some replacement planting/stocking will be required in the next wet
season and this will be evaluated in March/April 2012.
Maintenance and management work
following planting and stocking were as follows:
¡
Hand
weeding around all planted tree whips, shrubs and transplanted reeds;
¡
Clearance
of undesired exotic plants such as Acacia,
Typha, Mimosa, Ipomoea, Sesbania , Leucaena, Aster subdulata and Brachiaria mutica;
¡
Removal
of Apple Snails.
There were no additional implications
to the WRA design from the survey findings.
Ecological monitoring between 1 May
and 31 October 2011 was carried out following the survey methodology and
frequency outlined in the EM&A Manual.
Summary of survey findings listed as
follow:
Table 4.1: Summary of Ecological Monitoring in WRA and Survey Area between 1 May and 31 October 2011
|
No.of Species |
Survey Area (excluding WRA) |
WRA |
|
Birds |
44 |
36 |
|
Amphibians |
4 |
3 |
|
Reptiles |
2 |
2 |
|
Mammals |
3 |
0 |
|
Dragonflies |
14 |
18 |
|
Butterflies |
13 |
8 |
Survey findings demonstrate that the
WRA is supporting a comparable number of species as the fish ponds in the
Survey Area, and as noted in Section 2 above, is attracting a number of
uncommon species of conservation interest. Hence, the WRA is effective as a
buffer between the residential portion of the site in the north and the
fishpond areas in the south, and is also providing habitat for species of
conservation interest.
AEC, 2011.
Proposed Comprehensive Development at Wo Shang Wai, Yuen Long: Detailed Design
and Implementation. Wetland Restoration and Creation Scheme November 2011 v3.
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,
J.F., Lau, M.W.N., Dudgeon, D., Reels, G.T., Ades, G.W.J., Carey, G.J., Chan,
B.P.L., Kendrick, R.C., Lee, K.S., Leven, M.R., Wilson, K.D.P., Yu, Y.T. 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
Tam, T. W.,
Leung, K.K., Kwan, B.S.P., Wu, K.K.Y., Tang, S.S.H., So, I.W.Y., Cheng, J.C.Y.,
Yuen, E.F.M., Tsang, Y.M., and Hui, W.L.
2011. The Dragonflies of Hong Kong (1st edition).
Agriculture, Fisheries and Conservation Department. Friends of
Young, J.J.
& Yiu, V. 2002. Butterfly Watching
In
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Inspection Visits |
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Note:
*
Light grey cells indicated public holidays, Saturdays or Sundays.
Table B1. Summary of
bird monitoring within the
Survey Area
|
Species
Name |
Scientific
Name |
Conservation
Status (2) |
Mean(3) |
|||||
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||
|
Little Grebe |
Tachybaptus ruficollis |
LC, (1) |
4.3 |
3.8 |
3.8 |
14.8 |
13.0 |
12.5 |
|
Great Cormorant |
Phalacrocorax carbo |
PRC, (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 |
2.5 |
11.8 |
|
Great Egret |
Egretta alba |
PRC, (1) |
8.8 |
2.3 |
8.0 |
8.6 |
25.8 |
15.3 |
|
Intermediate Egret |
Egretta intermedia |
RC, (1) |
0.3 |
0.0 |
0.0 |
0.2 |
0.0 |
0.0 |
|
Little Egret |
Egretta garzetta |
PRC, (1) |
33.5 |
9.5 |
17.3 |
90.6 |
134.8 |
151.0 |
|
Cattle Egret |
Bubulcus ibis |
(LC) |
1.0 |
0.0 |
0.0 |
9.0 |
18.8 |
0.8 |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (1) |
15.0 |
17.0 |
15.0 |
18.0 |
28.3 |
27.3 |
|
Black-crowned Night Heron |
Nycticorax nycticorax |
(LC), (1) |
1.8 |
1.0 |
0.5 |
2.6 |
0.3 |
0.0 |
|
Black-faced Spoonbill |
Platalea minor |
PGC, EN, (1) |
