|
Proposed Comprehensive Development at Wo Shang Wai Yuen Long |
|
|
|
|
|
Biannual EM&A Report on Ecology for May 2015 - October 2015 (Rev A) |
|
|
|
|
|
|
|
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.. |
%20May%202015%20-%20Oct%202015%20Rev%20A_files/image002.png)
Certification by Environmental Team Leader and Verification by Independent Environmental Checker
|
Contents |
Chapter Title Page
Tables
|
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
Figure 1.2 Water Quality Monitoring Locations for Ecological Monitoring
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
1
Introduction
|
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 completed, except along the western and southern boundaries 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 11th Biannual EM&A report and it summarises the findings on EM&A results of ecological aspects during the period from 1 May 2015 to 31 October 2015. This report documents surveys and management activities conducted in the Survey Area and WRA from 1 May 2015 to 31 October 2015, which is based on ecological surveys and advices on management which were undertaken by the appointed Non-government Organisations (Green Power / Eco-Education & Resources 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
|
|
Water quality of Wetland Restoration Area (WRA) |
WRA |
After filling of WRA with water, monthly for in situ water quality and every six 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 |
2
Ecological
Monitoring
|
In accordance with the EM&A requirements, monitoring of birds, dragonflies and butterflies, and herpetofauna were 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 54 bird species were recorded in the Survey Area (excluding the WRA) in May 2015 to October 2015, 26 of which were species of conservation importance and/or wetland-dependence. A summary of survey data is provided in Appendix B.
A total of 59 species were recorded in the WRA in the survey periods, 34 of which were species of conservation importance and/or wetland-dependent species. The WRA has attracted a number of species of conservation interest, including Great Cormorant, Phalacrocorax carbo, Grey Heron, Ardea cinerea, Purple Heron, Ardea purpurea, Black-crowned Night Heron, Nycticorax nycticorax, Yellow Bittern, Ixobrychus sinensis, Black Kite, Milvus migrans, Pheasant-tailed Jacana, Hydrophasianus chirurgus, White-throated Kingfisher, Halcyon smyrnensis, Thick-billed Warbler, Iduna aedon, White-cheeked Starling, Spodiopsar cineraceus and Collared Crow, Corvus torquatus. Black-crowned Night Heron, Yellow Bittern, Pheasant-tailed Jacana, White-throated Kingfisher, Thick-billed Warbler and Collared Crow are listed by Fellowes et al. as of “Local Concern” in 2002. Purple Heron and Black Kite are listed by Fellowes et al. as of “Regional Concern” in 2002. Great Cormorant, White-cheeked Starling and Grey Heron are listed by Fellowes et al. as of “Potential Regional Concern” in 2002.
The three target species (i.e. Little Egret, Egtretta garzetta, Eastern Cattle Egret, Bubulcus coromandus and Chinese Pond Heron, Ardeola bacchus) were recorded in the WRA during regular survey.
Baillon's Crake, Porzana pusilla was also recorded in the WRA and it is a scarce passage migrant of Hong Kong. This indicated that the WRA provided suitable wetland habitats to wetland-dependent passage migrant.
The fish ponds to the north of the WRA are at a greater distance from the residential portion and any disturbance impact(s) from the construction works would have first affected the WRA. Further, 34 bird species of conservation importance and /or wetland dependence, were observed using the site during survey period, 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 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 per month between May 2015 and October 2015. Further, notable herpetofauna observations during other surveys were also recorded.
Asian Common Toad, Bufo melanostictus and Gunther's Frog, Hylarana guentheri, were recorded in the survey area (excluding WRA) in the survey period. For reptile, Changeable Lizard, Calotes versicolor was observed in the survey area within the survey period.
Gunther's Frog, Hylarana guentheri, was recorded in the WRA in the survey period. No reptile species was recorded in the WRA within the survey period.
A summary of survey data is provided in Appendix C.
Monitoring of dragonflies and butterflies was conducted once per month in September 2015 and October 2015 and twice per month from May 2015 to August 2015. Further, notable dragonfly and butterfly observations during other surveys were recorded.
A total of five dragonfly species and one butterfly species were recorded using the ponds in the Survey Area (excluding WRA) in the reporting period. At the WRA, a higher diversity of dragonfly species (14 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 (excluding WRA) within the reporting period.
One unidentified bat species 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. pH of Cell 1 and Cell 3 reached action level in May 2015; while water level of Cell 1, Cell 2 and Cell 4 reached action levels in May 2015; According to the ecological monitoring data, the low water level in the WRA attracted wetland-dependent species including Great Cormorant, Phalacrocorax carbo, Grey Heron, Ardea cinerea, Purple Heron, Ardea purpurea, Black-crowned Night Heron, Nycticorax nycticorax, Yellow Bittern, Ixobrychus sinensis, Pheasant-tailed Jacana, Hydrophasianus chirurgus and White-throated Kingfisher, Halcyon smyrnensis. As the low water level attracts wetland-dependent birds, the existing water level will be maintained and monitored regularly. Monitoring data are presented in Appendix D. Locations for the monitoring of water quality for the ecological monitoring are shown in Figure 1.2.
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..
Vegetation management activities undertaken at the site primarily involved watering of plants, tree pruning, weeding and grass cutting.
Golden Apple Snails were removed on an “as-seen” basis.
All red fire ant nests were treated with approved pesticide and covered with overturn baskets for a week. All pesticide used were in powder form and the pesticide usage was confined to Fire Ants’ nest found on terrestrial area which were further away from the Cells to prevent the contamination of water. All treated fire ant nests were inactive within one week of treatment.
Preliminarily actions have been taken to increase the WRA utilization by birds. 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.
The first two measures aim to increase the foraging area and food sources for the target species respectively. The third measure aims to increase foraging ground for the target species. According to Horiuchi et al (2007), floating platform can gather fish in the pond and this provides opportunities for the target species to prey for the fish which can be use as a fishing platform. The fourth measure aims to maintain suitable habitat for target species.
Ecological monitoring between 1 May 2015 and 31 October 2015 was carried out following the survey methodology and frequency outlined in the EM&A Manual.
Summary of ecological monitoring in the Survey Area and WRA between May 2015 and October 2015 (Table 4.1):
Table 4.1: Summary of Ecological Monitoring in WRA and Survey Area
|
Species |
Number of species recorded in Survey Area (excluding WRA) |
Number of species recorded in WRA |
|
Birds (total) |
54 |
59 |
|
Birds (of conservation importance and/or wetland-dependence) |
26 |
34 |
|
Amphibians |
2 |
1 |
|
Reptiles |
1 |
0 |
|
Mammals |
0 |
1 |
|
Dragonflies |
5 |
14 |
|
Butterflies |
1 |
7 |
A total of 59 bird species, 1 mammal species, 14 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. A list of the bird species recorded at the WRA since completion of site formation is provided in Appendix B (Table B4 to B6).
With the completion of planting as scheduled in the approved Habitat Creation and Management Plan (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 an approved Variation to Environmental Permit (EP-311/2008/D) to defer planting at the location applies), and the 30 month establishment period concluded in October 2012. A review of the performance of the WRA during the review period in terms of target species attraction 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/shrub 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 is anticipated to be fully operational after an establishment period of 2.5 years (30 months).
Table 4.2: Annual Mean of the Three Bird Target Species Recorded at the WRA between May 2010 and Oct 2015
|
Common Name |
Scientific Name |
Conservation Status (2) |
Baseline Annual Mean (3) |
May 10-Apr 11 |
May 11-Apr 12 |
May 12-Apr 13 |
May 13-Apr 14 |
May 14-Apr 15 |
(Reporting period) May 15 – Oct 15* |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (RC) |
1.3 |
0.2 |
2.7 |
1.3 |
1.9 |
2.0 |
2.1 |
|
Little Egret |
Egretta garzetta |
PRC, (RC) |
5.5 |
1.6 |
1.0 |
0.9 |
2.3 |
2.0 |
1.5 |
|
Eastern Cattle Egret |
Bubulcus coromandus |
(LC) |
1.3 |
0.0 |
1.2 |
0.0 |
0.1 |
0.0 |
0.1 |
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).
(3) Annual mean number recorded during Baseline Ecological Monitoring.
* The mean number of the target species was calculated in annual basis.
Based on Table 4.2 above, the target level of the Chinese Pond Heron was achieved between May 2015 and October 2015 while the target levels for Little Egret and Eastern Cattle Egret was not achieved.
As the Proposed Comprehensive Development at Wo Shang Wai is still under construction phase, it is considered acceptable. According to the ecological monitoring data of the survey area (excluding the WRA), Eastern Cattle Egret was observed only in one fifth of the regular ecological survey (i.e. 6 out of 29) and the annual mean of the Eastern Cattle Egret of the survey area (excluding the WRA) is 2.1 birds per survey, the results indicated the number of Eastern Cattle Egret in the whole area was low and the low number of Eastern Cattle Egret in the WRA is considered acceptable.
In addition, although the target levels for Little Egret and Eastern Cattle Egret have not been achieved between May 2015 and October 2015, the WRA continues to attract wetland dependent species. Among all the wetland dependent species, Great Cormorant, Phalacrocorax carbo, Grey Heron, Ardea cinerea, Purple Heron, Ardea purpurea, Black-crowned Night Heron, Nycticorax nycticorax, Yellow Bittern, Ixobrychus sinensis, Black Kite, Milvus migrans, Pheasant-tailed Jacana, Hydrophasianus chirurgus, White-throated Kingfisher, Halcyon smyrnensis, Thick-billed Warbler, Iduna aedon, White-cheeked Starling, Spodiopsar cineraceus and Collared Crow, Corvus torquatus. Black-crowned Night Heron, Yellow Bittern, Pheasant-tailed Jacana, White-throated Kingfisher, Thick-billed Warbler and Collared Crow are listed by Fellowes et al. as of “Local Concern” in 2002. Purple Heron and Black Kite are listed by Fellowes et al. as of “Regional Concern” in 2002. Great Cormorant, White-cheeked Starling and Grey Heron are listed by Fellowes et al. as of “Potential Regional Concern” in 2002. The presence of these wetland-dependent species indicates that the WRA was effective in providing habitat suitable for species of conservation interest.
A total of 121 bird species have been recorded within the WRA since completion of site formation. Of the 121 species, 76 were species of conservation importance and/or wetland dependence – indicating that the WRA provides suitable habitats for these species despite the construction work within the residential portion of the Project Site.
