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Issue and revision record |
This document is
issued for the party which commissioned it and for specific purposes
connected with the above-captioned project only. It should not be relied
upon by any other party or used for any other purpose. |
We accept no
responsibility for the consequences of this document being relied upon by
any other party, or being used for any other purpose, or containing any
error or omission which is due to an error or omission in data supplied to
us by other parties. This document
contains confidential information and proprietary intellectual property. It
should not be shown to other parties without consent from us and from the
party which commissioned it.. |
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Date |
Originator |
Checker |
Approver |
Description |
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A |
May
2014 |
Brandon
Wong |
Terence Kong |
Eric Ching |
Issue
to Client |
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Contents |
Chapter Title Page
Tables
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Table 1.1:__ Summary of Ecological Impact
EM&A Requirements Table 4.1:__ Summary of Ecological
Monitoring in WRA and Survey Area |
List of Figures
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 Quality Monitoring
In March 2005, the Project Proponent, Profit Point Enterprises Limited, acquired the development site at Wo Shang Wai in Yuen Long. An Environmental Impact Assessment (EIA) was then carried out and approved under the EIA Ordinance (EIAO), and the Environmental Permit (EP) for construction of the comprehensive development in Wo Shang Wai was first granted by Environmental Protection Department (EPD) on 9 September 2008 (EP-311/2008) and has been subsequently varied, with the current version (EP-311/2008/D) issued by EPD on 20 March 2013.
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. The site formation construction works of the Wetland Restoration Area (hereafter WRA) were completed on 15 November 2010, while the 30-month establishment period of the WRA was concluded in October 2012 – this indicated that planting works as scheduled in the approved Wetland Restoration and Creation Scheme (WRCS; Nov 2009) were complete, except along the western and southern boundary where the planting is affected by the existing site boundary and noise barrier, and for which a Variation to Environmental Permit (EP-311/2008/C) to defer planting at the location was approved. This factor remains applicable in the current valid EP (EP-311/2008/D) which also includes specific mitigation measures to minimise certain identified noise impacts during the operation phase of the Project.
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 Advisory Council on the Environment (ACE), EPD and Agriculture, Fisheries and Conservation Department (AFCD) on a biannual basis. This is the 8th Biannual EM&A report and it summarises the findings on EM&A results of ecological aspects during the period from 1 November 2013 to 30 April 2014. This report documents surveys and management activities conducted in the Survey Area and WRA from 1 November 2013 to 30 April 2014, which is based on ecological surveys and advices on management which were undertaken by the appointed ecological consultant (Green Power/Ecological Resource Centre) during the reporting period.
Surveys
were conducted within 500m of
the Project area. The
WRA was surveyed since early September 2010. The survey area and transect are
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 Nov, and twice per month during Apr to Aug |
|
Herpetofauna |
Within the Project Area and Assessment Area of 500m |
Daytime: Once per month during Apr to Nov Night-time: Once per month during Mar to Aug |
|
Water quality of Wetland Restoration Area (WRA) |
WRA |
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 and frequency outlined in the
EM&A Manual (Table 7-1). Since September 2010, monitoring included the
newly formed cells to monitor faunal usage of this area. 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 throughout the period. A total of 64 bird species were recorded in the
Survey Area (excluding the WRA) in November 2013 to April 2014, 37 of which were species of
conservation importance and/or wetland-dependence. A summary of survey
data is provided in Appendix B.
A total of 63 species were recorded in the WRA in
the survey periods, 34 of which were species of conservation importance and/or
wetland-dependent species. Of all three target species (i.e. Little Egret (Egtretta garzetta), Eastern Cattle Egret
(Bubulcus coromandus) and Chinese
Pond Heron (Ardeola bacchus)), all of
them were recorded in the WRA. The
WRA has attracted a number of species of conservation interest, including Yellow Bittern, Ixobrychus
sinensis (this species is listed by Fellowes et al. as of “Local Concern” in 2002), Black-faced Spoonbill, Platalea
minor (this is an
endangered species which also listed by Fellowes et al. as of “Potential Global Concern” in 2002), and one local
concern wetland dependence species, Black-crowned Night Heron, Nycticorax nycticorax, indicating that
the WRA was effective in providing habitat suitable for species of interest.
Outside routine surveys, a
Eurasian Eagle Owl, Bubo bubo, was observed in the WRA, indicating that the WRA was effective in
providing habitat suitable for species of interest.
The fishponds to the north of the WRA are at a greater distance from the residential portion and any disturbance impact(s) from the construction works which would have first affected the WRA. Further, 34 bird species of conservation importance and/or wetland-dependence, were observed using the under review, including some bird species which are highly sensitive to disturbance and three target species (i.e. Little Egret, Eastern Cattle Egret and Chinese Pond Heron). Thus, the WRA is considered to be effective both in acting as a buffer against potential disturbance impacts from the construction site and in providing suitable wetland habitats and the fringe of the Deep Bay system.
Monitoring was undertaken following the survey methodology in the EM&A Manual. Day-time herpetofauna surveys were conducted once per month in November 2013 and April 2014. Further, notable herpetofauna observations during other surveys were also recorded.
No herpetofauna species were recorded in the survey area (excluding WRA)
in the survey period.
Gunther's Frog, Rana guentheri, and Chinese Bull
Frog, Hoplobatrachus chinensis, were
recorded during the survey period within the WRA. Chinese Bull Frog is listed by Fellowes et al. as of “Potential Regional
Concern” in 2002. A summary of survey data is provided in Appendix C.
Monitoring of dragonflies and butterflies was conducted once per
month in November 2013 and March 2014 and twice per month in April 2014. Further, notable dragonfly and butterfly observations during
other surveys were recorded.
A total of four dragonfly
species and two butterfly species were recorded using the ponds in the survey area (excluding WRA) in the
survey period. At the WRA, a
higher diversity of dragonfly species (10 species) and butterfly species (7 species) were recorded. A
summary of the survey findings is provided in Appendix C.