0.3 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Garganey |
Anas querquedula |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
2.0 |
|
Black Kite |
Milvus migrans |
(RC) |
0.3 |
0.3 |
0.5 |
0.4 |
0.3 |
1.0 |
|
Common Buzzard |
Buteo buteo |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
0.0 |
|
White-breasted Waterhen |
Amaurornis phoenicurus |
(1) |
4.8 |
1.8 |
1.0 |
1.0 |
2.5 |
2.0 |
|
Common Moorhen |
Gallinula chloropus |
(1) |
0.0 |
0.0 |
0.0 |
0.2 |
0.0 |
3.3 |
|
Black-winged Stilt |
Himantopus himantopus |
RC, (1) |
0.5 |
0.0 |
0.0 |
0.0 |
1.3 |
7.5 |
|
Little Ringed Plover |
Charadrius dubius |
LC, (1) |
0.8 |
0.0 |
0.3 |
0.6 |
10.0 |
7.5 |
|
Kentish Plover |
Charadrius alexandrinus |
RC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
Common Redshank |
Tringa totanus |
RC, (1) |
0.0 |
0.0 |
0.0 |
1.4 |
0.0 |
0.0 |
|
Marsh Sandpiper |
Tringa stagnatilis |
RC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
9.3 |
|
Common Greenshank |
Tringa nebularia |
RC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
5.3 |
|
Green Sandpiper |
Tringa ochropus |
(1) |
0.0 |
0.0 |
0.0 |
1.2 |
2.0 |
2.8 |
|
Wood Sandpiper |
Tringa glareola |
LC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
8.8 |
|
Common Sandpiper |
Actitis hypoleucos |
(1) |
1.8 |
0.0 |
0.3 |
2.0 |
6.5 |
6.0 |
|
Pintail/Swinhoe's Snipe* |
Gallinago
stenura/G. megala |
LC,
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
2.0 |
0.0 |
|
Temminck's Stint |
Calidris temminckii |
LC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.5 |
|
Long-toed
Stint |
Calidris subminuta |
LC,
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
Whiskered
Tern |
Chlidonias hybridus |
(1) |
2.8 |
0.0 |
0.0 |
0.2 |
5.0 |
5.5 |
|
Pied Kingfisher |
Ceryle rudis |
(LC), (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
0.0 |
|
Common Kingfisher |
Alcedo atthis |
(1) |
1.0 |
2.3 |
1.8 |
2.4 |
4.3 |
4.5 |
|
White-throated Kingfisher |
Halcyon smyrnensis |
(LC), (1) |
0.0 |
0.0 |
0.5 |
0.8 |
0.5 |
0.5 |
|
Yellow Wagtail |
Motacilla flava |
(1) |
47.5 |
0.0 |
0.0 |
0.0 |
0.8 |
9.3 |
|
Grey Wagtail |
Motacilla cinerea |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.8 |
|
Richard’s
Pipit |
Anthus richardi |
- |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
2.5 |
|
Common
Stonechat |
Saxicola torquata |
- |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
3.0 |
|
Black-browed Reed Warbler |
Acrocephalus bistrigiceps |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
|
Oriental Reed Warbler |
Acrocephalus orientalis |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
1.3 |
0.5 |
|
Zitting Cisticola |
Cisticola juncidis |
LC |
0.8 |
0.5 |
0.0 |
0.0 |
0.0 |
1.0 |
|
Yellow-billed
Grosbeak |
Eophona migratoria |
LC |
0.0 |
0.0 |
0.0 |
0.6 |
0.0 |
0.0 |
|
Red-billed Starling |
Sturnus sericeus |
GC |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
|
White-cheeked Starling |
Sturnus cineraceus |
PRC |
0.0 |
0.5 |
0.0 |
0.4 |
0.0 |
0.0 |
|
White-shouldered Starling |
Sturnus sinensis |
(LC) |
1.8 |
3.3 |
3.8 |
5.2 |
0.0 |
0.0 |
|
Black-naped
Oriole |
Oriolus chinensis |
LC |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
0.0 |
|
Collared Crow |
Corvus torquatus |
LC, NT |
0.0 |
0.3 |
0.8 |
0.0 |
2.8 |
2.5 |
|
No. of Species Recorded |
18 |
12 |
13 |
20 |
25 |
33 |
||
(1) Indicates wetland-dependant or
wetland-associated species.
