wetlands
a publication of Sungei Buloh Wetland Reserve

Vol 14 No 1

Water Regime Management

Bird Ringing 2006

Shorebird counts (2000-2006)
 
Shorebird Counts (2000-2006)
at Sungei Buloh Wetland Reserve


By James Gan
Senior Conservation Officer
Main article | Peak High Tide Counts part 1, part 2 |
Comparison of selected species | Day Peak Counts


Summary


Shorebirds from the Scolopacidae and Charadriidae were counted regularly in Sungei Buloh Wetland Reserve between January 2000 and December 2006. A total of 23 species was recorded during the census sessions. Total shorebird numbers peaked in October, November or December for all years. The most abundant bird was the Pacific Golden Plover Pluvialis fulva with counts consistently exceeding 1,000 for all years since 2001 with a maximum of 2,000.

The counts have revealed information on the composition of shorebird species, their numbers and their presence in different months over the past seven years. More specifically, the relative importance of Sungei Buloh as a shorebird site in Singapore is reinforced. Data collected will help to improve the conservation work and management practices at Sungei Buloh for the next few years.

Introduction

This article is based on an earlier paper submitted by the same authors and published in The Stilt No.48 Oct 2005. It is an update of the shorebird count data obtained from monthly wader census conducted at SBWR with a brief analysis. It is also the intention of this update to prime people to take a greater interest and appreciation in the shorebirds of Singapore.

Results

A total of 23 species was recorded during the census sessions. Seven of the 23 species dominated with counts of at least 100 birds at any one session during the study period. Count data for these seven species for the period January 2000 to December 2006 are listed in Table 1. Note that the totals as given in the tables refer to the highest count for a given month and are not average counts.

For all years, maximum shorebird counts were in either November or December with the exception of 2006 when it peaked in October. Peak counts of shorebirds did not exceed 3,200 birds in any year. Only the Pacific Golden Plover had counts exceeding 1,000 birds. This occurred fairly regularly during both the periods for southward and northward migration. The only other shorebird with numbers exceeding a thousand was the Mongolian Plover Charadrius mongolus (1,003 on January 2000). Common Redshank Tringa totanus and Whimbrel Numenius phaeopus were the only two species noted in the boreal summer for 2001 to 2006 where they were present in very low numbers (below 20 birds) except in June 2003 when no shorebirds were observed.

To generalise, the species with the highest numbers recorded during the southward migration (Sep/Oct/Nov) relative to their numbers throughout the year were Common Redshank, Mongolian Plover and Curlew Sandpiper. Species with the highest numbers recorded during the northward migration (Mar/Apr) were Pacific Golden Plover and Whimbrel. Species with the highest numbers in the northern mid winter (Dec/Jan) were Common Greenshank and Marsh Sandpiper.

Species Account

A comparison was made of the seven most common shorebird species at the reserve with the maximum counts recorded by the Asian Waterfowl Census (AWC) for Singapore between 1991 and 2001 (Perennou & Mundkur 1991, 1992; Mundkur & Taylor 1993; Lopez & Mundkur 1997; Li & Mundkur 2004). Direct comparison is possible for counts taken in January since the AWC counts are consistently conducted in that month at low tide. The percentage of each species of shorebird that can be found in the reserve against the Singapore population is at best a rough estimate but still an indicator of the relative importance of the reserve with respect to other sites in Singapore. The relevant data are given in Table 2.

Common Greenshank
Tringa nebularia

Trend:
Increased numbers during both southward and northward migration The maximum count at the wetland was 364 recorded in Nov 2005. It seems likely that during high tide about half the population of Greenshanks in Singapore use the wetland as a roost.

Common Redshank
Tringa totanus

Trend:
Increased numbers during both southward and northward migration The maximum count was 683 recorded in Sep 2000. The peaks in September followed by a 60% to 70% drop the following month in 2000, 2001 and 2002 provide some indication of turnover rates for Redshanks on passage.

Curlew Sandpiper
Calidris ferruginea

Trend:
Erratic numbers during the southward migration. Avoidance of the wetland during the northward migration since the spring of 2001 The maximum count was 519 in Oct 2006. The 1991-2001 counts for Singapore range from 5 to 781. First migrants were recorded in August. Since 2001, negligible (less than 10) numbers of birds were present between January and July. The data and observation could be explained by the possibility that since 2001, Curlew Sandpipers take a northward migration route that bypass or use other wetlands in Singapore or the region. Such an alternative route could possibly be along the eastern coast of Sumatra before crossing over to Malaysia and/or Thailand. Large numbers of Curlew Sandpiper occur along the east coast of Sumatra at this time (A. Crossland pers. comm.). Wader counts at suitable sites in Indonesia and the Malay Peninsula would help to clarify the actual route taken. The peak counts in October for most years indicate a strong southward passage in that month before falling sharply in January for the northward migration.