Monitoring of mammals was conducted concurrently with other surveys. No mammal was recorded in
the Survey Area within the survey period.
Japanese Pipistrelle, Pipistrellus
abramus, was recorded in the WRA
during regular survey. A summary of the survey findings is provided in Appendix C.
Monthly
water quality monitoring continued during the reporting period. Monitoring
parameters followed that in the EM&A Manual. During the reporting period, the pH of Cell 2 and 4 in November
2013 reached Action Levels,
but returned to acceptable levels in the following month. Monitoring data are presented in Appendix D.
Vegetation management activities undertaken at the site
primarily involved watering of plants,
tree pruning, weeding and grass cutting.
Removal of exotic vegetation in all cells was undertaken;
these included but not limited to Ipomoes
sp., Mikania sp., Mimosa
sp., Pennisetum sp. and
Typha sp..
Golden Apple Snails were removed on an “as-seen” basis.
All fire ant nests were treated with an approved pesticide and covered with overturn baskets for a week. All treated fire ant nests were inactive within one week of treatment.
Ecological
monitoring between 1 November 2013 and 30 April 2014 was carried out following the survey
methodology and frequency outlined in the EM&A Manual.
Summary of
survey findings are listed as follows (Table
4.1):
Table 4.1: Summary of Ecological Monitoring in WRA and Survey Area
|
Species |
Number recorded in Survey Area (excluding WRA) |
Number recorded in WRA |
|
Birds (total) |
64 |
63 |
|
Birds (of
conservation importance and/or wetland-dependence) |
37 |
34 |
|
Amphibians |
0 |
2 |
|
Reptiles |
0 |
0 |
|
Mammals |
0 |
1 |
|
Dragonflies |
4 |
10 |
|
Butterflies |
2 |
7 |
A total of 63 bird
species, 2 amphibian species, 1 mammal
species, 10 dragonfly
species and 7 butterfly species
were recorded in the WRA, including 34
bird species of conservation importance and/or wetland-dependence, while all
dragonfly species are wetland-dependent. These findings indicate that the WRA is supporting wetland-dependent
birds and other species of conservation importance.
Survey findings indicate that the WRA is attracting the three target species to varying degrees. During the survey period (i.e. November 2013 to April 2014), the site was particularly attractive to Little Egret, which was recorded on nearly-weekly basis, with monthly means ranging from 1.4 to 4.4 birds per survey. Chinese Pond Heron was also recorded every month in regular survey under review (November 2013 to April 2014) with monthly means ranging from 1.0 to 6.8 bird per survey. Eastern Cattle Egret was least attracted to the site, Eastern Cattle Egret was only recorded in April under review period (May 2013 to October 2013), with monthly means 1.6 birds per survey.
With the completion of planting as scheduled in the approved HCMP in August 2012, establishment work at the WRA is considered complete (except along the western and southern boundary where the planting is affected by the existing site boundary and noise barrier, and for which a previous Variation to Environmental Permit (EP-311/2008/C) to defer planting at the location was approved by EPD and remains applicable in the current valid EP (EP-311/2008/D)), and the 30-month establishment period concluded in October 2012. A review of the performance of the WRA in terms of target species attraction during and after the 30-month establishment period is provided in Section 4.2 below.
It should be noted that the high planting density was intended to ensure a rapid establishment of the site prior to occupation intake, and not intended to be maintained as a long-term tree density at the WRA. It is a standard arboricultural practice to apply appropriate horticultural/arboricultural maintenance methods in the subsequent five or six years after initial planting to remove less desired specimens to facilitate the successful growth of those which are of higher landscape and/or ecological value. Further, some fine tuning of planting locations and tree/shurb mix is required in order to fulfill the design intent of the habitat structure at WRA after reviewing the site configuration following site formation. Vegetation management hereafter should largely consist of maintenance of planted trees and shrubs for the creation of suitable habitats for target species and long-term habitat structure of the site.
The provision,
maintenance and operation of a WRA are a requirement under the Environmental
Permit for compensation for predicted ecological impacts to species of
conservation importance. Three bird target species were identified during the
EIA process; they are Little Egret, Eastern Cattle Egret and Chinese Pond
Heron. Target levels of these species are the annual mean number recorded
during the Baseline Ecological Monitoring (i.e. a mean of 5.5 Little Egret, 1.3
Eastern Cattle Egret and 1.3 Chinese Pond Heron over a 12 month period) thus,
the ecological impact of the project to the species concerned is considered to
have been fully compensated when the target level for each of the three species
is achieved. Whilst further discussion and agreement regarding the target level
is yet to be undertaken with the relevant Government departments prior to the
operation of the WRA, the proposed level offers a clear reference to the
effectiveness of the mitigation measures. According to the approved Wetland
Creation and Restoration Scheme (Nov 2009, hereafter WCRS), the WRA was anticipated
to be fully operational after an establishment period of 2.5 years (30 months).
Of all three target
species, all of them were recorded using the site under review period (November
2013 – April 2014). Among all target species, Little Egret and Chinese Pond
Heron were recorded in all six months and Eastern Cattle Egret was recorded in
one month during the reporting period. Table 4.2 below presents the target
level achievement of the three target bird species during and after the
establishment period.
Table 4.2: Annual Mean of the Three Bird Target Species Recorded at the WRA between May 2013 and Apr 2014
|
Common Name |
Scientific Name |
Conservation Status (2) |
Annual mean number recorded during the Baseline Ecological Monitoring |
May 2013 – Apr 2014 * |
|
Little Egret |
Egretta garzetta |
PRC, (RC) |
5.5 |
2.3 |
|
Eastern Cattle Egret |
Bubulcus coromandus |
(LC) |
1.3 |
0.1 |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (RC) |
1.3 |
1.9 |
Note:
(1) Values in bold indicate that the Target Level was achieved.
(2) Conservation Status follows that of Fellowes et. al. (2002). See Appendix B (Table B3).
* The mean number of the target species was calculated in annual basis.