The site continuously attracts bird species of conservation importance, indicating that the WRA not only provides a buffer for potential disturbance during construction phase, but also a valuable habitat for wetland dependent species and species of conservation importance.
5
References
|
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.
Hong Kong Bird Watching Society
2014. List of Hong Kong Birds - 2015-1-12. <www.hkbws.org.hk>.
Horiuchi, S., Odawara, T., Yonemura, S., Hayashi, Y., Kawaguchi, M., Asada, M., Kato, M. & Yasuhara, K. (2007, November). Floating structure using waste tires for water environmental remediation. In Scrap Tire Derived Geomaterials-Opportunities and Challenges: Proceedings of the International Workshop IW-TDGM 2007. p. 291. CRC Press.
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.
|
May 2015 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
22 |
23 |
24 |
25 |
26 |
27 |
28 |
29 |
30 |
31 |
|
Mammals |
|
ü |
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
Birds |
|
ü |
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
Herpetofauna |
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
Dragonflies & butterflies |
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
Water Quality |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
Inspection Visits |
|
ü |
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
June 2015 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
22 |
23 |
24 |
25 |
26 |
27 |
28 |
29 |
30 |
|
|
Mammals |
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
Birds |
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
Herpetofauna |
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
Dragonflies & Butterflies |
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
Water Quality |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
Inspection Visits |
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
July 2015 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
22 |
23 |
24 |
25 |
26 |
27 |
28 |
29 |
30 |
31 |
|
Mammals |
|
|
ü |
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
Birds |
|
|
ü |
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
Herpetofauna |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Dragonflies & Butterflies |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
Water Quality |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
Inspection Visits |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
August 2015 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
22 |
23 |
24 |
25 |
26 |
27 |
28 |
29 |
30 |
31 |
|
Mammals |
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
Birds |
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
Herpetofauna |
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Dragonflies & Butterflies |
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Water Quality |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
Inspection Visits |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
|
September 2015 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
22 |
23 |
24 |
25 |
26 |
27 |
28 |
29 |
30 |
|
|
Mammals |
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
Birds |
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
Herpetofauna |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Dragonflies & Butterflies |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Water Quality |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
Inspection Visits |
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
|
October 2015 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
22 |
23 |
24 |
25 |
26 |
27 |
28 |
29 |
30 |
31 |
|
Mammals |
|
ü |
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
Birds |
|
ü |
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
|
ü |
|
|
|
|
|
Herpetofauna |
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Dragonflies & Butterflies |
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Water Quality |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Inspection Visits |
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
|
|
ü |
|
|
ü |
|
Note:
1. Light grey cells indicate public holidays, Saturdays or Sundays.
2. Dark cells indicate that no survey was required during the relevant month.
Table B1. Summary of bird species of conservation importance and/or wetland-dependence within the Survey Area (excluding the WRA) during reporting period
|
Common Name (3) |
Scientific Name (3) |
Conservation Status (1) |
Wetland Dependent |
May Mean (2) |
Jun Mean (2) |
Jul Mean (2) |
Aug Mean (2) |
Sep Mean (2) |
Oct Mean (2) |
|
Little Grebe |
Tachybaptus ruficollis |
LC |
ü |
6.2 |
5.0 |
5.0 |
12.3 |
12.6 |
5.8 |
|
Great Cormorant |
Phalacrocorax carbo |
PRC |
ü |
|
|
|
|
|
0.2 |
|
Grey Heron |
Ardea cinerea |
PRC |
ü |
0.2 |
|
|
|
1.8 |
6.6 |
|
Great Egret |
Ardea alba |
PRC, (RC) |
ü |
1.4 |
3.8 |
0.4 |
2.5 |
6.8 |
11.8 |
|
Intermediate Egret |
Egretta intermedia |
RC |
ü |
|
0.2 |
|
|
|
|
|
Little Egret |
Egretta garzetta |
PRC, (RC) |
ü |
10.8 |
11.2 |
4.6 |
11.5 |
18.4 |
17.4 |
|
Eastern Cattle Egret |
Bubulcus coromandus |
LC |
ü |
V |
|
|
|
1.2 |
10.4 |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (RC) |
ü |
8.0 |
8.2 |
7.4 |
11.3 |
18.2 |
14.8 |
|
Black-crowned Night Heron |
Nycticorax nycticorax |
(LC) |
ü |
1.4 |
1.8 |
|
3.3 |
0.4 |
0.6 |
|
Yellow Bittern |
Ixobrychus sinensis |
LC |
ü |
|
V |
|
|
V |
|
|
Black Kite |
Milvus migrans |
RC |
ü |
V |
0.2 |
|
|
|
V |
|
White-breasted Waterhen |
Amaurornis phoenicurus |
- |
ü |
1.4 |
3.0 |
1.0 |
2.3 |
0.8 |
1.0 |
|
Common Moorhen |
Gallinula chloropus |
- |
ü |
0.2 |
|
|
|
|
|
|
Black-winged Stilt |
Himantopus himantopus |
(RC) |
ü |
3.8 |
0.2 |
0.4 |
4.0 |
|
|
|
Little Ringed Plover |
Charadrius dubius |
(LC) |
ü |
0.6 |
1.0 |
0.4 |
|
|
|
|
Common Sandpiper |
Actitis hypoleucos |
- |
ü |
0.8 |
|
0.2 |
0.5 |
0.6 |
1.6 |
|
Whiskered Tern |
Chlidonias hybrida |
LC |
ü |
|
|
|
|
|
0.6 |
|
Pied Kingfisher |
Ceryle rudis |
(LC) |
ü |
|
|
|
0.3 |
1.6 |
0.6 |
|
White-throated Kingfisher |
Halcyon smyrnensis |
LC |
ü |
|
|
0.2 |
0.3 |
0.2 |
0.4 |
|
Common Kingfisher |
Alcedo atthis |
- |
ü |
1.0 |
V |
V |
1.0 |
3.0 |
2.8 |
|
Eastern Yellow Wagtail |
Cecropis daurica |
- |
ü |
0.2 |
|
|
|
|
|
|
White Wagtail |
Motacilla alba |
- |
ü |
1.2 |
0.6 |
0.6 |
0.3 |
1.4 |
4.4 |
|
Red-billed Starling |
Spodiopsar sericeus |
- |
ü |
V |
V |
|
|
|
|
|
White-cheeked Starling |
Spodiopsar cineraceus |
PRC |
ü |
|
0.6 |
0.8 |
|
|
|
|
White-shouldered Starling |
Sturnia sinensis |
(LC) |
x |
0.4 |
1.4 |
|
0.8 |
|
|
|
Collared Crow |
Corvus torquatus |
LC |
ü |
0.8 |
0.8 |
|
0.3 |
0.6 |
0.2 |
|
|
|
|
No. of species recorded |
19 |
17 |
12 |
14 |
15 |
17 |
Note:
(1) Conservation status follows that of Fellowes et al. (2002) and BirdLife International listing (2010). See Table B3.
(2) Refers to the mean number of individuals recorded in each survey in the Survey Area (excluding the WRA).
(3) Follows HK bird list (dated 2015-1-12).
“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 during reporting period
|
Common Name (3) |
Scientific Name (3) |
Conservation Status (1) |
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
Wetland Dependent |
Mean (2) |
Mean (2) |
Mean (2) |
Mean (2) |
Mean (2) |
Mean (2) |
|||
|
Little Grebe |
Tachybaptus ruficollis |
LC |
ü |
1.2 |
2.8 |
1.6 |
1.8 |
1.0 |
2.0 |
|
Great Cormorant |
Phalacrocorax carbo |
PRC |
ü |
|
|
|
|
|
0.2 |
|
Grey Heron |
Ardea cinerea |
PRC |
ü |
|
|
|
|
0.4 |
1.8 |
|
Purple Heron |
Ardea purpurea |
RC, LC |
ü |
|
|
|
|
|
0.2 |
|
Great Egret |
Ardea alba |
PRC, (RC) |
ü |
V |
|
0.2 |
0.3 |
1.8 |
1.0 |
|
Intermediate Egret |
Egretta intermedia |
RC |
ü |
|
|
|
|
V |
|
|
Little Egret |
Egretta garzetta |
PRC, (RC) |
ü |
1.4 |
0.6 |
0.2 |
1.8 |
2.0 |
1.8 |
|
Eastern Cattle Egret |
Bubulcus coromandus |
LC |
ü |
|
|
|
|
|
0.8 |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC, (RC) |
ü |
0.6 |
0.8 |
1.8 |
1.3 |
2.8 |
5.4 |
|
Black-crowned Night Heron |
Nycticorax nycticorax |
(LC) |
ü |
|
V |
V |
V |
|
V |
|
Yellow Bittern |
Ixobrychus sinensis |
LC |
ü |
0.4 |
1.6 |
0.6 |
1.0 |
0.6 |
2.6 |
|
Black-winged Kite |
Elanus caeruleus |
LC |
ü |
|
|
|
|
V |
|
|
Black Kite |
Milvus migrans |
RC |
ü |
0.2 |
0.2 |
|
|
0.2 |
0.4 |
|
Eastern Buzzard |
Buteo japonicus |
- |
ü |
|
|
|
|
|
0.2 |
|
Peregrine Falcon |
Falco peregrinus |
LC |
x |
|
|
V |
|
|
|
|
Baillon's Crake |
Porzana pusilla |
LC |
ü |
|
|
|
|
|
0.2 |
|
White-breasted Waterhen |
Amaurornis phoenicurus |
- |
ü |
V |
V |
0.2 |
V |
0.2 |
0.6 |
|
Watercock |
Gallicrex cinerea |
RC |
ü |
|
0.2 |
|
|
|
|
|
Common Moorhen |
Gallinula chloropus |
- |
ü |
|
|
|
|
|
V |
|
Pheasant-tailed Jacana |
Hydrophasianus chirurgus |
LC |
ü |
|
|
|
|
|
0.2 |
|
Black-winged Stilt |
Himantopus himantopus |
(RC) |
ü |
|
|
|
|
V |
|
|
Little Ringed Plover |
Charadrius dubius |
(LC) |
ü |
2.0 |
|
|
|
|
|
|
Green Sandpiper |
Tringa ochropus |
- |
ü |
|
|
|
|
|
V |
|
Common Sandpiper |
Actitis hypoleucos |
- |
ü |
|
|
|
0.3 |
1.2 |
0.6 |
|
Pied Kingfisher |
Ceryle rudis |
(LC) |
ü |
0.2 |
|
|
0.8 |
|
|
|
White-throated Kingfisher |
Halcyon smyrnensis |
LC |
ü |
|
|
|
|
0.2 |
0.4 |
|
Common Kingfisher |
Alcedo atthis |
- |
ü |
0.8 |
0.8 |
0.2 |
0.5 |
0.6 |
2.2 |
|
White Wagtail |
Motacilla alba |
- |
ü |
1.4 |
V |
|
0.3 |
0.4 |
0.4 |
|
Black-browed Reed Warbler |
Acrocephalus bistrigiceps |
- |
ü |
|
|
|
|
|
V |
|
Thick-billed Warbler |
Iduna aedon |
LC |
ü |
|
|
|
|
V |
|
|
Red-billed Starling |
Spodiopsar sericeus |
- |
ü |
V |
0.4 |
|
|
|
|
|
White-cheeked Starling |
Spodiopsar cineraceus |
PRC |
x |
|
|
|
|
0.2 |
|
|
White-shouldered Starling |
Sturnia sinensis |
(LC) |
ü |
|
0.8 |
V |
V |
|
|
|
Collared Crow |
Corvus torquatus |
LC |
ü |
0.2 |
|
|
|
V |
0.4 |
|
|
|
|
No. of species recorded |
13 |
12 |
10 |
12 |
18 |
23 |
Note:
(1) Conservation status follows that of Fellowes et al. (2002) and BirdLife International listing (2010). See Table B3.