(2) Conservation status follows that of Fellowes
et al. (2002) and BirdLife International listing (2010).
(3) Refers to the mean number of individuals
recorded in each survey in the Survey Area (excluding the WRA)
* Includes one species pair, Swinhoe’s/Pintail Snipe,
not distinguishable in the field. Swinhoe’s Snipe is listed as Local Concern in
Fellowes et al. (2002)
Table B2. Summary
of bird monitoring in the WRA
|
Common Name |
Scientific
Name |
Conservation |
Mean(3) |
|
Records Outside Survey(4) |
||||
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
||||
|
Little Grebe |
Tachybaptus ruficollis |
LC, (1) |
0.0 |
0.0 |
1.0 |
3.8 |
0.8 |
0.5 |
|
|
Great Cormorant |
Phalacrocorax carbo |
PRC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
|
|
Grey Heron |
Ardea cinerea |
PRC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
|
Purple
Heron |
Ardea purpurea |
RC,
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
|
Great Egret |
Egretta alba |
PRC, (1) |
0.3 |
0.5 |
0.3 |
0.0 |
1.5 |
1.8 |
|
|
Intermediate Egret |
Egretta intermedia |
RC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
1.5 |
1.5 |
|
|
Little Egret |
Egretta garzetta |
PRC, (1) |
0.8 |
0.3 |
0.3 |
1.0 |
1.0 |
0.5 |
|
|
Cattle
Egret |
Bubulcus ibis |
(LC), (1) |
0.0 |
0.3 |
11.8 |
0.0 |
1.3 |
0.3 |
|
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (1) |
0.3 |
0.3 |
1.5 |
4.2 |
7.8 |
4.5 |
|
|
Yellow
Bittern |
Ixobrychus sinensis |
(LC),
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.5 |
|
|
Mandarin
Duck |
Aix galericulata |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
|
Black Kite |
Milvus migrans |
(RC) |
0.3 |
0.0 |
0.0 |
0.0 |
0.3 |
0.0 |
|
|
White-breasted
Waterhen |
Amaurornis phoenicurus |
(1) |
0.5 |
0.8 |
1.3 |
2.6 |
1.3 |
1.5 |
|
|
Black-winged
Stilt |
Himantopus himantopus |
RC,
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
|
Little Ringed Plover |
Charadrius dubius |
LC, (1) |
5.5 |
0.5 |
0.0 |
0.2 |
0.0 |
0.0 |
|
|
Common Greenshank |
Tringa nebularia |
RC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
|
|
Green Sandpiper |
Tringa ochropus |
(1) |
0.0 |
0.0 |
0.3 |
0.0 |
0.0 |
0.0 |
|
|
Common Sandpiper |
Actitis hypoleucos |
(1) |
0.3 |
0.0 |
0.0 |
0.2 |
0.0 |
0.0 |
|
|
Pintail/Swinhoe's Snipe* |
Gallinago stenura/G. megala |
LC, (1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
|
Pied Kingfisher |
Ceryle rudis |
(LC), (1) |
0.0 |
0.3 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
Common Kingfisher |
Alcedo atthis |
(1) |
0.5 |
1.0 |
0.3 |
1.0 |
0.8 |
0.5 |
|
|
Yellow Wagtail |
Motacilla flava |
(1) |
1.8 |
0.0 |
0.0 |
0.2 |
0.8 |
1.5 |
|
|
Grey Wagtail |
Motacilla cinerea |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
0.0 |
|
|
Richard's Pipit |
Anthus richardi |
- |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
|
|
Common Stonechat |
Saxicola torquata |
- |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
|
Lanceolated
Warbler |
Locustella lanceolata |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
|
Pallas’s
Grasshopper Warbler |
Locustella certhiola |
LC,
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