Based on Table 4.2 above, the target levels for
Little Egret and Eastern Cattle Egret have not been achieved between May 2013
and April 2014. As the Proposed Comprehensive Development at Wo Shang Wai is
still under construction phase, it is considered acceptable. However, should this situation continue, a
review of the management of the WRA and adaptive management steps will be
required.
Preliminarily actions
will be taken to increase the WRA utilization by birds, results of these
actions will be closely monitored. The mitigation
actions are:
1. Lowering the water level;
2. Restocking the Cell in the WRA;
3. Installing flooding platform; and
4. Controlling the vegetation
A total of 108
bird species have been recorded within the WRA since completion of site
formation. Of the 108 species, 71 were species of conservation importance
and/or wetland dependence - indicating that the WRA provides suitable habitat
for these species despite the construction work within the residential portion
of the Project Site. A list of the bird species recorded at the WRA since
completion of site formation is provided in Appendix B
(Table B4 & B5).
The site
continuously attracts bird species of conservation importance, indicating that
the WRA not only provides a buffer for potential disturbance during
construction phase, it is also a valuable habitat for wetland dependent species
and 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 Hong Kong. Cosmos Books Ltd., Hong Kong.
Fellowes et
al., 2002. Wild Animals to Watch: Terrestrial and Freshwater Fauna of
Conservation Concern in Hong Kong.
Karsen, S., M.W.N. Lau &
A. Bogadek, 1998. Hong Kong Amphibians and Reptiles. Provisional Urban Council, Hong Kong.
IUCN 2011. IUCN Red List of Threatened Species.
Version 2011.1. <www.iucnredlist.org>.
Downloaded on 07 October 2011.
Lo, P. Y. F. and W.L. Hui, 2004. Hong Kong
Butterflies. Hong Kong, Cosmos Books Ltd.
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 Hong Kong. Friends of
the Country Parks Cosmos Books Ltd., Hong Kong.
Tam, T. W., K.K. Leung,
B.S.P. Kwan, K.K.Y. Wu, S.S.H. Tang, I.W.Y. So, J.C.Y. Cheng, E.F.M. Yuen, Y.M. Tsang, and W.L. Hui, 2011. The Dragonflies of Hong Kong (1st
edition). Agriculture, Fisheries and Conservation Department. Friends of
Country Parks and Cosmos Books Ltd., Hong Kong.
Young, J.J. & Yiu, V., 2002. Butterfly Watching In Hong Kong.
Wan Li Book Co. Ltd., Hong Kong.
|
Appendix A. Schedule of Ecological Monitoring |
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Nov 2013 |
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Mammals |
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Dragonflies & Butterflies |
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Inspection Visits |
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Dec 2013 |
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Water Quality |
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Jan 2014 |
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Feb 2014 |
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Water Quality |
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Inspection Visits |
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Mar 2014 |
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Apr 2014 |
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Note:
1. Light grey cells indicate public holidays,
Saturdays or Sundays.
2. Dark cells indicate that no survey was
required during the relevant month.
|
Appendix
B. Summary of Bird Surveys |
Table B1. Summary of bird monitoring (for species of conservation importance and/or wetland-dependence) within the Survey Area (excluding the WRA)
|
Common Name (4) |
Scientific Name (4) |
Conservation Status (2) |
Nov Mean (3) |
Dec Mean (3) |
Jan Mean (3) |
Feb Mean (3) |
Mar Mean (3) |
Apr Mean (3) |
|
Little
Grebe |
Tachybaptus ruficollis |
LC, (1) |
10.0 |
8.6 |
5.6 |
6.3 |
5.0 |
3.6 |
|
Great
Cormorant |
Phalacrocorax carbo |
PRC, (1) |
8.4 |
8.0 |
3.4 |
5.3 |
3.5 |
|
|
Grey
Heron |
Ardea cinerea |
PRC, (1) |
8.8 |
5.4 |
4.6 |
3.0 |
0.8 |
0.2 |
|
Great
Egret |
Egretta alba |
PRC, (RC), (1) |
4.0 |
4.0 |
3.8 |
3.0 |
16.3 |
3.0 |
|
Little
Egret |
Egretta garzetta |
PRC, (RC), (1) |
17.8 |
9.8 |
9.6 |
13.5 |
67.5 |
23.2 |
|
Eastern
Cattle Egret |
Bubulcus coromandus |
LC, (1) |
|
|
|
|
0.3 |
9.0 |
|
Chinese
Pond Heron |
Ardeola bacchus |
PRC, (RC), (1) |
9.6 |
4.0 |
8.4 |
6.8 |
6.0 |
7.0 |
|
Black-crowned
Night Heron |
Nycticorax nycticorax |
(LC), (1) |
|
0.2 |
|
|
|
0.2 |
|
Yellow
Bittern |
Ixobrychus sinensis |
LC, (1) |
0.2 |
|
|
|
|
|
|
Black-faced
Spoonbill |
Platalea minor |
PGC, (1) |
0.6 |
|
V |
2.0 |
2.5 |
|
|
Northern
Shoveler |
Anas clypeata |
RC, (1) |
|
1.2 |
5.8 |
|
|
|
|
Tufted
Duck |
Aythya fuligula |
LC, (1) |
|
2.8 |
13.0 |
18.3 |
16.3 |
|
|
Black
Kite |
Milvus migrans |
RC, (1) |
