Annex C
List of Floral and Faunal Species recorded within the Study Area
Annex C |
Table 1 Representative
Rare Plant Species (131 out of 151 Species) Recorded on Lamma Island (Extracted
From Wong 1999)
Species |
Family |
Form |
|
Rarity |
Species |
Family |
Form |
|
Rarity |
Actinidia latifolia |
Actinidiaceae |
Liana |
|
vr |
Glycosmis parvifolia |
Rutaceae |
Shrub |
|
vr |
Alangium chinense |
Alangiaceae |
Tree |
|
vr |
Meliosma rigida |
Sabiaceae |
Tree |
|
vr |
Crinum asiaticum |
Amaryllidaceae |
Herb |
|
vr |
Kadsura heteroclita |
Schisandraceae |
Liana |
|
vr |
Ilex memecylifolia |
Aquifoliaceae |
Shrub |
|
vr |
Picrasma quassioides |
Simaroubaceae |
Tree |
|
vr |
Ilex viridis |
Aquifoliaceae |
Shrub |
|
vr |
Turpinia montana |
Staphyleaceae |
Tree |
|
vr |
Ilex kwangtungensis |
Aquifoliaceae |
Tree |
|
vr |
Camellia hongkongensis |
Theaceae |
Tree |
|
vr |
Ilex ficoidea |
Aquifoliaceae |
Tree |
|
vr |
Ternstroemia luteoflora |
Theaceae |
Tree |
|
vr |
Ilex rotunda |
Aquifoliaceae |
Tree |
|
vr |
Tutcheria spectabilis |
Theaceae |
Tree |
|
vr |
Arisaema penicillatum |
Araceae |
Herb |
|
vr |
Tutcheria microcarpa |
Theaceae |
Tree |
|
vr |
Arisaema erubescens |
Araceae |
Herb |
|
vr |
Grewia biloba |
Tiliaceae |
Shrub |
|
vr |
Asparagus lucidus |
Asparagaceae |
Vine |
|
vr |
Celtis biondii |
Ulmaceae |
Tree |
|
vr |
Balanophora harlandii |
Balanophoraceae |
Para |
|
vr |
Acanthus ilicifolius |
Acanlhaceae |
Shrub |
|
r |
Ehretia longiflora |
Boraginaceae |
Tree |
|
vr |
Artabotrys hongkongensis |
Annonaceae |
Liana |
|
r |
Cordia dichotoma |
Boraginaceae |
Tree |
|
vr |
Tectaria subtriphylla |
Aspidiaceae |
Herb |
|
r |
Buxus harlandii |
Buxaceae |
Shrub |
|
vr |
Impatiens chinensis |
Balsaminaceae |
Herb |
|
r |
Buxus sinica |
Buxaceae |
Shrub |
|
vr |
Viburnum odoratissimum |
Caprifoliaceae |
Tree |
|
r |
Caesalpinia bonduc |
Caesalpiniaceae |
Liana |
|
vr |
Microtropis latifolia |
Celastraceae |
Shrub |
|
r |
Capparis acutifolia |
Capparaceae |
Liana |
|
vr |
Euonymus laxiflorus |
Celastraceae |
Shrub |
|
r |
Lonicera macrantha |
Caprifoliaceae |
Liana |
|
vr |
Sarcandra glabra |
Chloranthaceae |
Shrub |
|
r |
Loeseneriella concinna |
Celastraceae |
Liana |
|
vr |
Aster panduratus |
Compositae |
Herb |
|
r |
Euonymus hederaceus |
Celastraceae |
Liana |
|
vr |
Tridax procumbens |
Compositae |
Herb |
|
r |
Euonymus longifolius |
Celastraceae |
Shrub |
|
vr |
Gahnia tristis |
Cyperaceae |
Herb |
|
r |
Gerbera piloselloides |
Compositae |
Herb |
|
vr |
Diospyros eriantha |
Ebenaceae |
Tree |
|
r |
Vernonia saligna |
Compositae |
Herb |
|
vr |
Alchornea trewioides |
Euphorbiaceae |
Shrub |
|
r |
Vernonia solanifolia |
Compositae |
Liana |
|
vr |
Antidesma japonicum |
Euphorbiaceae |
Tree |
|
r |
Aspidistra minutiflora |
Convallariaceae |
Herb |
|
vr |
Mallotus apelta |
Euphorbiaceae |
Tree |
|
r |
Merremia quinata |
Convolvulaceae |
Vine |
|
vr |
Bridelia insulana |
Euphorbiaceae |
Tree |
|
r |
Itea chinensis |
Escalloniaceae |
Tree |
|
vr |
Bischofia javanica |
Euphorbiaceae |
Tree |
|
r |
Euphorbia tirucalli |
Euphorbiaceae |
Shrub |
|
vr |