|
Black-browed
Reed Warbler |
Acrocephalus bistrigiceps |
(1) |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
|
|
Zitting Cisticola |
Cisticola juncidis |
LC |
2.5 |
2.5 |
1.0 |
0.4 |
0.0 |
0.3 |
|
|
Yellow-billed
Grosbeak |
Eophona migratoria |
LC |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
|
Scaly-breasted Munia |
Lonchura punctulata |
- |
7.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
Red-billed
Starling |
Sturnus sericeus |
GC |
0.0 |
0.0 |
0.0 |
0.0 |
0.3 |
0.0 |
|
|
White-cheeked
Starling |
Sturnus cineraceus |
PRC |
0.0 |
0.0 |
0.0 |
6.6 |
0.0 |
0.0 |
|
|
White-shouldered
Starling |
Sturnus sinensis |
(LC) |
0.3 |
0.0 |
0.5 |
2.4 |
0.0 |
0.0 |
|
|
Black-naped
Oriole |
Oriolus chinensis |
LC |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
0.0 |
|
|
Collared Crow |
Corvus torquatus |
LC, NT |
0.0 |
0.3 |
0.0 |
0.8 |
0.8 |
0.8 |
|
|
Black-winged Kite |
Elanus caeruleus |
LC |
- |
- |
- |
- |
- |
- |
ü |
|
Eurasian Hobby |
Falco subbuteo |
LC |
- |
- |
- |
- |
- |
- |
ü |
|
Savanna Nightjar |
Caprimulgus affinis |
- |
- |
- |
- |
- |
- |
- |
ü |
|
Cinnamon Bittern |
Ixobrychus sinensis |
LC, (1) |
- |
- |
- |
- |
- |
- |
ü |
|
Pheasant-tailed Jacana |
Hydrophasianus chirurgus |
LC, (1) |
- |
- |
- |
- |
- |
- |
ü |
|
No. of Species
Recorded |
13 |
10 |
10 |
12 |
14 |
25 |
|
||
(1) Indicates wetland-dependant or wetland-associated
species.
(2) Conservation
status follows that of Fellowes et al.
(2002) and BirdLife International listing (2010).
(3) Refers to the mean number of individuals
recorded in each survey in the WRA
(4) Includes observation during other surveys
and/or site visits
*
Includes one species pair, Swinhoe’s/Pintail Snipe, not distinguishable in the
field. Swinhoe’s Snipe is listed as Local Concern in Fellowes et al.
(2002)
Table C1. Summary of herpetofauna monitoring within the Survey Area
(excluding the WRA)
|
Common Name |
Scientific
Name |
Conservation
Status(1) |
Mean(2) |
|
Records Outside Survey(3) |
|||||||
|
Amphibian |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
||||||
|
Asian Common Toad |
Bufo melanostictus |
- |
0.5 |
0.0 |
2.5 |
0.5 |
0.0 |
0.0 |
|
|||
|
Ornate Pigmy Frog |
Microhyla ornata |
- |
1.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|||
|
Paddy Frog |
Fejervarya
limnocharis |
- |
1.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|||
|
Günther's Frog |
Rana guentheri |
- |
8.5 |
5.5 |
2.0 |
0.5 |
0.0 |
0.0 |
|
|||
|
No. of Species
Recorded |
4 |
1 |
2 |
2 |
0 |
0 |
|
|||||
|
Reptile |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
|||||
|
Bowring’s Gecko |
Hemidactylus bowringii |
- |
1.0 |
3.5 |
0.0 |
2.0 |
0.0 |
0.0 |
|
|
||
|
Checkered
Keelback |
Xenochrophis piscator |
- |
0.0 |
0.0 |
1.0 |
0.0 |
0.0 |
0.0 |
|
|
||
|
Chinese
Soft-shelled Turtle |
Pelodiscus sinensis |
GC, VU |
- |
- |
- |
- |
- |
- |
ü |
|
||
|
Indo-Chinese
Rat Snake |
Ptyas korros |
PRC |
- |
- |
- |
- |
- |
- |
ü |
|
||
|
No. of Species
Recorded |
1 |
1 |
1 |
1 |
0 |
0 |
|
|
||||
(1) Conservation status follows that of Fellowes et al. (2002), Chan et al. (2005) and Karsen et al. (1998).