|
0.2 |
0.2 |
0.5 |
0.5 |
|
|
Common
Kestrel |
Falco tinnunculus |
(-) |
|
V |
|
|
|
|
|
Peregrine
Falcon |
Falco peregrinus |
LC |
|
V |
|
|
|
|
|
White-breasted
Waterhen |
Amaurornis phoenicurus |
(1) |
1.0 |
1.6 |
V |
0.5 |
0.3 |
0.6 |
|
Common
Moorhen |
Gallinula chloropus |
(1) |
0.8 |
0.4 |
|
0.5 |
0.3 |
0.6 |
|
Black-winged
Stilt |
Himantopus himantopus |
(RC), (1) |
0.6 |
|
|
|
|
|
|
Pied
Avocet |
Recurvirostra avosetta |
RC, (1) |
4.6 |
V |
|
|
|
|
|
Little
Ringed Plover |
Charadrius dubius |
(LC), (1) |
7.0 |
0.8 |
|
1.0 |
1.3 |
0.2 |
|
Kentish
Plover |
Charadrius alexandrinus |
RC, (1) |
1.8 |
V |
|
|
|
|
|
Green
Sandpiper |
Tringa ochropus |
(1) |
|
|
0.2 |
|
|
0.8 |
|
Wood
Sandpiper |
Tringa glareola |
(LC), (1) |
|
|
|
|
|
0.2 |
|
Common
Sandpiper |
Actitis hypoleucos |
(1) |
4.0 |
2.0 |
1.6 |
3.5 |
3.0 |
2.6 |
|
Common
Snipe |
Gallinago gallinago |
(1) |
|
|
|
|
|
0.2 |
|
Black-headed
Gull |
Larus ridibundus |
PRC, LC, (1) |
|
|
|
|
1.3 |
|
|
Whiskered
Tern |
Chlidonias hybrida |
LC, (1) |
|
|
|
0.8 |
1.5 |
0.2 |
|
Eurasian
Eagle Owl |
Bubo bubo |
RC |
|
|
|
V |
|
|
|
Pied
Kingfisher |
Ceryle rudis |
(LC), (1) |
0.2 |
0.4 |
|
0.3 |
0.8 |
0.4 |
|
White-throated
Kingfisher |
Halcyon smyrnensis |
LC, (1) |
0.2 |
0.6 |
0.2 |
0.5 |
V |
|
|
Common
Kingfisher |
Alcedo atthis |
(1) |
2.2 |
1.6 |
1.0 |
0.5 |
1.0 |
2.4 |
|
Eastern
Yellow Wagtail |
Motacilla tschutschensis |
(1) |
1.6 |
2.6 |
3.2 |
2.0 |
2.3 |
5.8 |
|
White
Wagtail |
Motacilla alba |
(1) |
10.4 |
11.0 |
8.2 |
11.8 |
6.5 |
7.4 |
|
Richard's
Pipit |
Anthus richardi |
(1) |
|
|
1.6 |
0.8 |
1.0 |
1.6 |
|
Red-billed
Starling |
Spodiopsar sericeus |
(1) |
|
2.6 |
5.4 |
6.8 |
1.3 |
0.8 |
|
White-cheeked
Starling |
Spodiopsar cineraceus |
PRC, (1) |
0.2 |
|
|
|
|
|
|
Collared
Crow |
Corvus torquatus |
LC, (1) |
0.8 |
0.4 |
|
|
0.5 |
1.6 |
|
|
|
No. of species recorded |
22 |
25 |
19 |
22 |
24 |
22 |
Note:
(1) Indicates wetland-dependent or wetland-associated species.
(2) Conservation status follows that of Fellowes et al. (2002) and BirdLife International listing (2010). See Table B3.
(3) Refers to the mean number of individuals recorded in each survey in the Survey Area (excluding the WRA).
(4) Follows HK bird list (dated 2013-3-25).
(5) “V” indicates the species is recorded outside regular surveys.
Table B2. Summary of bird monitoring (for species of conservation importance and/or wetland-dependence) in the WRA
|
Common Name (4) |
Scientific Name (4) |
Conservation Status (2) |
Nov Mean (3) |
Dec Mean (3) |
Jan Mean (3) |
Feb Mean (3) |
Mar Mean (3) |
Apr Mean (3) |
|
Little Grebe |
Tachybaptus
ruficollis |
LC, (1) |
0.6 |
2.2 |
1.8 |
5.3 |
4.5 |
2.4 |
|
Great Cormorant |
Phalacrocorax
carbo |
PRC, (1) |
V |
0.4 |
0.6 |
0.5 |
|
|
|
Grey Heron |
Ardea cinerea |
PRC, (1) |
2.8 |
2.6 |
1.6 |
2.5 |
|
|
|
Great Egret |
Egretta alba |
PRC, (RC), (1) |
0.6 |
2.4 |
1.2 |
1.8 |
0.8 |
0.2 |
|
Intermediate Egret |
Egretta
intermedia |
RC, (1) |
|
|
|
V |
|
|
|
Little Egret |
Egretta garzetta |
PRC, (RC), (1) |
1.4 |
2.4 |
4.4 |
4.0 |
3.8 |
3.2 |
|
Eastern Cattle Egret |
Bubulcus
coromandus |
LC, (1) |
|
|
|
|
|
1.6 |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (RC), (1) |
1.4 |
2.6 |
6.8 |
3.5 |
2.5 |
1.0 |
|
Black-crowned Night Heron |
Nycticorax
nycticorax |
(LC), (1) |
|
|
|
|
V |
|
|
Yellow Bittern |
Ixobrychus
sinensis |
LC, (1) |
0.4 |
0.2 |
|
|
V |
V |
|
Black-faced Spoonbill |
Platalea minor |
PGC, (1) |
|
|
|
V |
V |
|
|
Northern Shoveler |
Anas clypeata |
RC, (1) |
|
1.2 |
7.0 |
5.5 |
V |
|
|
Black Kite |
Milvus migrans |
RC, (1) |
0.2 |
|
V |
0.5 |
0.8 |
0.4 |
|
Crested Serpent Eagle |
Spilornis cheela |
(LC) |
|
|
|
V |
|
|
|
White-breasted Waterhen |
Amaurornis
phoenicurus |
(1) |
0.4 |
|
|
|
V |
0.2 |
|
Common Moorhen |
Gallinula
chloropus |
(1) |
|
|
|
|
V |
0.2 |
|
Black-winged Stilt |
Himantopus
himantopus |
(RC), (1) |
V |
|
|
|
|
|
|
Little Ringed Plover |
Charadrius
dubius |
(LC), (1) |
0.4 |
|
V |
0.5 |
0.8 |
|
|
Common Greenshank |
Tringa nebularia |
LC, (1) |
|
V |
|
|
V |
|
|
Green Sandpiper |
Tringa ochropus |
(1) |
0.6 |
V |
V |
|
0.5 |
|
|
Wood Sandpiper |
Tringa glareola |
(LC), (1) |
V |
V |
V |
V |
V |
|
|
Common Sandpiper |
Actitis
hypoleucos |
(1) |
1.6 |
0.2 |
V |
0.3 |
1.3 |
0.2 |
|
Pintail Snipe |
Gallinago
stenura |
(1) |
V |
|
|
|
|
|
|
Eurasian Eagle Owl |
Bubo bubo |
RC |
V |
|
|
V |
|
|
|
Pied Kingfisher |
Ceryle rudis |
(LC), (1) |
|
0.4 |
V |
0.3 |
V |
|
|
White-throated Kingfisher |
Halcyon
smyrnensis |
LC, (1) |
|
0.2 |
|
|
|
|
|
Common Kingfisher |
Alcedo atthis |
(1) |
2.0 |
1.6 |
1.2 |
2.3 |
0.8 |
1.0 |
|
Eastern Yellow Wagtail |
Motacilla
tschutschensis |
(1) |
0.2 |
0.6 |
0.6 |
1.0 |
0.3 |
0.2 |
|
White Wagtail |
Motacilla alba |
(1) |
3.6 |
2.6 |
1.2 |
1.3 |
2.5 |
1.6 |
|
Richard's Pipit |
Anthus richardi |
(1) |
|
0.4 |
0.8 |
2.0 |
2.3 |
3.0 |
|
