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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 |
December
2013 |
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-311/2008) for construction of the comprehensive development in Wo Shang Wai was first granted by EPD on 9 September 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 ACE, EPD and AFCD on a biannual basis. This is the 7th Biannual EM&A report and it summarises the findings on EM&A results of ecological aspects during the period from 1 May to 31 October 2013. This report documents surveys and management activities conducted in the Survey Area and WRA from 1 May to 31 October 2013, 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 46 bird species were recorded in the
Survey Area (excluding the WRA) in May to October 2013, 28 of which were species of conservation importance and/or
wetland-dependence. A summary of survey data is provided in Appendix B.
A
total of 46 species were recorded in the WRA in the survey
periods, 25 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)), two were recorded in the WRA (Little Egret and Chinese Pond
Heron). 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) 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 chick of White-breasted Waterhen, Amaurornis phoenicurus, was
observed in the WRA, indicating that the WRA was effective in providing
suitable breed ground for this wetland-dependence species..
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, 25 bird species of conservation
importance and/or wetland-dependence, were observed using the site, including
some bird species which are highly sensitive to disturbance and two bird target species (i.e.
Little 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 at 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 a month in May 2013 and October 2013. Further, notable herpetofauna observations during other surveys were also
recorded.
Gunther's Frog, Rana guentheri, was recorded in the Survey Area (excluding WRA) in the reporting period.
A total of one
amphibian species and two reptile species were recorded during the survey
period within the WRA. A Softshell Turtle, Trionychidae
sp. was recorded outside survey within the WRA. A summary of survey data is provided in Appendix C.
Monitoring of dragonflies and butterflies was conducted
twice-monthly in May 2013 to October 2013.
Further, notable dragonfly and butterfly observations during other surveys were
recorded.
A total of 11 dragonfly species and seven 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 (18 species) and
butterfly species (16 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.
A Small Asian Mongoose, Herpestes javanicus, was recorded
in the WRA during regular survey. Japanese Pipistrelle,
Pipistrellus abramus were
recorded outside survey within the WRA. 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, pH of some Cells reached the Action Level.
No measures are proposed at the moment, but the condition will be monitored. Monitoring data are presented in Appendix D.
Pedology
samples were collected on 31 May 2013 for laboratory analysis of soil
quality. 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 May 2013 and 31 October 2013 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) |
46 |
46 |
|
Birds (of
conservation importance and/or wetland-dependence) |
28 |
25 |
|
Amphibians |
1 |
1 |
|
Reptiles |
0 |
3 |
|
Mammals |
0 |
2 |
|
Dragonflies |
11 |
18 |
|
Butterflies |
7 |
16 |
A total of
46 bird species, 1 amphibian species, 3 reptile species, 2 mammal species, 18
dragonfly species and 16 butterfly species were recorded in the WRA, including
25 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. May 2013 to October 2013), the site was particularly attractive to Little Egret, which was recorded on nearly-weekly basis, with monthly means ranging from 0.5 to 3.6 birds per survey. Chinese Pond Heron was recorded four out of six months in regular survey under review (May 2013 to October 2013) with monthly means ranging from 0.5 to 2.0 bird per survey. Eastern Cattle Egret was least attracted to the site, no Eastern Cattle Egret was recorded under review period (May 2013 to October 2013).
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; these 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 for when the target level for each of the three species is
achieved.
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) was complete, except as described in
Section 4.1 above.
Of all three target species, two were recorded using the site including
Chinese Pond Heron and Little Egret during the reporting period (May 2013 –
October 2013). Among all target species, Little Egret was recorded most
regularly (recorded in all six months), followed by Chinese Pond Heron
(recorded in 4 out of 6 months) and no Eastern Cattle Egret was recorded 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 2010 and Oct 2013
|
Common Name |
Scientific Name |
Conservation Status (2) |
May 2010 – Apr 2011 |
May 2011 – Apr 2012 |
May 2012 – Apr 2013 |
Nov 2012 – Oct 2013 |
|
Little Egret |
Egretta garzetta |
PRC, (RC) |
1.6 |
1.0 |
0.9 |
1.4 |
|
Eastern Cattle Egret |
Bubulcus coromandus |
(LC) |
0.0 |
1.2 |
0.0 |
0.0 |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (RC) |
0.2 |
2.7 |
1.3 |
0.8 |
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).