(2)
Refers to the number of individuals recorded in each month in the survey
area (excluding the WRA)
(3) Includes observation during other
surveys and/or site visits
Table C2. Summary of herpetofauna monitoring conducted in the WRA
|
Common Name |
Scientific
Name |
Conservation
Status(1) |
Mean(2) |
|
Records Outside Survey(3) |
|||||||||||
|
Amphibian |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
||||||||||
|
Ornate Pigmy Frog |
Microhyla ornata |
- |
10.0 |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
||||||
|
Paddy Frog |
Fejervarya
limnocharis |
- |
2.0 |
1.0 |
1.0 |
0.0 |
0.0 |
0.0 |
|
|
||||||
|
Günther's Frog |
Rana guentheri |
- |
10.5 |
8.0 |
2.5 |
0.5 |
0.0 |
0.0 |
|
|
||||||
|
No. of Species
Recorded |
3 |
3 |
2 |
1 |
0 |
0 |
|
|||||||||
|
Reptile |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
|||||||||
|
Bowring’s Gecko |
Hemidactylus bowringii |
- |
0.0 |
0.0 |
1.0 |
0.0 |
0.0 |
0.0 |
|
|
||||||
|
Common Rat Snake |
Ptyas mucosus |
PRC |
0.0 |
0.0 |
0.0 |
0.5 |
0.0 |
0.0 |
|
|
||||||
|
Chinese
Soft-shelled Turtle |
Pelodiscus sinensis |
GC, VU |
- |
- |
- |
- |
- |
- |
ü |
|
||||||
|
Checkered Keelback |
Xenochrophis piscator |
|
- |
- |
- |
- |
- |
- |
ü |
|
||||||
|
No. of Species
Recorded |
0 |
0 |
1 |
1 |
0 |
0 |
|
|||||||||
(1) Conservation status follows that of Fellowes et al. (2002), Chan et al. (2005) and Karsen et al. (1998).
(2)
Refers to the number of individuals recorded in each month in the WRA
(3) Includes observation during other
surveys and/or site visits
Table C3. Summary of mammal monitoring within the Study Area (excluding
the WRA)
|
Common Name |
Scientific Name |
Conservation Status(1) |
Max(2) |
|||||
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||
|
Unidentified Rat |
Rattus
sp. |
- |
0.0 |
0.0 |
1.0 |
0.0 |
0.0 |
0.0 |
|
House Mouse |
Mus musculus |
- |
0.0 |
0.0 |
0.0 |
2.0 |
0.0 |
0.0 |
|
Small Asian Mongoose |
Herpestes
javanicus |
- |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
No. of Species Recorded |
0 |
0 |
1 |
1 |
0 |
1 |
||
(1) Conservation status follows that of Fellowes et al. (2002) and Shek
(2006).
(2) Refers to the maximum number of
individuals recorded in each month in the survey area (excluding WRA).
Table C4. Summary of mammal monitoring conducted in the WRA
|
Common Name |
Scientific Name |
Conservation Status(1) |
Max(2) |
|||||
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||
|
No Records |
|
|
|
|
|
|
||
|
No. of Species Recorded |
0 |
0 |
0 |
0 |
0 |
0 |
||
(1) Conservation status follows that of Fellowes et al. (2002) and Shek
(2006).