Pseudopogonatherum contortum |
Gramineae |
Herb |
|
r |
Antidesma paniculatum |
Euphorbiaceae |
Tree |
|
vr |
Stauntonia obovata |
Lardizabalaceae |
Liana |
|
r |
Mallotus hookerianus |
Euphorbiaceae |
Tree |
|
vr |
Stauntonia chinensis |
Lardizabalaceae |
Liana |
|
r |
Drypetes formosana |
Euphorbiaceae |
Tree |
|
vr |
Litsea monopetala |
Lauraceae |
Tree |
|
r |
Cyclobalanopsis myrsinifolia |
Fagaceae |
Tree |
|
vr |
Lindera communis |
Lauraceae |
Tree |
|
r |
Casearia glomerata |
Flacourtiaceae |
Tree |
|
vr |
Neolitsea pulchella |
Lauraceae |
Tree |
|
r |
Calophyllum membranaceum |
Guttiferae |
Shrub |
|
vr |
Bowringia callicarpa |
Leguminosae |
Liana |
|
r |
Altingia chinensis |
Hamamelidaceae |
Tree |
|
vr |
Indigofera hirsuta |
Leguminosae |
Shrub |
|
r |
Engelhardtia roxburgiana |
Juglandaceae |
Tree |
|
vr |
Ormosia emarginata |
Leguminosae |
Tree |
|
r |
Persea chinensis |
Lauraceae |
Tree |
|
vr |
Lycopodium cernuum |
Lycopodiaceae |
Herb |
|
r |
Litsea verticillata |
Lauraceae |
Tree |
|
vr |
Tinospora sinensis |
Menispermaceae |
Liana |
|
r |
Beilschmiedia fordii |
Lauraceae |
Tree |
|
vr |
Maclura cochinchinensis |
Moraceae |
Shrub |
|
r |
Cinnamomum parthenoxylon |
Lauraceae |
Tree |
|
vr |
Ficus virens |
Moraceae |
Tree |
|
r |
Albizia corniculata |
Leguminosae |
Liana |
|
vr |
Embelia vestita |
Myrsinaceae |
Liana |
|
r |
Abrus precatorius |
Leguminosae |
Liana |
|
vr |
Maesa perlarius |
Myrsinaceae |
Shrub |
|
r |
Millettia pulchra |
Leguminosae |
Shrub |
|
vr |
Myrsine seguinii |
Myrsinaceae |
Tree |
|
r |
Ormosia semicastrata |
Leguminosae |
Tree |
|
vr |
Ludwigia adscendens |
Onagraceae |
Herb |
|
r |
Gleditsia fera |
Leguminosae |
Tree |
|
vr |
Ludwigia octovalvis |
Onagraceae |
Herb |
|
r |
Thespesia populnea |
Malvaceae |
Tree |
|
vr |
Eulophia flava |
Orchidaceae |
Herb |
|
r |
Ficus sarmentosa |
Moraceae |
Liana |
|
vr |
Pentaphylax euryoides |
Pentaphylacacea |
Tree |
|
r |
Ficus pyriformis |
Moraceae |
Shrub |
|
vr |
Pittosporum tobira |
Pittosporaceae |
Shrub |
|
r |
Maclura tricuspidata |
Moraceae |
Shrub |
|
vr |
Podocarpus neriifolia |
Podocarpaceae |
Tree |
|
r |
Ardisia lindleyana |
Myrsinaceae |
Shrub |
|
vr |
Clematis uncinata |
Ranunculaceae |
Liana |
|
r |
Baeckea frutescens |
Myrtaceae |
Shrub |
|
vr |
Morinda villosa |
Rubiaceae |
Liana |
|
r |
Acmena acuminatissima |
Myrtaceae |
Tree |
|
vr |
Antirhoea chinensis |
Rubiaceae |
Shrub |
|
r |
Pholidota chinensis |
Orchidaceae |
Herb |
|
vr |
Adina pilulifera |
Rubiaceae |
Tree |
|
r |
Cymbidium ensifolium |
Orchidaceae |
Herb |
|
vr |
Toddalia asiatica |
Rutaceae |
Liana |
|
r |
Carallia brachiata |
Rhizophoraceae |
Tree |
|
vr |
Striga lutea |
Scrophulariacea |
Para |
|
r |
Rosa laveigata |
Rosaceae |
Liana |
|
vr |
Lepidagathis incurva |
Scrophulariaceae |
Herb |
|
r |
Prunus phaeosticta |
Rosaceae |
Tree |
|
vr |
Pterospermum heterophyllum |
Sterculiaceae |
Tree |
|
r |
Eriobotrya fragrans |
Rosaceae |
Tree |
|
vr |
Symplocos lucida |
Symplocaceae |
Tree |
|
r |
Ophiorrhiza pumila |
Rubiaceae |
Herb |
|
vr |
Camellia caudata |
Theaceae |
Tree |
|
r |
Mussaenda erosa |