(2) Refers to the mean number of individuals recorded in each survey in the Survey Area (excluding the WRA)
(3) Follows HK bird list (dated 2015-1-12)
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 Hong Kong would pose significant threat to global survival |
Fellowes et al. (2002) |
|
RC |
Regional Concern |
Habitat loss/damage in Hong Kong would pose significant threat to regional survival. |
|
|
LC |
Local Concern |
Habitat loss/damage in Hong Kong would pose significant threat to local survival. |
|
|
PGC |
Potential Global Concern |
Large, secure population in Hong Kong is of global significance. |
|
|
PRC |
Potential Regional Concern |
Large, secure population in Hong Kong is of regional significance. |
|
|
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 |
Wetland Dependent |
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 |
ü |
|
|
|
|
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 |
ü |
|
|
|
|
0.8 |
|
|
|
|
|
|
|
|
0.3 |
0.3 |
0.4 |
1.2 |
0.7 |
0.2 |
|
|
|
|
|
|
|
|
Grey Heron |
Ardea cinerea |
PRC |
ü |
|
|
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 |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
Great Egret |
Ardea alba |
PRC |
ü |
|
|
|
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 |
ü |
|
|
|
|
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 |
ü |
|
|
|
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) |
ü |
|
|
|
|
|
|
|
|
|
0.3 |
11.8 |
|
1.3 |
0.3 |
|
|
0.4 |
|
|
|
|
0.3 |
|
0.2 |
|
|
|
Chinese Pond Heron |
Ardeola bacchus |
PRC |
ü |
|
|
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) |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
Black-crowned Night Heron |
Nycticorax nycticorax |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Spoonbill |
Platalea leucorodia |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-faced Spoonbill |
Platalea minor |
PGC, EN |
ü |
|
|
|
|
0.3 |
10.3 |
|
|
|
|
|
|
|
|
|
|
0.4 |
|
|
|
|
|
|
|
|
|
|
Mandarin Duck |
Aix galericulata |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Wigeon |
Anas penelope |
RC |
ü |
|
|
|
1.6 |
2.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Teal |
Anas crecca |
RC |
ü |
|
|
|
|
1.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Pintail |
Anas acuta |
RC |
ü |
|
|
|
0.2 |
7.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Shoveler |
Anas clypeata |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Tufted Duck |
Aythya fuligula |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Garganey |
Anas querquedula |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Western Osprey |
Pandion haliaetus |
RC |
ü |
|
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black Kite |
Milvus migrans |
(RC) |
x |
|
|
|
|
0.8 |
0.3 |
0.2 |
|
0.3 |
|
|
|
0.3 |
|
|
|
0.2 |
|
|
0.2 |
0.5 |
|
|
|
|
0.4 |
|
Crested Serpent Eagle |
Spilornis cheela |
(LC) |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eastern Buzzard |
Buteo japonicus |
- |
x |
|
|
|
|
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Kestrel |
Falco tinnunculus |
- |
x |
|
|
1.0 |
0.4 |
1.0 |
0.3 |
0.4 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Hobby |
Falco subbuteo |
(LC) |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Peregrine Falcon |
Falco peregrinus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Imperial Eagle |
Aquila heliaca |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Japanese Quail |
Coturnix japonica |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
White-breasted Waterhen |
Amaurornis phoenicurus |
- |
ü |
|
|
|
|
|
|
|
|
0.5 |
0.8 |
1.3 |
2.6 |
1.3 |
1.5 |
0.3 |
|
|
|
0.4 |
|
|
0.5 |
1.0 |
0.5 |
|
|
|
Common Moorhen |
Gallinula chloropus |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
|
|
|
Pheasant-tailed Jacana |
Hydrophasianus chirurgus |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
Greater Painted-snipe |
Rostratula benghalensis |
LC |
ü |
|
|
|
|
|
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-winged Stilt |
Himantopus himantopus |
RC |
ü |
8.0 |
|
|
|
|
|
|
|
|
|
|
|
|
1.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Pied Avocet |
Recurvirostra avosetta |
RC |
ü |
|
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
|
|
|
|
|
|
|
Oriental Pratincole |
Glareola maldivarum |
LC |
ü |
|
|
|
|
|
|
|
2.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Little Ringed Plover |
Charadrius dubius |
LC |
ü |
3.0 |
|
24.5 |
7.4 |
3.8 |
9.0 |
6.8 |
10.5 |
5.5 |
0.5 |
|
0.2 |
|
|
|
|
|
1.0 |
0.6 |
|
|
|
|
|
|
|
|
Kentish Plover |
Charadrius alexandrinus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Spotted Redshank |
Tringa erythropus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Redshank |
Tringa totanus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Marsh Sandpiper |
Tringa stagnatilis |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Greenshank |
Tringa nebularia |
RC |
ü |
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
|
0.3 |
0.8 |
0.2 |
|
|
|
|
|
|
|
|
|
|
Green Sandpiper |
Tringa ochropus |
- |
ü |
|
|
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 |
ü |
|
|
|
|
|
0.5 |
1.2 |
|
|
|
|
|
|
|
|
|
|
0.8 |
0.3 |
|
|
|
|
0.6 |
|
|
|
Common Sandpiper |
Actitis hypoleucos |
- |
ü |
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 |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Pintail/Swinhoe's Snipe* |
Gallinago stenura/G. megala |
LC*, |
ü |
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Snipe |
Gallinago gallinago |
|
ü |
|
|
|
|
|
0.3 |
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Red-necked Stint |
Calidris ruficollis |
LC |
ü |
3.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Temminck's Stint |
Calidris temminckii |
LC |
ü |
|
|
0.5 |
|
|
2.5 |
0.4 |
1.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Long-toed Stint |
Calidris subminuta |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
Whiskered Tern |
Chlidonias hybrida |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1.3 |
|
|
|
|
|
|
Domestic Pigeon |
Columba livia |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Oriental Turtle Dove |
Streptopelia orientalis |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Red Turtle Dove |
Streptopelia tranquebarica |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Spotted Dove |
Spilopelia chinensis |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
DS |
|
DS |
|
|
DS |
|
0.6 |
|
Asian Koel |
Eudynamys scolopaceus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Greater Coucal# |
Centropus sinensis |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Eagle Owl |
Bubo bubo |
RC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Savanna Nightjar |
Caprimulgus affinis |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Pacific Swift |
Apus pacificus |
(LC) |
x |
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
House Swift |
Apus nipalensis |
- |
x |
10.0 |
|
|
|
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
DS |
DS |
|
|
|
|
|
|
|
|
Pied Kingfisher |
Ceryle rudis |
(LC) |
ü |
|
|
|
0.2 |
0.3 |
0.5 |
0.2 |
|
|
0.3 |
|
|
|
|
|
|
|
|
0.2 |
|
|
|
0.5 |
|
|
|
|
Common Kingfisher |
Alcedo atthis |
- |
ü |
|
|
|
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) |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
0.3 |
|
|
|
|
Barn Swallow |
Hirundo rustica |
- |
x |
25.0 |
|
|
|
|
1.5 |
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
|
DS |
|
DS |
DS |
3.0 |
|
|
Red-rumped Swallow |
Hirundo daurica |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eastern Yellow Wagtail |
Motacilla tschutschensis |
- |
ü |
|
|
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 |
- |
ü |
|
|
|
0.2 |
|
0.3 |
0.2 |
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
White Wagtail |
Motacilla alba |
- |
ü |
3.0 |
|
|
1.8 |
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
DS |
DS |
DS |
|
|
|
DS |
1.8 |
3.2 |
|
Richard's Pipit |
Anthus richardi |
- |
ü |
|
|