(2) Refers to the maximum number of individuals recorded in each month in
the WRA.
Table C5. Summary of dragonfly and butterfly monitoring within the Survey Area
(excluding the WRA)
|
Common Name |
Scientific
Name |
Conservation
Status(1) |
Mean(2) |
|
|
|
|
||||
|
Odonate |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||||
|
Common Bluetail |
Ischnura senegalensis |
- |
0.5 |
20.5 |
5.0 |
0.0 |
0.0 |
0.0 |
|||
|
Common Flangetail |
Ictinogomphus pertinax |
- |
0.5 |
3.5 |
1.5 |
6.5 |
1.0 |
0.0 |
|||
|
Golden
Flangetail |
Sinictinogomphus clavatus |
- |
0.0 |
1.0 |
1.0 |
0.0 |
1.0 |
0.0 |
|||
|
Regal Pond
Cruiser |
Epophthalmia elegans |
- |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|||
|
Asian Pintail |
Acisoma panorpoides |
- |
0.0 |
1.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|||
|
Asian Amberwing |
Brachythemis contaminata |
- |
2.5 |
25.0 |
22.5 |
28.5 |
30.0 |
0.0 |
|||
|
Crimson
Darter |
Crocothemis servilia |
- |
1.0 |
2.0 |
3.0 |
4.0 |
5.0 |
0.0 |
|||
|
Blue Percher |
Diplacodes trivialis |
- |
0.0 |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
|||
|
Amber-winged Glider |
Hydrobasileus croceus |
- |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|||
|
Coastal Glider |
Macrodiplax cora |
LC |
4.5 |
10.0 |
8.0 |
9.0 |
15.0 |
0.0 |
|||
|
Green
Skimmer |
Orthetrum sabina |
- |
3.5 |
10.5 |
4.5 |
23.0 |
3.0 |
0.0 |
|||
|
Wandering
Glider |
Pantala flavescens |
- |
3.5 |
2.0 |
1.0 |
2.0 |
0.0 |
50.0 |
|||
|
Variegated
Flutterer |
Rhyothemis variegata |
- |
8.5 |
39.0 |
6.0 |
29.0 |
2.0 |
0.0 |
|||
|
Saddlebag
Glider |
Tramea virginia |
- |
0.0 |
3.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|||
|
No. of Species
Recorded |
10 |
12 |
9 |
7 |
7 |
1 |
|||||
|
Butterfly |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|||||
|
Tailed Jay
|
Graphium agamemnon |
- |
0.0 |
0.0 |
1.0 |
0.0 |
0.0 |
0.0 |
|||
|
Swallowtail
|
Papilio xuthus |
- |
0.0 |
0.0 |
0.5 |
0.0 |
0.0 |
0.0 |
|||
|
Common Mormon |
Papilio polytes |
- |
0.5 |
0.0 |
1.0 |
0.0 |
0.0 |
1.0 |
|||
|
Red-base
Jezebel |
Delias pasithoe |
- |
1.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|||
|
Indian Cabbage White |
Pieris canidia |
- |
10.0 |
1.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|||
|
Mottled Emigrant |
Catopsilia pyranthe |
- |
0.0 |
1.0 |
1.0 |
1.0 |
3.0 |
0.0 |
|||
|
Lemon Emigrant |
Catopsilia |
- |
1.5 |
3.0 |
1.0 |
0.0 |
1.0 |
0.0 |
|||
|
Common Grass Yellow |
Eurema hecabe |
- |
0.0 |
2.0 |
1.0 |
0.0 |
2.0 |
2.0 |
|||
|
Pale Grass
Blue |
Zizeeria maha |
- |
3.0 |
0.0 |
1.0 |
2.0 |
0.0 |
1.0 |
|||
|
Dark Grass Blue |
Zizeeria karsandra |
- |
1.0 |
1.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|||
|
Angled Castor |
Ariadne ariadne |
- |
0.0 |
0.0 |
0.5 |
0.5 |
0.0 |
0.0 |
|||
|
Great Egg-fly |
Hypolimnas bolina |
- |
0.0 |
0.0 |
0.0 |
0.0 |
3.0 |
0.0 |
|||
|
Common Tiger |
Danaus genutia |
- |
0.0 |
0.0 |
1.0 |
0.0 |
0.0 |
0.0 |
|||
|
No. of Species
Recorded |
6 |
5 |
9 |
3 |
4 |
3 |
|||||
(1) Conservation status follows that of Fellowes et al. (2002), Lo & Hui (2004),
Wilson (2004) and Young & Yiu (2002).