Based on Table 4.2 above, the target levels for
Chinese Pond Heron, Little Egret and Eastern Cattle Egret have not been
achieved between November 2012 and October 2013. It is noted that November 2012
to October 2013 was the first full annual period since the 30-month
establishment period of the WRA was concluded.
Actions
will be taken to increase the WRA utilization by birds in the coming winter,
including:
1. lowering the water level;
2. restocking the Cell in the WRA; and
3. installing flooding platform.
Results of
these actions will be closely monitored.
A total of
104 bird species have been recorded within the WRA since completion of site
formation. Of the 104 species, 70 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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May 2013 |
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Jun 2013 |
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Jul 2013 |
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Aug 2013 |
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Sep 2013 |
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Birds |
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Dragonflies & Butterflies |
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Inspection Visits |
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Oct 2013 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
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11 |
12 |
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14 |
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Birds |
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Herpetofauna |
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Water Quality |
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Inspection Visits |
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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) |
May Mean (3) |
Jun Mean (3) |
Jul Mean (3) |
Aug Mean (3) |
Sep Mean (3) |
Oct Mean (3) |
|
Little Grebe |
Tachybaptus ruficollis |
LC, (1) |
5.8 |
4.0 |
3.8 |
3.6 |
8.5 |
10.8 |
|
Great Cormorant |
Phalacrocorax carbo |
PRC, (1) |
|
|
|
|
|
2.4 |
|
Black-crowned Night Heron |
Nycticorax nycticorax |
(LC), (1) |
1.2 |
0.8 |
3.0 |
0.2 |
|
|
|
Yellow Bittern |
Ixobrychus sinensis |
LC, (1) |
|
|
|
|
0.3 |
|
|
Eastern Cattle Egret |
Bubulcus coromandus |
(LC), (1) |
|
0.3 |
|
|
|
1.2 |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (RC), (1) |
4.2 |
6.8 |
10.6 |
16.8 |
12.3 |
11.8 |
|
Little Egret |
Egretta garzetta |
PRC, (RC), (1) |
9.0 |
9.3 |
10.0 |
30.2 |
19.0 |
39.2 |
|
Intermediate Egret |
Egretta intermedia |
RC, (1) |
0.6 |
|
|
|
|
0.2 |
|
Grey Heron |
Ardea cinerea |
PRC, (1) |
|
|
|
|
1.8 |
7.2 |
|
Great Egret |
Egretta alba |
PRC, (RC), (1) |
4.0 |
2.8 |
12.4 |
11.6 |
9.5 |
18.4 |
|
Black-faced Spoonbill |
Platalea minor |
PGC, (1) |
|
|
|
|
|
2.2 |
|
Tufted Duck |
Aythya fuligula |
LC, (1) |
0.4 |
|
|
|
|
|
|
Black Kite |
Milvus migrans |
RC |
0.2 |
0.3 |
|
0.4 |
0.8 |
0.4 |
|
White-breasted Waterhen |
Amaurornis phoenicurus |
(1) |
|
1.0 |
1.6 |
0.2 |
1.5 |
2.0 |
|
Common Moorhen |
Gallinula chloropus |
(1) |
0.2 |
|
|
|
|
|
|
Black-winged Stilt |
Himantopus himantopus |
(RC), (1) |
|
|
|
|
|
4.6 |
|
Pied Avocet |
Recurvirostra avosetta |
RC, (1) |
|
|
|
|
|
9.6 |
|
Green Sandpiper |
Tringa ochropus |
(1) |
0.6 |
|
|
|
|
1.0 |
|
Common Sandpiper |
Actitis hypoleucos |
(1) |
0.2 |
|
|
1.6 |
2.6 |
2.0 |
|
Whiskered Tern |
Chlidonias hybrid |
LC, (1) |
1.2 |
|
|
|
|
|
|
Pied Kingfisher |
Ceryle rudis |
(LC), (1) |
|
|
|
0.2 |
|
0.2 |
|
Common Kingfisher |
Alcedo atthis |
(1) |
0.8 |
1.5 |
1.2 |
1.4 |
2.5 |
2.6 |
|
White-throated Kingfisher |
Halcyon smyrnensis |
LC, (1) |
|
0.3 |
0.4 |
|
|
|
|
Eastern Yellow Wagtail |
Motacilla tschutschensis |
(1) |
0.8 |
|
|
|
|
1.4 |
|
White Wagtail |
Motacilla alba |
(1) |
3.2 |
3.8 |
2.2 |
3.6 |
4.5 |
8.6 |
|
White-shouldered Starling |
Sturnus sinensis |
(LC), (1) |
0.6 |
0.8 |
0.6 |
0.8 |
|
|
|
Zitting Cisticola |
Cisticola juncidis |
LC, (1) |
|
|
|
|
|
0.2 |
|
Collared Crow |
Corvus torquatus |
LC, (1) |
|
0.8 |
0.6 |
|
|
0.6 |
|
|
|
No.