Zitting Cisticola |
Cisticola
juncidis |
LC, (1) |
|
|
0.4 |
|
0.3 |
1.2 |
|
Chinese Penduline Tit |
Remiz
consobrinus |
RC, (1) |
|
V |
|
4.5 |
V |
|
|
Red-billed Starling |
Spodiopsar
sericeus |
(1) |
|
|
|
V |
|
|
|
Collared Crow |
Corvus torquatus |
LC, (1) |
0.2 |
|
|
V |
0.5 |
0.8 |
|
|
|
No. of species recorded |
21 |
20 |
18 |
22 |
24 |
16 |
Note:
(1) Indicates wetland-dependent or wetland-associated species.
(2) Conservation status follows that of Fellowes et al. (2002) and BirdLife International listing (2010). See Table B3.
(3) Refers to the mean number of individuals recorded in each survey in the Survey Area (excluding the WRA)
(4) Follows HK bird list (dated 2013-3-25)
V Indicates the species is recorded outside regular surveys.
Table B3. Conservation Status Categories of Bird Species
|
Code |
Category |
Brief/Description |
Source |
|
GC |
Global Concern |
Habitat loss/damage in |
Fellowes et al. (2002) |
|
RC |
Regional Concern |
Habitat loss/damage in |
|
|
LC |
Local Concern |
Habitat loss/damage in |
|
|
PGC |
Potential Global Concern |
Large, secure population in |
|
|
PRC |
Potential Regional Concern |
Large, secure population in |
|
|
CR |
Critically Endangered |
Best available evidence indicates that it meets any
of the criteria A to E for Critically Endangered, and it is therefore
considered to be facing an extremely high risk of extinction in the wild. |
BirdLife International (2010) |
|
EN |
Endangered |
Best available evidence indicates that it meets any
of the criteria A to E for Endangered, and it is therefore considered to be
facing a very high risk of extinction in the wild. |
|
|
VU |
Vulnerable |
Best available evidence indicates that it meets any
of the criteria A to E for Vulnerable, and it is therefore considered to be
facing a high risk of extinction in the wild. |
|
|
NT |
Near Threatened |
Does not qualify for Critically Endangered,
Endangered or Vulnerable now, but is close to qualifying for or is likely to
qualify for a threatened category in the near future. |
Table B4. Summary of
Bird Species Recorded at the WRA and their Respective Monthly Mean between
September 2010 and October 2012
|
Common name |
Scientific name |
Conservation status |
Sep-10 |
Oct-10 |
Nov-10 |
Dec-10 |
Jan-11 |
Feb-11 |
Mar-11 |
Apr-11 |
May-11 |
Jun-11 |
Jul-11 |
Aug-11 |
Sep-11 |
Oct-11 |
Nov-11 |
Dec-11 |
Jan-12 |
Feb-12 |
Mar-12 |
Apr-12 |
May-12 |
Jun-12 |
Jul-12 |
Aug-12 |
Sep-12 |
Oct-12 |
|
Little
Grebe |
Tachybaptus ruficollis |
LC,
(1) |
|
|
|
|
0.5 |
|
|
|
|
|
1.0 |
3.8 |
0.8 |
0.5 |
0.5 |
|
0.6 |
|
1.4 |
1.6 |
0.8 |
1.0 |
1.3 |
0.2 |
|
0.2 |
|
Great
Cormorant |
Phalacrocorax carbo |
PRC,
(1) |
|
|
|
|
0.8 |
|
|
|
|
|
|
|
|
0.3 |
0.3 |
0.4 |
1.2 |
0.7 |
0.2 |
|
|
|
|
|
|
|
|
Grey
Heron |
Ardea cinerea |
PRC,
(1) |
|
|
1.0 |
1.6 |
2.0 |
2.0 |
0.4 |
|
|
|
|
|
|
1.0 |
2.5 |
1.8 |
0.8 |
2.3 |
0.8 |
|
|
|
0.3 |
|
|
0.4 |
|
Purple
Heron |
Ardea purpurea |
RC,
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
Great
Egret |
Ardea alba |
PRC,
(1) |
|
|
|
0.4 |
14.0 |
2.0 |
0.2 |
0.5 |
0.3 |
0.5 |
0.3 |
|
1.5 |
1.8 |
0.8 |
1.2 |
0.6 |
0.7 |
0.6 |
0.6 |
1.0 |
0.3 |
|
0.4 |
0.5 |
1.5 |
|
Intermediate
Egret |
Egretta intermedia |
RC,
(1) |
|
|
|
|
1.7 |
0.8 |
0.2 |
|
|
|
|
|
1.5 |
1.5 |
1.5 |
1.0 |
0.6 |
0.7 |
0.6 |
0.6 |
|
|
|
|
0.3 |
0.9 |
|
Little
Egret |
Egretta garzetta |
PRC,
(1) |
|
|
|
1.8 |
8.0 |
2.0 |
0.4 |
0.5 |
0.8 |
0.3 |
0.3 |
1.0 |
1.0 |
0.5 |
1.5 |
1.6 |
1.4 |
2.0 |
1.6 |
|
|
|
|
0.8 |
0.3 |
1.2 |
|
Eastern
Cattle Egret |
Bubulcus coromandus |
(LC),
(1) |
|
|
|
|
|
|
|
|
|
0.3 |
11.8 |
|
1.3 |
0.3 |
|
|
0.4 |
|
|
|
|
0.3 |
|
0.2 |
|
|
|
Chinese
Pond Heron |
Ardeola bacchus |
PRC,
(1) |
|
|
1.0 |
0.2 |
|
|
|
0.3 |
0.3 |
0.3 |
1.5 |
4.2 |
7.8 |
4.5 |
5.3 |
2.4 |
0.3 |
2.3 |
2.6 |
1.4 |
0.8 |
1.0 |
0.8 |
2.0 |
1.8 |
2.2 |
|
Yellow
Bittern |
Ixobrychus sinensis |
(LC),
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
Black-crowned
Night Heron |
Nycticorax nycticorax |
LC,
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian
Spoonbill |
Platalea leucorodia |
LC,
(1) |
|
|
|
|
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|
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|
|
Black-faced
Spoonbill |
Platalea minor |
PGC,
EN, (1) |
|
|
|
|
0.3 |
10.3 |
|
|
|
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|
|
|
|
|
|
0.4 |
|
|
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|
Mandarin
Duck |
Aix galericulata |
(1) |
|
|
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|
0.3 |
|
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|
|
Eurasian
Wigeon |
Anas penelope |
RC,
(1) |
|
|
|
1.6 |
2.5 |
|
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|
Eurasian
Teal |
Anas crecca |
RC,
(1) |
|
|
|
|
1.0 |
|
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|
Northern
Pintail |
Anas acuta |
RC,
(1) |