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 |
- |
x |
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
|
|
|
|
|
|
|
Red-throated Pipit |
Anthus cervinus |
LC |
x |
|
2.0 |
2.5 |
1.2 |
0.5 |
0.5 |
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
0.4 |
|
|
|
|
|
0.7 |
|
Buff-bellied Pipit |
Anthus rubescens |
LC |
x |
|
1.0 |
1.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Red-whiskered Bulbul |
Pycnonotus jocosus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Chinese Bulbul |
Pycnonotus sinensis |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
|
DS |
|
|
|
|
Long-tailed Shrike |
Lanius schach |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
|
|
|
|
DS |
DS |
|
|
|
Oriental Magpie Robin |
Copsychus saularis |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
|
|
|
|
|
Daurian Redstart |
Phoenicurus auroreus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Stejneger's Stonechat |
Saxicola stejnegeri |
- |
x |
|
3.0 |
0.5 |
1.0 |
1.0 |
0.8 |
0.2 |
0.3 |
|
|
|
|
|
1.0 |
|
DS |
DS |
|
DS |
|
|
|
|
|
|
|
|
Masked Laughingthrush |
Garrulax perspicillatus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
Lanceolated Warbler |
Locustella lanceolata |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Pallas's Grasshopper Warbler |
Locustella certhiola |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-browed Reed Warbler |
Acrocephalus bistrigiceps |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Zitting Cisticola |
Cisticola juncidis |
LC |
x |
|
|
|
|
|
|
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 |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
|
DS |
|
DS |
DS |
0.8 |
0.4 |
|
Plain Prinia |
Prinia inornata |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
|
DS |
DS |
|
|
|
Dusky Warbler |
Phylloscopus fuscatus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.5 |
|
DS |
|
|
|
|
|
|
|
|
|
|
|
Yellow-browed warbler |
Phylloscopus inornatus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1.4 |
|
Chinese Penduline-Tit |
Remiz consobrinus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1.2 |
0.2 |
|
|
|
|
|
|
|
Japanese White-eye |
Zosterops japonica |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Little Bunting |
Emberiza pusilla |
- |
x |
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-faced Bunting |
Emberiza spodocephala |
- |
x |
|
|
|
|
|
|
|
0.5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Chinese Grosbeak |
Eophona migratoria |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Scaly-breasted Munia |
Lonchura punctulata |
- |
x |
20.0 |
|
|
|
2.5 |
|
15.0 |
7.5 |
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
DS |
1.5 |
|
|
Eurasian Tree Sparrow |
Passer montanus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
DS |
|
DS |
|
|
|
|
Red-billed Starling |
Spodiopsar sericeus |
GC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
0.8 |
1.6 |
6.6 |
39.0 |
17.4 |
|
|
|
|
|
|
|
|
White-cheeked Starling |
Spodiopsar cineraceus |
PRC |
x |
|
|
|
|
|
|
|
|
|
|
|
6.6 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-collared Starling |
Gracupica nigricollis |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
DS |
DS |
|
|
|
|
DS |
|
|
|
White-shouldered Starling |
Sturnia sinensis |
(LC) |
x |
|
|
|
|
|
|
|
|
0.3 |
|
0.5 |
2.4 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Myna |
Acridotheres tristis |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
|
|
|
|
|
Crested Myna |
Acridotheres cristatellus |
– |
x |
3.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
DS |
|
|
DS |
|
V |
|
Black-napped Oriole |
Oriolus chinensis |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
1.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black Drongo |
Dicrurus macrocercus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
DS |
|
|
|
Azure-winged Magpie |
Cyanopica cyanus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Magpie |
Pica pica |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
DS |
|
|
|
|
DS |
0.3 |
|
|
Large-billed Crow |
Corvus macrorhynchos |
- |
x |
|
|
|
0.4 |
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Collared Crow |
Corvus torquatus |
LC, NT |
x |
|
|
|
0.2 |
0.3 |
|
|
0.5 |
|
0.3 |
|
0.8 |
0.8 |
0.8 |
0.5 |
|
|
|
|
|
|
0.8 |
|
|
|
|
|
No. of species recorded |
108 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Note: Conservation Status follows that of Fellowes et. al. (2002)
* 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 October 2014
|
Common name |
Scientific name |
Conservation status |
Wetland Dependent |
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 |
May-14 |
Jun-14 |
Jul-14 |
Aug-14 |
Sep-14 |
Oct-14 |
|
Little Grebe |
Tachybaptus ruficollis |
LC |
ü |
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 |
0.8 |
2.0 |
3.2 |
1.8 |
1.6 |
1.4 |
|
Great Cormorant |
Phalacrocorax carbo |
PRC |
ü |
0.8 |
3.2 |
0.8 |
1.0 |
0.0 |
0.0 |
|
|
|
|
|
0.2 |
V |
0.4 |
0.6 |
0.5 |
|
|
|
|
|
|
|
V |
|
Grey Heron |
Ardea cinerea |
PRC |
ü |
0.8 |
1.4 |
0.8 |
1.4 |
0.0 |
0.0 |
|
|
|
|
V |
1.0 |
2.8 |
2.6 |
1.6 |
2.5 |
|
|
|
|
|
|
1.0 |
1.6 |
|
Purple Heron |
Ardea purpurea |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Great Egret |
Ardea alba |
PRC |
ü |
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 |
V |
0.5 |
V |
V |
0.2 |
V |
|
Intermediate Egret |
Egretta intermedia |
RC |
ü |
0.2 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
V |
|
Little Egret |
Egretta garzetta |
PRC |
ü |
0.8 |
2.0 |
2.2 |
1.4 |
0.6 |
1.2 |
0.6 |
1.8 |
0.4 |
3.4 |
0.5 |
2.2 |
1.4 |
2.4 |
4.4 |
4.0 |
3.8 |
3.2 |
1.2 |
3.3 |
1.8 |
1.3 |
2.6 |
1.6 |
|
Eastern Cattle Egret |
Bubulcus coromandus |
(LC) |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1.6 |
V |
|
|
|
|
|
|
Chinese Pond Heron |
Ardeola bacchus |
PRC |
ü |
1.6 |
2.2 |
2.4 |
0.4 |
0.0 |
0.0 |
|
|
0.8 |
2.0 |
0.5 |
1.4 |
1.4 |
2.6 |
6.8 |
3.5 |
2.5 |
1.0 |
1.6 |
1.0 |
1.4 |
1.5 |
4.2 |
1.4 |
|
Yellow Bittern |
Ixobrychus sinensis |
(LC) |
ü |
|
|
|
|
|
V |
1.0 |
2.5 |
0.2 |
1.4 |
1.3 |
0.8 |
0.4 |
0.2 |
|
|
V |
V |
0.4 |
1.3 |
1.0 |
0.8 |
0.2 |
0.2 |
|
Black-crowned Night Heron |
Nycticorax nycticorax |
LC |
ü |
V |
|
|
0.2 |
|
|
|
0.3 |
|
|
|
V |
|
|
|
|
V |
|
V |
|
|
|
|
V |
|
Eurasian Spoonbill |
Platalea leucorodia |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-faced Spoonbill |
Platalea minor |
PGC, EN |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
V |
|
|
|
|
|
|
|
|
Mandarin Duck |
Aix galericulata |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Wigeon |
Anas penelope |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Teal |
Anas crecca |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Pintail |
Anas acuta |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Shoveler |
Anas clypeata |
RC |
ü |
|
|
V |
|
|
|
|
|
|
|
|
|
|
1.2 |
7.0 |
5.5 |
V |
|
|
|
|
|
|
|
|
Tufted Duck |
Aythya fuligula |
LC |
ü |
|
|
V |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Garganey |
Anas querquedula |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Western Osprey |
Pandion haliaetus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black Kite |
Milvus migrans |
(RC) |
x |
0.0 |
0.2 |
0.0 |
0.0 |
0.6 |
0.0 |
0.2 |
0.3 |
|
1.2 |
0.8 |
0.2 |
0.2 |
|
V |
0.5 |
0.8 |
0.4 |
0.6 |
0.3 |
0.6 |
|
|
0.4 |
|
Crested Serpent Eagle |
Spilornis cheela |
(LC) |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
|
|
Eastern Buzzard |
Buteo japonicus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
Common Kestrel |
Falco tinnunculus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Hobby |
Falco subbuteo |
(LC) |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
Peregrine Falcon |
Falco peregrinus |
- |
x |
|
V |
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
|
|
|
|
Imperial Eagle |
Aquila heliaca |
- |
x |
|
|
V |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Japanese Quail |
Coturnix japonica |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