of species recorded |
16 |
13 |
11 |
12 |
11 |
21 |
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)
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) |
May Mean (3) |
Jun Mean (3) |
Jul Mean (3) |
Aug Mean (3) |
Sep Mean (3) |
Oct Mean (3) |
|
Little Grebe |
Tachybaptus ruficollis |
LC, (1) |
1.5 |
0.5 |
|
0.6 |
0.5 |
1.2 |
|
Great Cormorant |
Phalacrocorax carbo |
PRC, (1) |
|
|
|
|
|
0.2 |
|
Grey Heron |
Ardea cinerea |
PRC, (1) |
|
|
|
|
ü |
1.0 |
|
Great Egret |
Egretta alba |
PRC, (RC), (1) |
|
0.8 |
0.6 |
|
|
0.6 |
|
Little Egret |
Egretta garzetta |
PRC, (RC), (1) |
0.6 |
1.8 |
0.4 |
3.4 |
0.5 |
2.2 |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (RC), (1) |
|
|
0.8 |
2.0 |
0.5 |
1.4 |
|
Black-crowned Night Heron |
Nycticorax nycticorax |
(LC), (1) |
|
0.3 |
|
|
|
ü |
|
Yellow Bittern |
Ixobrychus sinensis |
LC, (1) |
1.0 |
2.5 |
0.2 |
1.4 |
1.3 |
0.8 |
|
Black Kite |
Milvus migrans |
RC, (1) |
0.2 |
0.3 |
|
1.2 |
0.8 |
0.2 |
|
Japanses Quail |
Coturnix japonica |
LC, (1) |
|
|
|
|
|
ü |
|
White-breasted Waterhen |
Amaurornis phoenicurus |
(1) |
ü |
1.8 |
0.2 |
0.2 |
ü |
0.8 |
|
Black-winged Stilt |
Himantopus himantopus |
(RC), (1) |
|
|
0.2 |
0.6 |
ü |
0.2 |
|
Kentish Plover |
Charadrius alexandrines |
(RC), (1) |
|
|
0.8 |
|
|
|
|
Little Ringed Plover |
Charadrius dubius |
(LC), (1) |
|
|
|
|
|
ü |
|
Spotted Redshank |
Tringa erythropus |
RC, (1) |
|
|
|
|
|
ü |
|
Green Sandpiper |
Tringa ochropus |
(1) |
|
|
|
|
|
1 |
|
Wood Sandpiper |
Tringa glareola |
- |
|
|
|
|
|
ü |
|
Common Sandpiper |
Actitis hypoleucos |
(1) |
0.2 |
|
ü |
0.6 |
ü |
0.8 |
|
Eurasian Eagle Owl * |
Bubo bubo |
RC |
|
|
|
|
ü |
|
|
Pied Kingfisher |
Ceryle rudis |
(LC), (1) |
|
|
|
ü |
|
|
|
Common Kingfisher |
Alcedo atthis |
(1) |
0.6 |
0.3 |
0.4 |
0.4 |
0.8 |
1.0 |
|
Eastern Yellow Wagtail |
Motacilla tschutschensis |
(1) |
0.2 |
|
|
|
|
0.4 |
|
White Wagtail |
Motacilla alba |
(1) |
1.0 |
|
1.2 |
0.4 |
3.5 |
2.8 |
|
White-shouldered Starling |
Sturnus sinensis |
(LC), (1) |
|
|
0.2 |
|
|
|
|
Collared Crow |
Corvus torquatus |
LC, (1) |
|
|
|
|
|
0.2 |
|
|
|
No.