|
|
|
0.2 |
7.0 |
|
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|
Northern
Shoveler |
Anas clypeata |
RC,
(1) |
|
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|
Tufted
Duck |
Aythya fuligula |
LC,
(1) |
|
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Garganey |
Anas querquedula |
(1) |
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|
Western
Osprey |
Pandion haliaetus |
RC,
(1) |
|
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|
0.2 |
|
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|
Black
Kite |
Milvus migrans |
(RC) |
|
|
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|
0.8 |
0.3 |
0.2 |
|
0.3 |
|
|
|
0.3 |
|
|
|
0.2 |
|
|
0.2 |
0.5 |
|
|
|
|
0.4 |
|
Crested
Serpent Eagle |
Spilornis cheela |
(LC) |
|
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|
Eastern
Buzzard |
Buteo japonicus |
- |
|
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|
0.2 |
|
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|
Common
Kestrel |
Falco tinnunculus |
- |
|
|
1.0 |
0.4 |
1.0 |
0.3 |
0.4 |
|
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|
Eurasian
Hobby |
Falco subbuteo |
(LC),
(1) |
|
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Peregrine
Falcon |
Falco peregrinus |
- |
|
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|
Imperial
Eagle |
Aquila heliaca |
- |
|
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Japanese Quail |
Coturnix japonica |
LC,
(1) |
|
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White-breasted
Waterhen |
Amaurornis phoenicurus |
(1) |
|
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|
0.5 |
0.8 |
1.3 |
2.6 |
1.3 |
1.5 |
0.3 |
|
|
|
0.4 |
|
|
0.5 |
1.0 |
0.5 |
|
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|
Common Moorhen |
Gallinula chloropus |
(1) |
|
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|
0.2 |
|
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Pheasant-tailed
Jacana |
Hydrophasianus chirurgus |
LC,
(1) |
|
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|
0.3 |
|
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|
Greater
Painted-snipe |
Rostratula benghalensis |
LC,
(1) |
|
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|
0.5 |
|
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|
Black-winged
Stilt |
Himantopus himantopus |
RC,
(1) |
8.0 |
|
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|
1.0 |
|
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|
Pied Avocet |
Recurvirostra avosetta |
RC,
(1) |
|
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|
0.2 |
|
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|
0.2 |
|
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|
Oriental
Pratincole |
Glareola maldivarum |
LC,
(1) |
|
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|
2.5 |
|
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|
Little
Ringed Plover |
Charadrius dubius |
LC,
(1) |
3.0 |
|
24.5 |
7.4 |
3.8 |
9.0 |
6.8 |
10.5 |
5.5 |
0.5 |
|
0.2 |
|
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|
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|
1.0 |
0.6 |
|
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|
Kentish
Plover |
Charadrius alexandrinus |
RC,
(1) |
|
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Spotted
Redshank |
Tringa erythropus |
RC,
(1) |
|
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Common
Redshank |
Tringa totanus |
RC,
(1) |
|
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Marsh
Sandpiper |
Tringa stagnatilis |
RC,
(1) |
|
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Common
Greenshank |
Tringa nebularia |
RC,
(1) |
|
|
0.5 |
|
|
|
|
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|
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|
|
|
0.3 |
0.8 |
0.2 |
|
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|
Green
Sandpiper |
Tringa ochropus |
(1) |
|
|
1.0 |
0.4 |
0.5 |
0.5 |
0.4 |
|
|
|
0.3 |
|
|
|
|
|
|
0.2 |
|
0.2 |
0.4 |
|
|
0.2 |
|
|
|
Wood
Sandpiper |
Tringa glareola |
LC,
(1) |
|
|
|
|
|
0.5 |
1.2 |
|
|
|
|
|
|
|
|
|
|
0.8 |
0.3 |
|
|
|
|
0.6 |
|
|
|
Common
Sandpiper |
Actitis hypoleucos |
(1) |
1.0 |
|
0.5 |
1.0 |
|
0.5 |
0.6 |
1.0 |
0.3 |
|
|
0.2 |
|
|
|
|
|
|
|
0.4 |
0.2 |
|
|
|
|
0.9 |
|
Eurasian
Woodcock |
Scolopax rusticola |
(1) |
|
|
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|
|
Pintail/Swinhoe's
Snipe* |
Gallinago stenura/G. megala |
LC*,(1) |
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
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|
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|
|
Common
Snipe |
Gallinago gallinago |
(1) |
|
|
|
|
|
0.3 |
0.2 |
|
|
|
|
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|
Red-necked
Stint |
Calidris ruficollis |
LC,
(1) |
3.0 |
|
|
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|
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|