Marsh Sandpiper
Tringa stagnatilis

Trend:
Stable numbers during both southward and northward migration. The maximum count was 486 observed in Dec 2001. Counts for Singapore range from 526 and 1294. Birds arrive at the wetland in appreciable numbers only from October. The data collected are consistent with the observations in the Malay Peninsula where Marsh Sandpipers arrive late and depart relatively early with a further peak in the boreal spring (Wells 1999). This surge was noted in early April 2001 but not in 2000. It may however have happened between count dates and was therefore unrecorded.

Mongolian Plover
Charadrius mongolus

Trend:
Steady recovery in numbers during the southward migration after a dramatic and steep decrease observed in 2002 and 2003; Avoidance of the wetland during the northward migration since the spring of 2003. The maximum count of 1,003 was recorded on 26 January 2000. Another count of 878 was recorded on 10 February 2000. AWC counts for Singapore have recorded historic peaks of up to 1,000 birds. Observations in the Malay Peninsula have generally noted decreases in Mongolian Plover numbers from December to March (Wells 1999). These observations are consistent with the pattern of counts recorded for all years when counts are generally highest in December and decrease as the northward migration progresses. This may indicate a boreal spring exodus without significant augmentation by passage migrants. High tide counts taken from a boat in the West Johore Straits on 3 Jan 03 revealed up to 600 Mongolian Plovers resting on floating pontoons. The following year, on 6 Feb 04, 200 Mongolian Plovers were counted at the same pontoons during high tide. Thus it would seem, unlike the Curlew Sandpiper, that the main northward migration route of Mongolian Plovers continues to include the vicinity of Sungei Buloh. Further monitoring and implementation of various habitat management measures at Sungei Buloh may help to reveal the reasons for the general avoidance of the wetland in favour of the pontoons during the northward migration period.

Pacific Golden Plover
Pluvialis fulva

Trend:
General increase in numbers during both the periods of southward and northward migration. Counts exceeded 1,000 birds in all years except 2000. A mid-winter peak count of 2000 was recorded in Jan 2005 and this number is unusual as Jan counts for Pacific Golden Plovers in previous years had never exceeded 1,000 birds. It could however indicate some disturbance at the Mandai Mudflats where records of Pacific Golden Plovers exceeding 2,000 birds at low tide have been recorded. The southward migration in the same year confirmed this number with a peak of 1,735 birds counted in Nov 2005. The following year also saw an unusually high surge of Pacific Golden Plovers in Jan 2006 with a count of 1,321 birds. AWC counts for Singapore range from 908 to 2416. There appears to be a trend that more Pacific Golden Plovers are making use of Sungei Buloh. The reasons are not clear but could be due to the loss of previously derelict land in the Kranji area that had been used by the plovers as a high tide roost area and which was in 2005 and 2006 being redeveloped resulting in the plovers moving to Sungei Buloh as the next best high tide roost. The count of 1,081 birds in April 2001 suggests staging during northward migration.

Whimbrel
Numenius phaeopus
Trend:
Increased numbers during both southward and northward migration A maximum count of 442 was obtained. That count was taken in Nov 2003 and likely involves birds passing through and making use of Sungei Buloh as a stop over site. Significant increases in Whimbrels from the preceding months in April 2001 (219 birds), Mar 2002 (215 birds), Mar 2004 (301 birds), Apr 2005 (320 birds) and Apr 2006 (268 birds) might indicate staging. The high counts of Whimbrels in Mar and April quickly slumps to generally 20 birds or less in early May. Some Whimbrels may have over summered in Singapore as small numbers were present throughout May, June and July in most years. First arrivals were noted in late July or early August and a large influx of birds was noted in September for most years.