of species recorded |
9 |
8 |
11 |
11 |
12 |
21 |
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)
ü 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 |
3.8 |
0.8 |
0.5 |
0.5 |
|
0.6 |
|
1.4 |
1.6 |
0.8 |
1 |
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 |
1.6 |
2 |
2 |
0.4 |
|
|
|
|
|
|
1 |
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 |
2 |
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 |
0.3 |
|
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 |
0.6 |
0.7 |
0.6 |
0.6 |
|
|
|
|
0.3 |
0.9 |
|
Little Egret |
Egretta garzetta |
PRC, (1) |
|
|
|
1.8 |
8 |
2 |
0.4 |
0.5 |
0.8 |
0.3 |
0.3 |
1 |
1 |
0.5 |
1.5 |
1.6 |
1.4 |
2 |
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 |
0.2 |
|
|
|
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 |
0.8 |
2 |
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) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-faced Spoonbill |
Platalea minor |
PGC, EN, (1) |
|
|
|
|
0.3 |
10.3 |
|
|
|
|
|
|
|
|
|
|
0.4 |
|
|
|
|
|
|
|
|
|
|
Mandarin Duck |
Aix galericulata |
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Wigeon |
Anas penelope |
RC, (1) |
|
|
|
1.6 |
2.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Teal |
Anas crecca |
RC, (1) |
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Pintail |
Anas acuta |
RC, (1) |
|
|
|
0.2 |
7 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Shoveler |
Anas clypeata |
RC, (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Tufted Duck |
Aythya fuligula |
LC, (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Garganey^ |
Anas querquedula |
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Western Osprey |
Pandion haliaetus |
RC, (1) |
|
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black Kite |
Milvus migrans |
(RC) 0.8 |
|
|
|
|
0.8 |
0.3 |
0.2 |
|
0.3 |
|
|
|
0.3 |
|
|
|
0.2 |
|
|
0.2 |
0.5 |
|
|
|
|
0.4 |
|
Eastern Buzzard |
Buteo japonicus |
- |
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0.2 |
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Common Kestrel |
Falco tinnunculus |
- |
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1 |
0.4 |
1 |
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 |
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0.4 |
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0.5 |
1 |
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 |
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1 |
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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 |
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24.5 |
7.4 |
3.8 |
9 |
6.8 |
10.5 |
5.5 |
0.5 |
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0.2 |
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1 |
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) |
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0.5 |
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0.3 |
0.8 |
0.2 |
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Green Sandpiper |
Tringa ochropus |
(1) |
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1 |
0.4 |
0.5 |
0.5 |
0.4 |
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0.3 |
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0.2 |
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0.2 |
0.4 |
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0.2 |
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Wood Sandpiper |
Tringa glareola |
LC, (1) |
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0.5 |
1.2 |
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0.8 |
0.3 |
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0.6 |
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Common Sandpiper |
Actitis hypoleucos |
(1) |
1 |
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0.5 |
1 |
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0.5 |
0.6 |
1 |
0.3 |
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0.2 |
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0.4 |
0.2 |
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0.9 |
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Eurasian Woodcock^ |
Scolopax rusticola |
(1) |
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Pintail/Swinhoe's Snipe* |
Gallinago stenura/G. megala |
LC*,(1) |
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0.5 |
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0.3 |
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Common Snipe |
Gallinago gallinago |
(1) |
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0.3 |
0.2 |
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Red-necked Stint |
Calidris ruficollis |
LC, (1) |
3 |
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Temminck's Stint |
Calidris temminckii |
LC, (1) |
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0.5 |
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2.5 |
0.4 |
1.3 |
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Long-toed Stint |
Calidris subminuta |
LC, (1) |
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0.3 |
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Whiskered Tern |
Chlidonias hybrida |
(1) |
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1.3 |
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Domestic Pigeon |
Columba livia |
- |
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v |
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Oriental Turtle Dove |
Streptopelia orientalis |
- |
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0.2 |
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Red Turtle Dove^ |
Streptopelia tranquebarica |
- |
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Spotted Dove |
Spilopelia chinensis |