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|
|
Temminck's
Stint |
Calidris temminckii |
LC,
(1) |
|
|
0.5 |
|
|
2.5 |
0.4 |
1.3 |
|
|
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|
Long-toed
Stint |
Calidris subminuta |
LC,
(1) |
|
|
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|
|
|
|
|
|
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|
|
0.3 |
|
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|
Whiskered
Tern |
Chlidonias hybrida |
(1) |
|
|
|
|
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|
|
|
|
|
|
|
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|
|
1.3 |
|
|
|
|
|
|
Domestic
Pigeon |
Columba livia |
- |
|
|
|
|
|
|
|
|
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|
|
DS |
|
|
|
|
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|
|
|
Oriental
Turtle Dove |
Streptopelia orientalis |
- |
|
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
|
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|
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|
Red
Turtle Dove |
Streptopelia tranquebarica |
- |
|
|
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|
Spotted
Dove |
Spilopelia chinensis |
- |
|
|
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|
|
|
|
|
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|
|
|
|
|
|
DS |
|
DS |
DS |
|
DS |
|
|
DS |
|
0.6 |
|
Asian
Koel |
Eudynamys scolopaceus |
- |
|
|
|
|
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|
Greater
Coucal# |
Centropus sinensis |
|
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|
|
Eurasian
Eagle Owl |
Bubo bubo |
RC |
|
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|
Savanna
Nightjar |
Caprimulgus affinis |
- |
|
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|
Pacific
Swift |
Apus pacificus |
(LC) |
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
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|
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|
|
|
House
Swift |
Apus nipalensis |
- |
10.0 |
|
|
|
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
DS |
DS |
|
|
|
|
|
|
|
|
Pied
Kingfisher |
Ceryle rudis |
(LC),
(1) |
|
|
|
0.2 |
0.3 |
0.5 |
0.2 |
|
|
0.3 |
|
|
|
|
|
|
|
|
0.2 |
|
|
|
0.5 |
|
|
|
|
Common
Kingfisher |
Alcedo atthis |
(1) |
|
|
|
0.4 |
0.5 |
0.3 |
|
0.3 |
0.5 |
1.0 |
0.3 |
1.0 |
0.8 |
0.5 |
0.8 |
1.0 |
0.4 |
|
0.8 |
|
|
|
|
0.6 |
|
0.4 |
|
White-throated
Kingfisher |
Halcyon smyrnensis |
(LC) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
0.3 |
|
|
|
|
Barn
Swallow |
Hirundo rustica |
- |
25.0 |
|
|
|
|
1.5 |
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
|
DS |
|
DS |
DS |
3.0 |
|
|
Red-rumped
Swallow |
Hirundo daurica |
- |
|
|
|
|
|
|
|
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|
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|
|
|
|
|
|
|
|
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|
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|
|
|
|
Eastern
Yellow Wagtail |
Motacilla tschutschensis |
(1) |
|
|
14.5 |
10.2 |
15.0 |
23.5 |
8.2 |
11.8 |
1.8 |
|
|
0.2 |
0.8 |
1.5 |
2.0 |
1.2 |
0.6 |
|
4.0 |
1.0 |
|
|
|
|
|
|
|
Grey
Wagtail |
Motacilla cinerea |
(1) |
|
|
|
0.2 |
|
0.3 |
0.2 |
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
White
Wagtail |
Motacilla alba |
(1) |
3.0 |
|
|
1.8 |
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
DS |
DS |
DS |
|
|
|
DS |
1.8 |
3.2 |
|
Richard's
Pipit |
Anthus richardi |
(1) |
|
|
1.5 |
0.8 |
0.5 |
1.0 |
1.0 |
1.8 |
0.5 |
|
|
|
|
0.3 |
|
DS |
|
DS |
DS |
DS |
|
|
|
|
|
|
|
Olive-backed
Pipit |
Anthus hodgsoni |
- |
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
|
|
|
|
|
|
|
Red-throated
Pipit |
Anthus cervinus |
LC |
|
2.0 |
2.5 |
1.2 |
0.5 |
0.5 |
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
0.4 |
|
|
|
|
|
0.7 |
|
Buff-bellied
Pipit |
Anthus rubescens |
LC |
|
1.0 |
1.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Red-whiskered
Bulbul |
Pycnonotus jocosus |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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|
|
|
|
|
|
|
|
Chinese
Bulbul |
Pycnonotus sinensis |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
|
DS |
|
|
|
|
Long-tailed
Shrike |
Lanius schach |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
|
|
|
|
DS |
DS |
|
|
|
Oriental
Magpie Robin |
Copsychus saularis |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
|
|
|
|
|
Daurian
Redstart |
Phoenicurus auroreus |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Stejneger's
Stonechat |
Saxicola stejnegeri |
- |
|
3.0 |
0.5 |
1.0 |
1.0 |
0.8 |
0.2 |
0.3 |
|
|
|
|
|
1.0 |
|
DS |
DS |
|
DS |
|
|
|
|
|
|
|
|
Masked
Laughingthrush |
Garrulax perspicillatus |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
Lanceolated
Warbler |
Locustella lanceolata |
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Pallas's