|
|
|
|
|
|
White-breasted Waterhen |
Amaurornis phoenicurus |
- |
ü |
0.2 |
|
0.2 |
0.0 |
0.4 |
0.2 |
V |
1.8 |
0.2 |
0.2 |
V |
0.8 |
0.4 |
|
|
|
V |
0.2 |
0.2 |
V |
1.4 |
0.5 |
0.5 |
0.2 |
|
Common Moorhen |
Gallinula chloropus |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
0.2 |
|
|
|
|
|
|
|
Pheasant-tailed Jacana |
Hydrophasianus chirurgus |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Greater Painted-snipe |
Rostratula benghalensis |
LC |
ü |
0.2 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-winged Stilt |
Himantopus himantopus |
RC |
ü |
|
|
|
|
|
|
|
|
0.2 |
0.6 |
V |
0.2 |
V |
|
|
|
|
|
|
|
|
|
V |
V |
|
Pied Avocet |
Recurvirostra avosetta |
RC |
ü |
0.0 |
0.2 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Oriental Pratincole |
Glareola maldivarum |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Little Ringed Plover |
Charadrius dubius |
LC |
ü |
0.0 |
0.0 |
0.4 |
1.0 |
0.2 |
0.0 |
|
|
|
|
|
V |
0.4 |
|
V |
0.5 |
0.8 |
|
|
0.3 |
|
|
|
1.2 |
|
Kentish Plover |
Charadrius alexandrinus |
RC |
ü |
|
|
|
|
|
|
|
|
0.8 |
|
|
|
V |
|
|
|
|
|
|
|
|
|
|
|
|
Spotted Redshank |
Tringa erythropus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Redshank |
Tringa totanus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Marsh Sandpiper |
Tringa stagnatilis |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Greenshank |
Tringa nebularia |
RC |
ü |
V |
V |
V |
|
V |
|
|
|
|
|
|
|
|
V |
V |
|
V |
|
|
|
|
|
|
V |
|
Green Sandpiper |
Tringa ochropus |
- |
ü |
|
|
|
|
|
0.2 |
|
|
|
|
|
1.0 |
0.6 |
V |
|
|
0.5 |
|
|
|
|
V |
|
V |
|
Wood Sandpiper |
Tringa glareola |
LC |
ü |
|
V |
|
V |
V |
|
|
|
|
|
|
V |
V |
V |
V |
V |
V |
|
|
|
0.4 |
0.3 |
|
0.2 |
|
Common Sandpiper |
Actitis hypoleucos |
- |
ü |
0.2 |
|
|
|
|
0.2 |
0.2 |
|
V |
0.6 |
V |
0.8 |
1.6 |
0.2 |
V |
0.3 |
1.3 |
0.2 |
0.4 |
V |
V |
0.3 |
2.6 |
4.4 |
|
Eurasian Woodcock |
Scolopax rusticola |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Pintail/Swinhoe's Snipe* |
Gallinago stenura/G. megala |
LC* |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
|
|
|
|
|
Common Snipe |
Gallinago gallinago |
- |
ü |
|
V |
|
|
|
V |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Red-necked Stint |
Calidris ruficollis |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Temminck's Stint |
Calidris temminckii |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.6 |
|
Long-toed Stint |
Calidris subminuta |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Whiskered Tern |
Chlidonias hybrida |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Domestic Pigeon |
Columba livia |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Collared Dove |
Streptopelia decaocto |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
Oriental Turtle Dove |
Streptopelia orientalis |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Red Turtle Dove |
Streptopelia tranquebarica |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Spotted Dove |
Spilopelia chinensis |
- |
x |
0.4 |
1.2 |
0.4 |
|
0.2 |
0.2 |
0.4 |
0.5 |
0.8 |
2.8 |
2.0 |
2.6 |
2.6 |
3.0 |
6.2 |
2.3 |
2.0 |
1.0 |
0.6 |
1.6 |
1.2 |
1.3 |
2.2 |
3.6 |
|
Asian Koel |
Eudynamys scolopaceus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
Greater Coucal# |
Centropus sinensis |
- |
x |
|
|
|
|
|
|
0.2 |
0.3 |
0.2 |
0.2 |
|
0.2 |
0.2 |
|
|
|
|
0.4 |
0.8 |
0.3 |
0.8 |
0.5 |
0.2 |
0.2 |
|
Eurasian Eagle Owl |
Bubo bubo |
RC |
x |
|
|
|
|
|
|
|
|
|
|
V |
|
V |
|
|
V |
|
|
|
|
|
|
|
|
|
Savanna Nightjar |
Caprimulgus affinis |
- |
x |
|
|
|
V |
|
|
|
V |
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
|
Pacific Swift |
Apus pacificus |
(LC) |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
House Swift |
Apus nipalensis |
- |
x |
|
0.4 |
V |
|
|
|
|
|
|
|
|
|
|
|
V |
0.5 |
|
|
|
|
|
|
|
|
|
Pied Kingfisher |
Ceryle rudis |
(LC) |
ü |
|
|
|
|
|
V |
|
|
|
V |
|
|
|
0.4 |
V |
0.3 |
V |
|
|
|
V |
|
|
|
|
Common Kingfisher |
Alcedo atthis |
- |
ü |
0.2 |
0.2 |
0.5 |
0.4 |
0.2 |
0.2 |
0.6 |
0.3 |
0.4 |
0.4 |
0.8 |
1.0 |
2.0 |
1.6 |
1.2 |
2.3 |
0.8 |
1.0 |
|
|
V |
|
|
|
|
White-throated Kingfisher |
Halcyon smyrnensis |
(LC) |
x |
|
|
|
|
|
|
|
|
|
|
|
|
V |
0.2 |
|
|
|
|
1.2 |
1.8 |
0.6 |
1.3 |
1.4 |
1.8 |
|
Barn Swallow |
Hirundo rustica |
- |
x |
0.2 |
1.0 |
|
0.2 |
9.2 |
23.0 |
11.2 |
|
1.4 |
1.8 |
1.0 |
|
V |
|
|
0.5 |
7.8 |
15.4 |
18.0 |
1.5 |
1.0 |
1.5 |
0.4 |
V |
|
Red-rumped Swallow |
Hirundo daurica |
- |
x |
1.2 |
1.2 |
|
|
|
|
|
|
|
|
|
|
|
|
0.6 |
|
|
|
|
|
|
|
|
|
|
Eastern Yellow Wagtail |
Motacilla tschutschensis |
- |
ü |
0.2 |
0.2 |
1.4 |
2.8 |
2.2 |
2.2 |
0.2 |
|
|
|
|
0.4 |
0.2 |
0.6 |
0.6 |
1.0 |
0.3 |
0.2 |
|
|
|
|
0.6 |
0.2 |
|
Grey Wagtail |
Motacilla cinerea |
- |
ü |
0.6 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
White Wagtail |
Motacilla alba |
- |
ü |
2.6 |
1.0 |
1.0 |
3.0 |
4.8 |
2.0 |
1.0 |
|
1.2 |
0.4 |
3.5 |
2.8 |
3.6 |
2.6 |
1.2 |
1.3 |
2.5 |
1.6 |
0.6 |
1.2 |
0.8 |
1.8 |
1.8 |
3.2 |
|
Richard's Pipit |
Anthus richardi |
- |
ü |
0.2 |
0.4 |
1.2 |
0.4 |
0.4 |
|
|
|
|
|
|
|
|
0.4 |
0.8 |
2.0 |
2.3 |
3.0 |
V |
|
|
|
|
V |
|
Olive-backed Pipit |
Anthus hodgsoni |
- |
x |
|
|
|
0.6 |
1.2 |
1.4 |
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
|
|
|
|
|
|
Red-throated Pipit |
Anthus cervinus |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Buff-bellied Pipit |
Anthus rubescens |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Red-whiskered Bulbul |
Pycnonotus jocosus |
- |
x |
|
|
|
|
|
0.2 |
|
0.3 |
|
0.2 |
|
|
V |
|
0.8 |
1.3 |
0.3 |
0.2 |
|
|
0.2 |
0.3 |
1.2 |
|
|
Chinese Bulbul |
Pycnonotus sinensis |
- |
x |
|
0.2 |
2.0 |
0.2 |
0.2 |
3.2 |
2.0 |
3.8 |
|
2.4 |
3.5 |
0.2 |
1.8 |
4.0 |
3.8 |
0.5 |
0.8 |
1.6 |
1.8 |
2.3 |
2.2 |
2.3 |
0.4 |
4.6 |
|
Bull-headed Shrike |
Lanius bucephalus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
Long-tailed Shrike |
Lanius schach |
- |
x |
0.2 |
|
0.4 |
|
|
0.2 |
|
V |
0.4 |
0.2 |
0.3 |
0.2 |
|
0.2 |
V |
0.3 |
|
|
0.2 |
0.3 |
0.4 |
0.5 |
V |
|
|
Oriental Magpie Robin |
Copsychus saularis |
- |
x |
|
0.2 |
|
|
|
|
0.2 |
0.5 |
|
0.2 |
0.3 |
V |
0.2 |
0.2 |
0.4 |
|
|
0.2 |
|
0.3 |
V |
V |
V |
|
|
Daurian Redstart |
Phoenicurus auroreus |
- |
x |
|
|
0.2 |
|
|
|
|
|
|
|
|
|
0.2 |
0.2 |
0.4 |
|
|
|
|
|
|
|
|
V |
|
Stejneger's Stonechat |
Saxicola stejnegeri |
- |
x |
0.4 |
0.4 |
0.8 |
|
|
0.6 |
|
|
|
|
|
V |
0.2 |
0.2 |
0.4 |
0.5 |
0.3 |
V |
0.2 |
|
|
|
|
0.4 |
|
Masked Laughingthrush |
Garrulax perspicillatus |
- |
x |
|
|
|
|
0.6 |
1.2 |
|
|
|
|
1.0 |
|
|
0.4 |
0.8 |
V |
0.5 |
0.2 |
0.2 |
0.5 |
V |
1.5 |
0.8 |
|
|
Lanceolated Warbler |
Locustella lanceolata |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Pallas's Grasshopper Warbler |
Locustella certhiola |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Oriental Reed Warbler |
Acrocephalus orientalis |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
Black-browed Reed Warbler |
Acrocephalus bistrigiceps |
- |
ü |
0.2 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Tailorbird |
Orthotomus sutorius |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
Zitting Cisticola |
Cisticola juncidis |
LC |
x |
|
0.2 |
|
|
V |
|
|
|
|
|
|
|
|
|
0.4 |
|
0.3 |
0.2 |
|
|
|
|
|
|
|
Yellow-bellied Prinia |
Prinia flaviventris |
- |
x |
|
0.8 |
0.6 |
0.8 |
1.4 |
4.6 |
4.4 |
5.0 |
2.4 |
1.8 |
3.0 |
2.4 |
0.8 |
1.0 |
0.8 |
1.3 |
2.8 |
0.8 |
0.8 |
0.4 |
|
|
0.4 |
|
|
Plain Prinia |
Prinia inornata |
- |
x |
1.2 |
0.4 |
V |
1.4 |
0.2 |
0.2 |
0.2 |
0.5 |
0.8 |
0.4 |
0.3 |
|
0.4 |
|
0.2 |
V |
0.8 |
2.0 |
1.0 |
|
2.6 |
4.3 |
3.4 |
|
|
Dusky Warbler |
Phylloscopus fuscatus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
V |
0.4 |
|
0.4 |
0.8 |
1.5 |
V |
|
|
|
|
V |
V |
|
Yellow-browed warbler |
Phylloscopus inornatus |
- |
x |
0.8 |
0.6 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.8 |
0.5 |
|
V |
|
Chinese Penduline-Tit |
Remiz consobrinus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