- |
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v |
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v |
v |
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v |
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v |
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0.6 |
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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) |
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0.3 |
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House Swift |
Apus nipalensis |
- |
10 |
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0.2 |
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v |
v |
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Pied Kingfisher |
Ceryle rudis |
(LC), (1) |
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0.2 |
0.3 |
0.5 |
0.2 |
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0.3 |
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0.2 |
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0.5 |
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Common Kingfisher |
Alcedo atthis |
(1) |
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0.4 |
0.5 |
0.3 |
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0.3 |
0.5 |
1 |
0.3 |
1 |
0.8 |
0.5 |
0.8 |
1 |
0.4 |
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0.8 |
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0.6 |
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0.4 |
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White-throated Kingfisher |
Halcyon smyrnensis |
(LC) |
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0.3 |
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0.3 |
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Barn Swallow |
Hirundo rustica |
- |
25 |
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1.5 |
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v |
v |
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v |
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v |
v |
3 |
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Red-rumped
Swallow |
Hirundo daurica |
- |
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Eastern Yellow Wagtail |
Motacilla tschutschensis |
(1) |
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14.5 |
10.2 |
15 |
23.5 |
8.2 |
11.8 |
1.8 |
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0.2 |
0.8 |
1.5 |
2 |
1.2 |
0.6 |
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4 |
1 |
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Grey Wagtail |
Motacilla cinerea |
(1) |
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0.2 |
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0.3 |
0.2 |
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0.3 |
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White Wagtail |
Motacilla alba |
(1) |
3 |
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1.8 |
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v |
v |
v |
v |
v |
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v |
1.8 |
3.2 |
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Richard's Pipit |
Anthus richardi |
(1) |
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1.5 |
0.8 |
0.5 |
1 |
1 |
1.8 |
0.5 |
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0.3 |
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v |
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v |
v |
v |
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Olive-backed Pipit |
Anthus hodgsoni |
- |
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0.5 |
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v |
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Red-throated Pipit |
Anthus cervinus |
LC |
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2 |
2.5 |
1.2 |
0.5 |
0.5 |
0.2 |
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0.4 |
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0.7 |
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Buff-bellied Pipit |
Anthus rubescens |
LC |
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1 |
1.5 |
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Red-whiskered Bulbul |
Pycnonotus jocosus |
- |
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Chinese Bulbul |
Pycnonotus sinensis |
- |
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v |
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v |
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v |
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Long-tailed Shrike |
Lanius schach |
- |
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v |
v |
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v |
v |
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Oriental Magpie Robin |
Copsychus saularis |
- |
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v |
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Daurian Redstart |
Phoenicurus auroreus |
- |
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Stejneger's Stonechat |
Saxicola stejnegeri |
- |
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3 |
0.5 |
1 |
1 |
0.8 |
0.2 |
0.3 |
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1 |
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v |
v |
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v |
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Masked Laughingthrush |
Garrulax perspicillatus |
- |
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v |
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Lanceolated Warbler |
Locustella lanceolata |
(1) |
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0.3 |
|
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Pallas's Grasshopper
Warbler |