Grasshopper Warbler |
Locustella certhiola |
LC,
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-browed
Reed Warbler |
Acrocephalus bistrigiceps |
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Zitting
Cisticola |
Cisticola juncidis |
LC |
|
|
|
|
|
|
0.2 |
1.5 |
2.5 |
2.5 |
1.0 |
0.4 |
|
0.3 |
0.8 |
1.8 |
0.2 |
0.3 |
0.6 |
|
|
|
|
0.2 |
|
|
|
Yellow-bellied
Prinia |
Prinia flaviventris |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
|
DS |
|
DS |
DS |
0.8 |
0.4 |
|
Plain
Prinia |
Prinia inornata |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
|
DS |
DS |
|
|
|
Dusky
Warbler |
Phylloscopus fuscatus |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.5 |
|
DS |
|
|
|
|
|
|
|
|
|
|
|
Yellow-browed
warbler |
Phylloscopus inornatus |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1.4 |
|
Chinese
Penduline-Tit |
Remiz consobrinus |
RC,
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1.2 |
0.2 |
|
|
|
|
|
|
|
Japanese
White-eye |
Zosterops japonica |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Little
Bunting |
Emberiza pusilla |
- |
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-faced
Bunting |
Emberiza spodocephala |
- |
|
|
|
|
|
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Chinese
Grosbeak |
Eophona migratoria |
LC |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Scaly-breasted
Munia |
Lonchura punctulata |
- |
20.0 |
|
|
|
2.5 |
|
15.0 |
7.5 |
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
DS |
1.5 |
|
|
Eurasian
Tree Sparrow |
Passer montanus |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
|
DS |
|
|
|
|
Red-billed
Starling |
Spodiopsar sericeus |
GC |
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
0.8 |
1.6 |
6.6 |
39.0 |
17.4 |
|
|
|
|
|
|
|
|
White-cheeked
Starling |
Spodiopsar cineraceus |
PRC |
|
|
|
|
|
|
|
|
|
|
|
6.6 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-collared
Starling |
Gracupica nigricollis |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
DS |
DS |
|
|
|
|
DS |
|
|
|
White-shouldered
Starling |
Sturnia sinensis |
(LC) |
|
|
|
|
|
|
|
|
0.3 |
|
0.5 |
2.4 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common
Myna |
Acridotheres tristis |
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
|
|
|
|
|
Crested
Myna |
Acridotheres cristatellus |
– |
3.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
DS |
|
|
DS |
|
V |
|
Black-napped
Oriole |
Oriolus chinensis |
LC |
|
|
|
|
|
|
|
|
|
|
|
|
1.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black
Drongo |
Dicrurus macrocercus |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
|
|
|
Azure-winged
Magpie |
Cyanopica cyanus |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian
Magpie |
Pica pica |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
DS |
0.3 |
|
|
Large-billed
Crow |
Corvus macrorhynchos |
- |
|
|
|
0.4 |
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Collared
Crow |
Corvus torquatus |
LC,
NT |
|
|
|
0.2 |
0.3 |
|
|
0.5 |
|
0.3 |
|
0.8 |
0.8 |
0.8 |
0.5 |
|
|
|
|
|
|
0.8 |
|
|
|
|
|
No. of species recorded |
108 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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|
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|
|
Note: Conservation Status follows that of Fellowes et. al. (2002)
(1) Indicates the bird species is wetland dependent.
* Pintail Snipe and Swinhoe's Snipe cannot be distinguished in field, conservation status refers to Swinhoe's Snipe.
V Indicates the species is recorded outside regular surveys.
DS Indicates species recorded during survey.
# Greater Coucal is listed as vulnerable (VU) in China Red Data Book and it is protected under terrestrial wildlife state protection (category II).
Table B5. Summary of
Bird Species Recorded at the WRA and their Respective Monthly Mean between November
2012 and April 2014
|
Common name |
Scientific name |
Conservation status |
Nov-12 |
Dec-12 |
Jan-13 |
Feb-13 |
Mar-13 |
Apr-13 |
May-13 |
Jun-13 |
Jul-13 |
Aug-13 |
Sep-13 |
Oct-13 |
Nov-13 |
Dec-13 |
Jan-14 |
Feb-14 |
Mar-14 |
Apr-14 |
|
Little
Grebe |
Tachybaptus
ruficollis |
LC,
(1) |
1.0 |
1.0 |
1.2 |
0.4 |
0.6 |
0.4 |
1.5 |
0.5 |
|
0.6 |
0.5 |
1.2 |
0.6 |
2.2 |
1.8 |
5.3 |
4.5 |
2.4 |
|
Great
Cormorant |
Phalacrocorax
carbo |
PRC,
(1) |
0.8 |
3.2 |
0.8 |
1.0 |
0.0 |
0.0 |
|
|
|
|
|
0.2 |
V |
0.4 |
0.6 |
0.5 |
|
|
|
Grey
Heron |
Ardea
cinerea |
PRC,
(1) |
0.8 |
1.4 |
0.8 |
1.4 |
0.0 |
0.0 |
|
|
|
|
V |
1.0 |
2.8 |
2.6 |
1.6 |
2.5 |
|
|
|
Purple
Heron |
Ardea
purpurea |
RC,
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Great
Egret |
Ardea
alba |
PRC,
(1) |
1.4 |
0.6 |
1.0 |
0.8 |
0.2 |
0.6 |
|
0.8 |
0.6 |
|
|
0.6 |
0.6 |
2.4 |
1.2 |
1.8 |
0.8 |
0.2 |
|
Intermediate
Egret |
Egretta
intermedia |
RC,
(1) |
0.2 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
|
|
|