(2) Refers to the mean number of individuals recorded in each month in the survey area (excluding the WRA)
Table C6. Summary of dragonfly and butterfly monitoring conducted
in the WRA
|
Common Name |
Scientific
Name |
Conservation
Status(1) |
Mean(2) |
|||||
|
Odonate |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
||
|
Orange-tailed Sprite |
Ceriagrion
auranticum |
- |
0.0 |
0.0 |
0.0 |
0.0 |
2.0 |
0.0 |
|
Common Bluetail |
Ischnura
senegalensis |
- |
271.5 |
70.0 |
3.5 |
1.5 |
2.0 |
0.0 |
|
Pale-spotted Emperor |
Anax guttatus |
- |
0.5 |
1.0 |
1.0 |
1.0 |
1.0 |
0.0 |
|
Lesser Emperor |
Anax
parthenope |
- |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
0.0 |
|
Common Flangetail |
Ictinogomphus
pertinax |
- |
0.0 |
2.0 |
3.0 |
13.0 |
4.0 |
0.0 |
|
Golden Flangetail |
Sinictinogomphus
clavatus |
- |
0.0 |
1.0 |
0.0 |
0.0 |
2.0 |
0.0 |
|
Regal Pond Cruiser |
Epopthalmia
elegans |
- |
0.0 |
0.0 |
1.0 |
0.0 |
1.0 |
0.0 |
|
Asian Pintail |
Acisoma
panorpoides |
- |
0.0 |
1.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Blue Dasher |
Brachydiplax
chalybea |
- |
1.0 |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Asian Amberwing |
Brachythemis
contaminata |
- |
8.0 |
18.5 |
8.0 |
4.0 |
12.0 |
0.0 |
|
Crimson Darter |
Crocothemis
servilia |
- |
0.0 |
2.0 |
4.0 |
9.0 |
6.0 |
0.0 |
|
Blue Percher |
Diplacodes
trivialis |
- |
0.5 |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Coastal Glider |
Macrodiplax
cora |
LC |
0.0 |
7.0 |
3.0 |
0.0 |
3.0 |
1.0 |
|
Pied Percher |
Neurothemis
tullia |
- |
0.5 |
0.5 |
10.0 |
3.0 |
1.0 |
0.0 |
|
Green Skimmer |
Orthetrum
sabina |
- |
8.0 |
17.5 |
14.0 |
29.0 |
30.0 |
0.0 |
|
Wandering Glider |
Pantala
flavescens |
- |
5.5 |
1.0 |
3.0 |
2.0 |
10.0 |
3.0 |
|
Variegated Flutterer |
Rhyothemis
variegata |
- |
7.5 |
56.5 |
19.0 |
73.5 |
43.0 |
0.0 |
|
Saddlebag Glider |
Tramea
virginia |
- |
1.0 |
6.0 |
10.0 |
4.0 |
0.0 |
0.0 |
|
No. of Species
Recorded |
10 |
15 |
12 |
10 |
14 |
2 |
||
|
Butterfly |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
||
|
Indian Cabbage White |
Pieris
canidia |
- |
2.5 |
1.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
Mottled Emigrant |
Catopsilia
pyranthe |
- |
0.0 |
1.0 |
0.0 |
0.0 |
1.0 |
0.0 |
|
Lemon Emigrant |
Catopsilia
|
- |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
0.0 |
|
Common Grass Yellow |
Eurema
hecabe |
- |
0.0 |
0.0 |
5.0 |
3.0 |
3.0 |
2.0 |
|
Pale Grass Blue |
Zizeeria
maha |
- |
0.5 |
0.0 |
0.0 |
1.0 |
0.0 |
0.0 |
|
Common Evening Brown |
Melanitis
leda |
- |
0.0 |
0.0 |
2.0 |
0.0 |
0.0 |
0.0 |
|
Dark-brand Bush Brown |
Mycalesis
mineus |
- |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
1.0 |
|
Blue-spotted Crow |
Euploea
midamus |
- |
0.5 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
No. of Species
Recorded |
4 |
2 |
2 |
2 |
3 |
2 |
||
(1) Conservation status follows that of Fellowes et al. (2002), Lo & Hui (2004),
Wilson (2004) and Young & Yiu (2002).