DISCUSSION


This study of shorebird count data from the years 2000 to 2006 has shown that generally, for counts between September and March (Table 3), over 1,000 shorebirds may be expected at SBWR during the high tide period. From May to July, only a few species of shorebirds can be found, usually Common Redshank and Whimbrel with fewer than 30 individuals. From the census data for the seven years period, the shorebird community at the reserve is composed of seven main species and sixteen other species that occur in much smaller numbers. These in descending order of abundance are Common Sandpiper Tringa hypoleucos, Terek Sandpiper Tringa cinerea, Broadbilled Sandpiper Limicola falcinellus, Ruddy Turnstone Arenaria interpres, Bar-tailed Godwit Limosa lapponica, Little Ringed Plover Charadrius dubius, Great Knot Calidris tenuirostris, Pintail Snipe Gallinago sterura, Eurasian Curlew Numenius arquata, Grey-tailed Tattler Tringa brevipes, Grey Plover Pluvialis squatarola, Red-necked Stint Calidris ruficollis, and Black-tailed Godwit Limosa limosa, Little Curlew Numenius minutes, Greater Sand Plover Charadrius leschenaultii and Asian Dowitcher Limnodromus semipalmatus. Other shorebird species, for example Black-winged Stilt Himantopus himantopus observed at the reserve in 2005 (Tay 2006) were not recorded during the actual census sessions.

Preliminary data obtained through the counts and observations suggest that the wetland is favoured by perhaps more than 80% of the Singapore population of Whimbrel, Mongolian Plover (except during the northward migration period when they completely avoid the wetland) and Pacific Golden Plover. The data also suggest that about 50% of the Common Greenshank and 30% of the Marsh Sandpiper and Common Redshank population use the wetland as a high tide roost. About 10% of the Curlew Sandpiper population is thought to use Sungei Buloh as a high tide roost. Further studies would be required to confirm these hypotheses. More frequent counts over a longer period would help to establish patterns of seasonal abundance, distribution and movements of shorebirds in Singapore. A limitation of the data obtained during the study period is that a substantial influx of passage waders might last only a few days and might be missed through slipping between counts that are spaced at wider intervals. Closer-spaced counts during migration periods would refine our knowledge of the exact magnitude and timing of passage peaks. The data presented, though limited by resource constraints, is however sufficient to give an indicative picture of the seasonal abundance of shorebirds at Sungei Buloh. It is clear that the Sungei Buloh wetland area is an important site for these shorebirds. Similar sites in Singapore and around Singapore may possibly reveal similar species, similar monthly counts and composition of species.

Acknowledgements

The counts were possible through the assistance of the Conservation Officers and Rangers at Sungei Buloh Wetland Reserve. In particular we would like to register our appreciation to Abdul Khalid Hamid, Mustaffa Hajar, Charles Lim Sim Moh, Patricia Phua Lee Kheng, Lim Yew Soon, Jack Wong and the late Ong Hai Chwee for logistical assistance.

References

Gan, J. and Ramakrishnan, R.K. 2002. Shorebird Monitoring in Sungei Buloh Wetland Reserve in 2001, Wetlands Vol 9, No. 1, Pp13. Publication of SBWR, National Parks Board, Singapore

Gan, J. and Ramakrishnan, R.K. 2005. Notes on shorebird numbers in Sungei Buloh Wetland Reserve in 2000 and 2001. The Stilt 48:38-41

Li, Z.W.D. and Mundkur, T. 2004. Numbers and distribution of waterbirds and wetlands in the Asia- Pacific region. Results of the Asian Waterbird Census: 1997-2001. Wetlands International, Kuala Lumpur, Malaysia.

Li, Z.W.D. et. al. 2007. Numbers and distribution of waterbirds and wetlands in the Asia-Pacific region. Results of the Asian Waterbird Census: 2002-2004. Wetlands International, Kuala Lumpur, Malaysia.

Lopez, A., and Mundkur, T., (Eds). 1997. The Asian Waterfowl Census 1994-1996. Wetlands International. Kuala Lumpur

Mundkur, T., and Taylor, V., 1993. Asian Waterfowl Census 1993, Asian Wetland Bureau & The International Waterfowl and Wetlands Research Bureau

Perennou, C., and Mundkur, T., 1991. Asian Waterfowl Census 1991, Asian Wetland Bureau & The International Waterfowl and Wetlands Research Bureau

Perennou, C., and Mundkur, T., 1992. Asian and Australasian Waterfowl Census 1992, Asian Wetland Bureau & The International Waterfowl and Wetlands Research Bureau

Tay S. L., 2006. The Day a Super St__ flew into Bulohwood, Wetlands Vol 10:7, Pp15. Publication of SBWR, National Parks Board, Singapore

Wells, D.R. 1999. The Birds of the Thai-Malay Peninsula, Vol 1. Academic Press, San Diego
   
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