4.5 |
V |
|
|
|
|
|
|
|
|
Japanese White-eye |
Zosterops japonica |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
|
0.6 |
|
|
V |
|
|
|
|
Little Bunting |
Emberiza pusilla |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-faced Bunting |
Emberiza spodocephala |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
|
Chinese Grosbeak |
Eophona migratoria |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Scaly-breasted Munia |
Lonchura punctulata |
- |
x |
|
|
|
1.0 |
2.2 |
1.0 |
|
|
2.0 |
0.4 |
0.3 |
|
|
1.8 |
1.8 |
V |
1.8 |
V |
3.2 |
5.8 |
0.8 |
1.5 |
1.3 |
|
|
Eurasian Tree Sparrow |
Passer montanus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
0.8 |
V |
|
|
|
|
|
|
|
|
V |
8.8 |
3.6 |
|
Red-billed Starling |
Spodiopsar sericeus |
GC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
V |
|
|
|
V |
|
|
White-cheeked Starling |
Spodiopsar cineraceus |
PRC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-collared Starling |
Gracupica nigricollis |
- |
x |
|
|
0.8 |
0.4 |
0.2 |
0.2 |
0.2 |
|
|
|
0.8 |
|
0.8 |
1.6 |
0.8 |
0.5 |
1.8 |
0.2 |
0.2 |
V |
1.0 |
1.0 |
1.2 |
1.4 |
|
White-shouldered Starling |
Sturnia sinensis |
(LC) |
x |
|
|
|
|
|
|
|
|
0.2 |
|
|
|
|
|
|
|
|
|
|
V |
|
V |
|
V |
|
Common Myna |
Acridotheres tristis |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
Crested Myna |
Acridotheres cristatellus |
- |
x |
0.6 |
|
|
|
|
|
0.2 |
0.3 |
0.8 |
0.2 |
|
|
2.0 |
1.8 |
1.4 |
0.5 |
1.3 |
1.0 |
0.6 |
1.0 |
1.2 |
3.5 |
0.2 |
1.8 |
|
Black-naped Oriole |
Oriolus chinensis |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black Drongo |
Dicrurus macrocercus |
- |
x |
|
|
|
|
|
|
|
|
|
|
0.3 |
0.4 |
V |
|
|
|
|
V |
|
|
|
1.5 |
|
0.2 |
|
Azure-winged Magpie |
Cyanopica cyanus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
V |
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Magpie |
Pica pica |
- |
x |
|
|
|
|
|
|
|
0.3 |
|
|
|
|
V |
|
0.8 |
V |
0.3 |
0.2 |
|
|
|
|
|
|
|
Large-billed Crow |
Corvus macrorhynchos |
- |
x |
|
|
|
|
|
|
|
1.0 |
|
|
|
|
|
|
|
|
|
|
|
0.3 |
|
|
|
|
|
Collared Crow |
Corvus torquatus |
LC, NT |
x |
|
|
|
|
|
V |
|
|
|
|
|
0.2 |
0.2 |
|
|
V |
0.5 |
0.8 |
0.4 |
|
0.6 |
|
0.4 |
V |
|
No. of species recorded |
112 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Note: Conservation Status follows that of Fellowes et. al. (2002)
* 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 B6. Summary of Bird Species Recorded at the WRA and their Respective Monthly Mean between November 2014 and October 2015
|
Common name |
Scientific name |
Conservation status |
Wetland Dependent |
Nov-14 |
Dec-14 |
Jan-15 |
Feb-15 |
Mar-15 |
Apr-15 |
May-15 |
Jun-15 |
Jul-15 |
Aug-15 |
Sep-15 |
Oct-15 |
|
Little Grebe |
Tachybaptus ruficollis |
LC |
ü |
2.5 |
1.2 |
2.0 |
2.0 |
2.0 |
0.8 |
1.2 |
2.8 |
1.6 |
1.8 |
1.0 |
2.0 |
|
Great Cormorant |
Phalacrocorax carbo |
PRC |
ü |
0.5 |
1.8 |
2.0 |
0.8 |
0.6 |
|
|
|
|
|
|
0.2 |
|
Grey Heron |
Ardea cinerea |
PRC |
ü |
2.3 |
2.6 |
5.3 |
4.8 |
0.8 |
V |
|
|
|
|
0.4 |
1.8 |
|
Purple Heron |
Ardea purpurea |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
Great Egret |
Ardea alba |
PRC |
ü |
0.5 |
1.6 |
0.8 |
0.3 |
V |
0.3 |
V |
|
0.2 |
0.3 |
1.8 |
1.0 |
|
Intermediate Egret |
Egretta intermedia |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
V |
|
|
Little Egret |
Egretta garzetta |
PRC |
ü |
3.0 |
3.6 |
5.3 |
3.5 |
4.6 |
6.3 |
1.4 |
0.6 |
0.2 |
1.8 |
2.0 |
1.8 |
|
Eastern Cattle Egret |
Bubulcus coromandus |
(LC) |
ü |
|
|
V |
|
|
|
|
|
|
|
|
0.8 |
|
Chinese Pond Heron |
Ardeola bacchus |
PRC |
ü |
2.0 |
2.8 |
2.3 |
2.8 |
1.2 |
1.8 |
0.6 |
0.8 |
1.8 |
1.3 |
2.8 |
5.4 |
|
Yellow Bittern |
Ixobrychus sinensis |
(LC) |
ü |
0.3 |
0.2 |
|
|
0.2 |
0.5 |
0.4 |
1.6 |
0.6 |
1.0 |
0.6 |
2.6 |
|
Cinnamon Bittern |
Ixobrychus cinnamomeus |
LC |
ü |
|
|
|
|
|
V |
|
|
|
|
|
|
|
Black-crowned Night Heron |
Nycticorax nycticorax |
LC |
ü |
|
|
|
|
|
|
|
V |
V |
V |
|
V |
|
Eurasian Spoonbill |
Platalea leucorodia |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-faced Spoonbill |
Platalea minor |
PGC, EN |
ü |
|
V |
V |
|
V |
|
|
|
|
|
|
|
|
Mandarin Duck |
Aix galericulata |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Wigeon |
Anas penelope |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Teal |
Anas crecca |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Pintail |
Anas acuta |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Northern Shoveler |
Anas clypeata |
RC |
ü |
|
0.2 |
|
|
|
|
|
|
|
|
|
|
|
Tufted Duck |
Aythya fuligula |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Garganey |
Anas querquedula |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Western Osprey |
Pandion haliaetus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-winged Kite |
Elanus caeruleus |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
V |
|
|
Black Kite |
Milvus migrans |
(RC) |
x |
|
0.4 |
|
0.3 |
0.4 |
0.5 |
0.2 |
0.2 |
|
|
0.2 |
0.4 |
|
Crested Serpent Eagle |
Spilornis cheela |
(LC) |
x |
|
|
|
|
|
|
0.4 |
|
|
|
|
|
|
Eastern Buzzard |
Buteo japonicus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
Common Kestrel |
Falco tinnunculus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
V |
|
Eurasian Hobby |
Falco subbuteo |
(LC) |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Peregrine Falcon |
Falco peregrinus |
- |
x |
|
|
0.3 |
|
|
|
|
|
V |
|
|
|
|
Greater Spotted Eagle |
Clanga clanga |
GC |
x |
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
Imperial Eagle |
Aquila heliaca |
- |
x |
|
|
|
V |
0.2 |
|
|
|
|
|
|
|
|
Japanese Quail |
Coturnix japonica |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Baillon’s Crake |
Porzana pusilla |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
White-breasted Waterhen |
Amaurornis phoenicurus |
- |
ü |
0.5 |
V |
0.8 |
1.0 |
0.8 |
0.3 |
V |
V |
0.2 |
V |
0.2 |
0.6 |
|
Watercock |
GallicreN cinerea |
RC |
ü |
|
|
|
|
|
|
|
0.2 |
|
|
|
|
|
Common Moorhen |
Gallinula chloropus |
- |
ü |
V |
|
V |
|
0.2 |
|
|
|
|
|
|
V |
|
Pheasant-tailed Jacana |
Hydrophasianus chirurgus |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
0.2 |
|
Greater Painted-snipe |
Rostratula benghalensis |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-winged Stilt |
Himantopus himantopus |
RC |
ü |
|
|
|
0.3 |
0.2 |
|
|
|
|
|
V |
|
|
Pied Avocet |
Recurvirostra avosetta |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Oriental Pratincole |
Glareola maldivarum |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Little Ringed Plover |
Charadrius dubius |
LC |
ü |
1.8 |
0.2 |
0.8 |
0.5 |
1.6 |
1.8 |
2.0 |
|
|
|
|
|
|
Kentish Plover |
Charadrius alexandrinus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Spotted Redshank |
Tringa erythropus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Redshank |
Tringa totanus |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Marsh Sandpiper |
Tringa stagnatilis |
RC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Greenshank |
Tringa nebularia |
RC |
ü |
V |
V |
V |
|
|
|
|
|
|
|
|
|
|
Green Sandpiper |
Tringa ochropus |
- |
ü |
0.3 |
0.2 |
|
0.3 |
0.2 |
|
|
|
|
|
|
V |
|
Wood Sandpiper |
Tringa glareola |
LC |
ü |
|
2.2 |
V |
V |
V |
1.0 |
|
|
|
|
|
|
|
Common Sandpiper |
Actitis hypoleucos |
- |
ü |
0.8 |
1.2 |
3.0 |
2.0 |
2.2 |
0.5 |
|
|
|
0.3 |
1.2 |
0.6 |
|
Eurasian Woodcock |
Scolopax rusticola |
- |
ü |
|
V |
|
|
|
|
|
|
|
|
|
|
|
Pintail/Swinhoe's Snipe* |
Gallinago stenura/G. megala |
LC*,- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Snipe |
Gallinago gallinago |
- |
ü |
|
|
|
|
V |
|
|
|
|
|
|
|
|
Red-necked Stint |
Calidris ruficollis |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Temminck's Stint |
Calidris temminckii |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Long-toed Stint |
Calidris subminuta |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Whiskered Tern |
Chlidonias hybrida |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Domestic Pigeon |