(2) Refers to the mean number of individuals recorded in each month in the WRA
Table D1. Water quality at WRA
May 2011
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turb (mg/L) |
DO (mg/L) |
|
1 |
28.5 |
6.77 |
3.35 |
18 |
3.96 |
|
2 |
27.4 |
6.73 |
3.64 |
7 |
3.34 |
|
3 |
29.6 |
7.30 |
3.71 |
17 |
4.82 |
|
4 |
29.6 |
6.60 |
4.79 |
12 |
3.37 |
June 2011
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turb (mg/L) |
DO (mg/L) |
|
1 |
32.9 |
7.36 |
1.85 |
14 |
5.07 |
|
2 |
33.7 |
7.42 |
3.06 |
5 |
5.32 |
|
3 |
33.0 |
7.66 |
2.13 |
14 |
5.27 |
|
4 |
32.9 |
7.51 |
3.24 |
9 |
3.81 |
July 2011
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turb (mg/L) |
DO (mg/L) |
|
1 |
31.7 |
7.03 |
1.64 |
(1) |
1.59 |
|
2 |
32.3 |
7.57 |
1.89 |
(1) |
1.19 |
|
3 |
32.4 |
7.42 |
1.85 |
(1) |
2.12 |
|
4 |
32.9 |
7.11 |
2.02 |
(1) |
4.57 |
August 2011
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turb (mg/L) |
DO (mg/L) |
|
1 |
32.2 |
7.25 |
0.95 |
(1) |
1.55 |
|
2 |
31.6 |
7.08 |
1.22 |
(1) |
1.02 |
|
3 |
31.9 |
7.30 |
1.07 |
(1) |
3.03 |
|
4 |
32.9 |
6.92 |
1.32 |
(1) |
2.55 |
September 2011
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turb (mg/L) |
DO (mg/L) |
|
1 |
32.5 |
7.35 |
0.86 |
(1) |
1.88 |
|
2 |
31.7 |
7.39 |
1.02 |
(1) |
1.74 |
|
3 |
32.0 |
7.41 |
1.03 |
(1) |
3.20 |
|
4 |
32.4 |
7.25 |
1.26 |
(1) |
2.99 |
October 2011
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turb (mg/L) |
DO (mg/L) |
|
1 |
24.8 |
7.53 |
0.91 |
7 |
3.52 |
|
2 |
25.3 |
7.58 |
1.22 |
5 |
3.68 |
|
3 |
25.2 |
7.94 |
1.08 |
10 |
5.37 |
|
4 |
26.0 |
7.39 |
1.29 |
3 |
3.80 |
(1) The turbidity
water quality checker was under repair.
Notes:
Values Bold
indicate Action Level exceedance.
Values Underlined
and Bold indicate Limit Level exceedance.