Locustella certhiola |
LC, (1) |
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0.3 |
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Black-browed Reed Warbler |
Acrocephalus bistrigiceps |
(1) |
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0.3 |
|
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Zitting Cisticola |
Cisticola juncidis |
LC |
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0.2 |
1.5 |
2.5 |
2.5 |
1 |
0.4 |
|
0.3 |
0.8 |
1.8 |
0.2 |
0.3 |
0.6 |
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0.2 |
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Yellow-bellied Prinia |
Prinia flaviventris |
- |
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v |
|
v |
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v |
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v |
v |
0.8 |
0.4 |
|
Plain Prinia |
Prinia inornata |
- |
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v |
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v |
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v |
v |
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Dusky Warbler |
Phylloscopus fuscatus |
- |
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0.5 |
|
v |
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Yellow-browed warbler |
Phylloscopus inornatus |
- |
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1.4 |
|
Chinese Penduline-Tit |
Remiz consobrinus |
RC, (1) |
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1.2 |
0.2 |
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Little Bunting |
Emberiza pusilla |
- |
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0.5 |
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Black-faced Bunting |
Emberiza spodocephala |
- |
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0.5 |
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Chinese Grosbeak |
Eophona migratoria |
LC |
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0.3 |
|
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Scaly-breasted Munia |
Lonchura punctulata |
- |
20 |
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2.5 |
|
15 |
7.5 |
|
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|
v |
|
v |
v |
1.5 |
|
|
Eurasian Tree Sparrow |
Passer montanus |
- |
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v |
|
v |
|
v |
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Red-billed Starling |
Spodiopsar sericeus |
GC |
|
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0.3 |
|
0.8 |
1.6 |
6.6 |
39 |
17.4 |
|
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White-cheeked Starling |
Spodiopsar cineraceus |
PRC |
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6.6 |
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|
|
|
|
|
|
Black-collared Starling |
Gracupica nigricollis |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
v |
v |
v |
v |
|
|
|
|
v |
|
|
|
White-shouldered Starling |
Sturnia sinensis |
(LC) |
|
|
|
|
|
|
|
|
0.3 |
|
0.5 |
2.4 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Myna |
Acridotheres tristis |
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
v |
|
|
|
|
|
|
|
|
|
Crested Myna |
Acridotheres cristatellus |
– |
3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
v |
|
|
|
|
v |
|
|
v |
|
^ |
|
Black-naped
Oriole |
Oriolus chinensis |
LC |
|
|
|
|
|
|
|
|
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black Drongo |
Dicrurus macrocercus |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
v |
v |
|
|
|
Eurasian Magpie |
Pica pica |
- |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
v |
|
|
|
|
v |
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 |
102 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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.
^ Indicates the species is recorded outside regular surveys.
v Indicates species recorded during surveys.
Table B5. Summary of
Bird Species Recorded at the WRA and their Respective Monthly Mean between November
2012 and October 2013
|
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 |
|
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 |
|
Great Cormorant |
Phalacrocorax carbo |
PRC, (1) |
0.8 |
3.2 |
0.8 |
1 |
0 |
0 |
|
|
|
|
|
0.2 |
|
Grey Heron |
Ardea cinerea |
PRC, (1) |
0.8 |
1.4 |
0.8 |
1.4 |
0 |
0 |
|
|
|
|
^ |
1 |
|
Purple Heron |
Ardea purpurea |
RC, (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
Great Egret |
Ardea alba |
PRC, (1) |
1.4 |
0.6 |
1 |
0.8 |
0.2 |
0.6 |
|
0.8 |
0.6 |
|
|
0.6 |
|
Intermediate Egret |
Egretta intermedia |
RC, (1) |
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
Little Egret |
Egretta garzetta |
PRC, (1) |
0.8 |
2 |
2.2 |
1.4 |
0.6 |
1.2 |
0.6 |
1.8 |
0.4 |
3.4 |
0.5 |
2.2 |
|
Eastern Cattle Egret |
Bubulcus coromandus |
(LC), (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (1) |
1.6 |
2.2 |
2.4 |
0.4 |
|
|
|
|
0.8 |
2 |
0.5 |
1.4 |
|
Yellow Bittern |
Ixobrychus sinensis |
(LC), (1) |
|
|
|
|
|
^ |
1.0 |
2.5 |
0.2 |
1.4 |
1.3 |
0.8 |
|
Black-crowned Night Heron |
Nycticorax nycticorax |
LC, (1) |
^ |
|
|
0.2 |
|
|
|
0.3 |
|
|
|
^ |
|
Eurasian Spoonbill^ |
Platalea leucorodia |
LC, (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-faced Spoonbill |
Platalea minor |
PGC, EN, (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
Mandarin Duck |
Aix galericulata |
(1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Wigeon |
Anas penelope |
RC, (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Teal |
Anas crecca |
RC, (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Pintail |
Anas acuta |
RC, (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Shoveler |
Anas clypeata |
RC, (1) |
|
|
^ |
|
|
|
|
|
|
|
|
|
|
Tufted Duck |
Aythya fuligula |
LC, (1) |
|