Columba livia |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Collared Dove |
Streptopelia decaocto |
- |
x |
|
|
|
|
|
0.5 |
0.4 |
|
|
|
|
|
|
Oriental Turtle Dove |
Streptopelia orientalis |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Red Turtle Dove |
Streptopelia tranquebarica |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Spotted Dove |
Spilopelia chinensis |
- |
x |
1.5 |
4.2 |
3.8 |
1.3 |
2.2 |
6.0 |
3.6 |
1.6 |
2.2 |
2.0 |
3.0 |
3.4 |
|
Asian Koel |
Eudynamys scolopaceus |
- |
x |
|
|
|
|
V |
|
0.2 |
0.2 |
|
0.3 |
V |
|
|
Greater Coucal# |
Centropus sinensis |
|
x |
V |
0.2 |
0.3 |
0.3 |
0.6 |
1.0 |
0.4 |
0.2 |
0.2 |
V |
V |
|
|
Eurasian Eagle Owl |
Bubo bubo |
RC |
x |
|
|
|
V |
|
|
|
|
|
|
|
|
|
Savanna Nightjar |
Caprimulgus affinis |
- |
x |
|
|
|
V |
|
|
|
|
|
|
|
|
|
Pacific Swift |
Apus pacificus |
(LC) |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
House Swift |
Apus nipalensis |
- |
x |
|
|
14.5 |
105.8 |
14.4 |
0.8 |
|
0.2 |
|
|
|
|
|
Pied Kingfisher |
Ceryle rudis |
(LC) |
ü |
|
0.4 |
0.5 |
0.3 |
0.2 |
|
0.2 |
|
|
0.8 |
|
|
|
Common Kingfisher |
Alcedo atthis |
- |
ü |
1.3 |
0.8 |
1.8 |
2.8 |
1.4 |
1.5 |
|
|
|
|
0.2 |
0.4 |
|
White-throated Kingfisher |
Halcyon smyrnensis |
(LC) |
x |
|
0.2 |
|
|
|
0.3 |
0.8 |
0.8 |
0.2 |
0.5 |
0.6 |
2.2 |
|
Eurasian Hoopoe |
Upupa epops |
- |
x |
|
|
|
0.3 |
|
|
|
|
|
|
|
|
|
Barn Swallow |
Hirundo rustica |
- |
x |
0.5 |
|
13.0 |
15.3 |
14.4 |
9.8 |
0.2 |
2.2 |
0.8 |
V |
0.8 |
V |
|
Red-rumped Swallow |
Hirundo daurica |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Eastern Yellow Wagtail |
Motacilla tschutschensis |
- |
ü |
1.8 |
0.4 |
2.0 |
4.3 |
2.0 |
1.0 |
|
|
|
|
|
|
|
Grey Wagtail |
Motacilla cinerea |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
White Wagtail |
Motacilla alba |
- |
ü |
4.0 |
5.6 |
6.3 |
9.5 |
4.8 |
3.3 |
1.4 |
V |
|
0.3 |
0.4 |
0.4 |
|
Richard's Pipit |
Anthus richardi |
- |
ü |
0.3 |
|
0.5 |
V |
|
|
|
|
|
|
|
|
|
Olive-backed Pipit |
Anthus hodgsoni |
- |
x |
0.3 |
2.2 |
0.3 |
1.5 |
0.4 |
|
|
|
|
|
|
|
|
Red-throated Pipit |
Anthus cervinus |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Buff-bellied Pipit |
Anthus rubescens |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Red-whiskered Bulbul |
Pycnonotus jocosus |
- |
x |
0.8 |
3.4 |
7.3 |
1.3 |
0.6 |
0.8 |
1.0 |
2.6 |
5.8 |
4.5 |
1.4 |
1.0 |
|
Chinese Bulbul |
Pycnonotus sinensis |
- |
x |
5.3 |
3.0 |
24.8 |
10.0 |
4.8 |
6.3 |
5.6 |
4.6 |
2.6 |
1.8 |
2.6 |
1.4 |
|
Bull-headed Shrike |
Lanius bucephalus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Brown Shrike |
Lanius cristatus |
- |
x |
|
|
|
|
|
0.3 |
|
|
|
|
|
|
|
Long-tailed Shrike |
Lanius schach |
- |
x |
|
0.2 |
0.8 |
0.5 |
0.4 |
|
|
|
|
0.3 |
0.4 |
0.4 |
|
Oriental Magpie Robin |
Copsychus saularis |
- |
x |
|
0.2 |
0.5 |
0.8 |
0.6 |
0.5 |
0.2 |
1.2 |
0.2 |
|
|
0.2 |
|
Daurian Redstart |
Phoenicurus auroreus |
- |
x |
0.3 |
1.6 |
0.8 |
0.5 |
0.6 |
|
|
|
|
|
|
|
|
Stejneger's Stonechat |
Saxicola stejnegeri |
- |
x |
0.3 |
0.2 |
0.3 |
0.8 |
0.8 |
0.3 |
|
|
|
|
|
2.2 |
|
Masked Laughingthrush |
Garrulax perspicillatus |
- |
x |
|
1.2 |
|
1.5 |
1.0 |
1.3 |
1.2 |
0.4 |
2.4 |
3.0 |
1.2 |
V |
|
Lanceolated Warbler |
Locustella lanceolata |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Pallas's Grasshopper Warbler |
Locustella certhiola |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Oriental Reed Warbler |
Acrocephalus orientalis |
- |
ü |
|
|
|
|
|
|
|
|
|
|
|
|
|
Thick-billed Warbler |
Acrocephalus aedon |
LC |
ü |
|
|
|
|
|
|
|
|
|
|
V |
|
|
Black-browed Reed Warbler |
Acrocephalus bistrigiceps |
- |
ü |
|
V |
|
|
|
|
|
|
|
|
|
V |
|
Common Tailorbird |
Orthotomus sutorius |
- |
x |
0.5 |
1.2 |
1.0 |
1.5 |
0.4 |
|
|
|
|
0.8 |
|
|
|
Zitting Cisticola |
Cisticola juncidis |
LC |
ü |
|
|
|
V |
V |
|
|
|
|
|
|
|
|
Yellow-bellied Prinia |
Prinia flaviventris |
- |
x |
0.5 |
|
0.3 |
0.3 |
2.6 |
0.8 |
2.0 |
1.5 |
|
|
|
|
|
Plain Prinia |
Prinia inornata |
- |
x |
2.8 |
0.2 |
1.3 |
3.5 |
1.6 |
2.8 |
1.2 |
1.0 |
1.6 |
1.5 |
0.6 |
0.6 |
|
Dusky Warbler |
Phylloscopus fuscatus |
- |
x |
|
|
|
V |
V |
|
|
|
|
|
|
|
|
Pallas's Leaf Warbler |
Phylloscopus proregulus |
|
x |
|
V |
|
|
|
|
|
|
|
|
|
|
|
Yellow-browed warbler |
Phylloscopus inornatus |
- |
x |
0.3 |
0.2 |
0.3 |
|
|
|
|
|
|
|
|
|
|
Chinese Penduline-Tit |
Remiz consobrinus |
RC |
ü |
|
0.4 |
1.5 |
4.5 |
3.2 |
V |
|
|
|
|
|
|
|
Japanese White-eye |
Zosterops japonica |
- |
x |
|
1.0 |
V |
V |
0.2 |
|
0.2 |
V |
3.8 |
4.3 |
|
|
|
Little Bunting |
Emberiza pusilla |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-faced Bunting |
Emberiza spodocephala |
- |
x |
|
|
|
|
V |
|
|
|
|
|
|
|
|
Chinese Grosbeak |
Eophona migratoria |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Scaly-breasted Munia |
Lonchura punctulata |
- |
x |
3.3 |
0.6 |
V |
V |
4.0 |
11.3 |
0.6 |
V |
V |
3.3 |
1.6 |
0.4 |
|
Eurasian Tree Sparrow |
Passer montanus |
- |
x |
|
V |
4.5 |
4.0 |
1.4 |
|
0.2 |
|
0.4 |
|
0.6 |
0.4 |
|
Red-billed Starling |
Spodiopsar sericeus |
GC |
x |
|
|
|
24.5 |
V |
|
V |
0.4 |
|
|
|
|
|
White-cheeked Starling |
Spodiopsar cineraceus |
PRC |
x |
|
V |
|
|
|
|
|
|
|
|
0.2 |
|
|
Black-collared Starling |
Gracupica nigricollis |
- |
x |
0.3 |
3.0 |
1.3 |
2.0 |
4.2 |
2.3 |
2.0 |
1.0 |
1.6 |
1.8 |
0.4 |
1.6 |
|
White-shouldered Starling |
Sturnia sinensis |
(LC) |
x |
|
|
|
|
|
|
|
0.8 |
V |
V |
|
|
|
Common Myna |
Acridotheres tristis |
- |
x |
|
|
|
|
|
|
|
|
|
|
0.4 |
|
|
Crested Myna |
Acridotheres cristatellus |
– |
x |
2.8 |
4.0 |
|
0.5 |
2.2 |
2.3 |
2.8 |
6.8 |
0.4 |
1.8 |
0.2 |
0.6 |
|
Black-naped Oriole |
Oriolus chinensis |
LC |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Black Drongo |
Dicrurus macrocercus |
- |
x |
|
V |
|
|
|
|
|
|
|
2.3 |
1.6 |
0.6 |
|
Azure-winged Magpie |
Cyanopica cyanus |
- |
x |
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Magpie |
Pica pica |
- |
x |
|
|
0.3 |
0.8 |
V |
0.5 |
|
|
V |
|
|
|
|
Large-billed Crow |
Corvus macrorhynchos |
- |
x |
|
|
|
|
|
|
|
|
|
0.5 |
|
|
|
Collared Crow |
Corvus torquatus |
LC, NT |
x |
|
|
|
|
|
V |
0.2 |
|
|
|
V |
0.4 |
|
No. of species recorded |
121 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Note: Conservation Status follows that of Fellowes et. al. (2002)
* 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).
Appendix C. Summary of Herpetofauna Monitoring, Mammals and Insects Surveys |
Table C1. Summary of herpetofauna monitoring within the Survey Area (excluding the WRA)
|
Common Name |
Scientific Name |
Conservation Status(1) |
Mean (2) |
|||||
|
Amphibians |
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
Asian Common Toad |
Bufo melanostictus |
- |
2.0 |
|
|
|
|
|
|
Gunther's Frog |
Hylarana guentheri |
- |
1.0 |
0.5 |
0.5 |
|
|
|
|
|
|
No. of Species Recorded |
2 |
1 |
1 |
0 |
0 |
0 |
|
Reptiles |
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
Changeable Lizard |
Calotes versicolor |
- |
0.5 |
|
|
|
|
|
|
|
|
No. of Species Recorded |
1 |
0 |
0 |
0 |
0 |
0 |
(1) Conservation status follows that of Fellowes et al. (2002), Chan et al. (2005) and Karsen et al. (1998).
(2) Refers to the mean number of individuals recorded in the reporting period (excluding the WRA)
V Indicates the species is recorded outside regular surveys.
Table C2. Summary of herpetofauna monitoring in the WRA
|
Common Name |
Scientific Name |
Conservation Status(1) |
Mean (2) |
|||||
|
Amphibians |
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
Gunther’s Frog |
Hylarana guentheri |
- |
2.5 |
0.5 |
1.5 |
0.5 |
V |
|
|
|
|
No. of Species Recorded |
1 |
1 |
1 |
1 |
1 |
0 |
|
Reptiles |
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
(No records during the survey period) |
- |
- |
0 |
0 |
0 |
0 |
0 |
0 |
|
|
|
No. of Species Recorded |
0 |
0 |
0 |
0 |
0 |
0 |
(1) Conservation status follows that of Fellowes et al. (2002), Chan et al. (2005) and Karsen et al. (1998).
(2) Refers to the mean number of individuals recorded in the reporting period (excluding the WRA)
V indicates the species is recorded outside regular surveys.
Table C3. Summary of mammal monitoring in the Survey Area (excluding the WRA)
|
Common Name |
Scientific Name |
Conservation Status(1) |
Max (2) |
|||||
|
|
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
No records during the survey period |
- |
- |
0 |
0 |
0 |
0 |
0 |
0 |
|
|
|
No. of Species Recorded |
0 |
0 |
0 |
0 |
0 |
0 |
(1) Conservation status follows that of Fellowes et al. (2002) and Shek (2006).
(2) Refers to the maximum number of individuals recorded in each month in the survey area (excluding WRA).
Table C4. Summary of mammal monitoring in the WRA
|
Common Name |
Scientific Name |
Conservation Status(1) |
Max(2) |
|||||
|
|
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
Bat |
indet. sp.1 |
- |
|
|
V |
V |
V |
V |
|
|
|
No. of Species Recorded |
0 |
0 |
1 |
1 |
1 |
1 |
(1) Conservation status follows that of Fellowes et al. (2002) and Shek (2006).
(2) Refers to the maximum number of individuals recorded in each month in the survey area
V indicates the species is recorded outside regular surveys
Table C5. Summary of dragonfly and butterfly monitoring in the Survey Area (excluding the WRA)
|
Common Name |
Scientific Name |
Conservation Status(1) |
Mean (2) |
|||||
|
Odonate |
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
Asian Amberwing |
Brachythemis contaminata |
- |
|
2.5 |
3.0 |
|
|
|
|
Green Skimmer |
Orthetrum sabina sabina |
- |
|
2.5 |
0.5 |
|
|
|
|
Saddlebag Glider |
Tramea virginia |
- |
|
1.0 |
|
|
|
|
|
Variegated Flutterer |
Rhyothemis variegata arria |
- |
11.0 |
4.5 |
1.5 |
2.0 |
|
|
|
Wandering Glider |
Pantala flavescens |
- |
|
1.0 |
5.0 |
7.5 |
|
|
|
|
|
No. of Species Recorded |
1 |
5 |
4 |
2 |
0 |
0 |
|
Butterfly |
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
Indian Cabbage White |
Pieris canidia canidia |
- |
|
|
2.5 |
|
|
|
|
|
|
No. of Species Recorded |
0 |
0 |
1 |
0 |
|
|
(1) Conservation status follows that of Fellowes et al. (2002), Lo & Hui (2004), Wilson (2004) and Young & Yiu (2002).
(2) Refers to the mean number of individuals recorded in each month in the survey area (excluding the WRA)
Table C6. Summary of dragonfly and butterfly monitoring in the WRA
|
Common Name |
Scientific Name |
Conservation Status(1) |
Mean (2) |
|||||
|
Odonate |
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
Asian Amberwing |
Brachythemis contaminata |
- |
|
1.0 |
6.0 |
|
|
|
|
Blue Dasher |
Brachydiplax chalybea flavovittata |
- |
|
1.0 |
0.5 |
|
1.0 |
|
|
Common Bluetail |
Ischnura senegalensis |
- |
0.5 |
|
|
|
|
|
|
Common Flangetail |
Ictinogomphus pertinax |
- |
|
2.5 |
|
4.5 |
|
|
|
Crimson Dropwing |
Trithemis aurora |
- |
|
|
|
1.0 |
|
|
|
Dancing Dropwing |
Trithemis pallidinervis |
- |
1.0 |
|
|
|
|
|
|
Evening Skimmer |
Tholymis tillarga |
- |
|
|
2.0 |
|
|
|
|
Golden Flangetail |
Sinictinogomphus clavatus |
- |
|
1.5 |
|
|
|
|
|
Green Skimmer |
Orthetrum sabina sabina |
- |
|
0.5 |
3.0 |
2.5 |
2.0 |
|
|
Lesser Emperor |
Anax parthenope julius |
- |
|
|
|
|
|
1.0 |
|
Pied Percher |
Neurothemis tullia tullia |
- |
|
0.5 |
1.0 |
0.5 |
1.0 |
|
|
Saddlebag Glider |
Tramea virginia |
- |
|
4.5 |
0.5 |
|
|
|
|
Variegated Flutterer |
Rhyothemis variegata arria |
- |
22.5 |
12.0 |
18.0 |
6.0 |
2.0 |
|
|
Wandering Glider |
Pantala flavescens |
- |
0.5 |
|
1.0 |
0.5 |
|
22.0 |
|
|
|
No. of Species Recorded |
4 |
8 |
8 |
6 |
4 |
2 |
|
Butterfly |
|
|
May |
Jun |
Jul |
Aug |
Sep |
Oct |
|
Common Mormon |
Papilio polytes polytes |
|
|
|
|
|
|
1.0 |
|
Common Grass Yellow |
Eurema hecabe hecabe |
- |
|
2.0 |
|
|
|
|
|
Common Palmfly |
Elymnias hypermnestra hainana |
|
|
|
0.5 |
|
|
|
|
Common Sailer |
Neptis hylas |
- |
|
|
|
|
1.0 |
1.0 |
|
Great Egg-fly |
Hypolimnas bolina |
- |
|
|
|
|
|
1.0 |
|
Indian Cabbage White |
Pieris canidia |
- |
0.5 |
|
0.5 |
|
|
|
|
Lemon Emigrant |
Catopsilia pomona pomona |
|
|
|
0.5 |
|
|
|
|
|
|
No. of Species Recorded |
1 |
1 |
3 |
0 |
2 |
3 |
(1) Conservation status follows that of Fellowes et al. (2002), Lo & Hui (2004), Wilson (2004) and Young & Yiu (2002).
(2) Refers
to the mean number of individuals recorded in each month in the survey area
(excluding the WRA)
Table D1. Water quality at WRA
May 2015
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turbidity (mg/L) |
DO (mg/L) |
Water Level (cm) |
|
1 |
26.3 |
8.03 |
0.71 |
14.4 |
3.4 |
130 |
|
2 |
26.2 |
7.99 |
0.91 |
14.8 |
3.6 |
110 |
|
3 |
26.2 |
8.00 |
0.73 |
15.5 |
3.8 |
150 |
|
4 |
26.2 |
7.99 |
0.93 |
15.2 |
3.7 |
120 |
|
Action Level |
- |
<6.5 or >8.0 |
>2 |
- |
<2 |
<150 or >250 |
|
Limit Level |
- |
<6.0 or >8.5 |
>5 |
- |
<1 |
- |
June 2015
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turbidity (mg/L) |
DO (mg/L) |
Water Level (cm) |
|
1 |
30.6 |
7.42 |
0.63 |
7.2 |
5.8 |
160 |
|
2 |
30.6 |
7.40 |
0.77 |
8.6 |
4.8 |
160 |
|
3 |
30.9 |
7.50 |
0.60 |
10.6 |
7.2 |
180 |
|
4 |
31.0 |
7.51 |
0.60 |
10.7 |
6.7 |
170 |
|
Action Level |
- |
<6.5 or >8.0 |
>2 |
- |
<2 |
<150 or >250 |
|
Limit Level |
- |
<6.0 or >8.5 |
>5 |
- |
<1 |
- |
July 2015
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turbidity (mg/L) |
DO (mg/L) |
Water Level (cm) |
|
1 |
27.1 |
7.68 |
0.60 |
13.5 |
5.9 |
160 |
|
2 |
27.3 |
7.44 |
0.66 |
13.4 |
5.0 |
150 |
|
3 |
27.3 |
7.50 |
0.54 |
6.9 |
6.9 |
180 |
|
4 |
27.2 |
7.52 |
0.63 |
5.0 |
5.1 |
170 |
|
Action Level |
- |
<6.5 or >8.0 |
>2 |
- |
<2 |
<150 or >250 |
|
Limit Level |
- |
<6.0 or >8.5 |
>5 |
- |
<1 |
- |
August 2015
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turbidity (mg/L) |
DO (mg/L) |
Water Level (cm) |
|
1 |
28.2 |
7.37 |
0.34 |
8.2 |
6.0 |
170 |
|
2 |
28.4 |
7.13 |
0.33 |
7.2 |
5.2 |
150 |
|
3 |
28.4 |
7.19 |
0.27 |
5.9 |
6.6 |
180 |
|
4 |
28.3 |
7.21 |
0.31 |
4.7 |
5.3 |
180 |
|
Action Level |
- |
<6.5 or >8.0 |
>2 |
- |
<2 |
<150 or >250 |
|
Limit Level |
- |
<6.0 or >8.5 |
>5 |
- |
<1 |
- |
September 2015
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turbidity (mg/L) |
DO (mg/L) |
Water Level (cm) |
|
1 |
27.9 |
7.46 |
0.34 |
5.6 |
5.3 |
170 |
|
2 |
28.1 |
7.22 |
0.33 |
5.4 |
4.5 |
160 |
|
3 |
28.1 |
7.28 |
0.27 |
5.8 |
5.9 |
190 |
|
4 |
28.0 |
7.30 |
0.31 |
5.1 |
4.6 |
190 |
|
Action Level |
- |
<6.5 or >8.0 |
>2 |
- |
<2 |
<150 or >250 |
|
Limit Level |
- |
<6.0 or >8.5 |
>5 |
- |
<1 |
- |
October 2015
|
Cell No. |
Temp. (°C) |
pH |
Salinity (ppt) |
Turbidity (mg/L) |
DO (mg/L) |
Water Level (cm) |
|
1 |
27.2 |
7.52 |
0.54 |
6.7 |
5.2 |
180 |
|
2 |
27.4 |
7.25 |
0.43 |
6.5 |
4.3 |
170 |
|
3 |
27.4 |
7.28 |
0.47 |
6.9 |
5.6 |
210 |
|
4 |
27.3 |
7.30 |
0.51 |
7.8 |
4.4 |
170 |
|
Action Level |
- |
<6.5 or >8.0 |
>2 |
- |
<2 |
<150 or >250 |
|
Limit Level |
- |
<6.0 or >8.5 |
>5 |
- |
<1 |
- |
Notes: Values Bold indicate Action Level exceedance.
Values Underlined and Bold indicate Limit Level exceedance.