Rubiaceae |
Liana |
|
vr |
Callicarpa kochiana |
Verbenaceae |
Shrub |
|
r |
Ixora chinensis |
Rubiaceae |
Shrub |
|
vr |
Clerodendrum fortunatum |
Verbenaceae |
Shrub |
|
r |
Lasianthus trichophlebus |
Rubiaceae |
Shrub |
|
vr |
Gmelina chinensis |
Verbenaceae |
Tree |
|
r |
Tarenna brevicymigera |
Rubiaceae |
Shrub |
|
vr |
Callicarpa nudiflora |
Verbenaceae |
Tree |
|
r |
Randia canthioides |
Rubiaceae |
Tree |
|
vr |
Vitis balanseana |
Vitaceae |
Liana |
|
r |
Tarenna mollissima |
Rubiaceae |
Tree |
|
vr |
|
|
|
|
|
Rarity
: r = rare; vr = very rare.
Table
2 Bird
Species Previously Recorded in Lamma (from literature review)
Group |
Species |
Number of
individuals |
Year of Record |
Principal Status |
Habitats |
Remarks |
Reference |
Category with
Respect to Wind Turbine |
Fregatidae |
Frigate Bird (Fregata sp.) |
1 |
1975 (Nov) |
unclassifed |
Foraging: open water |
|
HKBWS 1976 |
Secondary Species The species is a vagrant |
|
Lesser Frigate Bird (Fregata ariel) |
1 |
1990 (Jun) |
OV |
Foraging: open water |
Seen flying over Hung Shing Ye Wan |
HKBWS 1991 |
Secondary Species The species is a vagrant |
Ardeidae |
Pacific Reef Egret (Egretta sacra) |
1-13 |
1972, 1993, 1994, 1995, 1996, 1997, 1998 |
R |
Foraging: Rocky coastline Breeding: Rocky coastline |
The highest count was 13 at Sok Kwu Wan in
1994 |
HKBWS 1973, 1992, 1994, 1995, 1998, 1999,
2002 |
Primary Species Ciconiiformes herons & storks are considered
to be sensitive. Despite this
the species utilizes coastal areas and is unlikely to fly over the study
area. |
|
Purple Heron (Ardea purpurea) |
1 |
1975 (Oct) |
AM, P |
Foraging: wetland Breeding: reedbed |
Seen flying over the West Lamma Channel |
HKBWS 1976 |
Primary Species Ciconiiformes herons & storks are considered to be
sensitive. Despite this the
species uses reedbed and wetland and is unlikely to fly over the study area. |
|
Striated Heron (Butorides striatus) |
1 |
2004 (Apr) |
SV |
Foraging: wetland, stream |
Seen foraging in a stream near Sok Kwu Wan |
So, unpublished
data |
Primary Species Ciconiiformes herons & storks are considered
to be sensitive. Despite this
the species utilizes wetland and stream and is unlikely to fly over the study
area |
|
Little Egret (Egretta garzetta) |
Up to 6 |
1996-2004 |
P |
Foraging: wetland and coastal area Breeding: woodland edge |
Seen next to piers of both Yung Shue Wan
and Sok Kwu Wan |
So, unpublished
data |
Primary Species Ciconiiformes herons & storks are considered
to be sensitive. Despite this
the species utilizes wetland and coastal area and is unlikely to fly over the
study area. |
|
Black-crowned Night Heron (Nycticorax nycticorax) |
Up to 3 |
1996-2004 |
P |
Foraging: wetland and coastal area Breeding: woodland edge |
Seen next to piers of both Yung Shue Wan
and Sok Kwu Wan |
So, unpublished
data |
Primary Species Ciconiiformes herons & storks are considered
to be sensitive. Despite this
the species utilizes coastal area and is unlikely to fly over the study area. |
|
Chinese Pond Heron (Ardeola bacchus) |
Not specified |
Not specified |
P |
Foraging: wetland Breeding: woodland edge |
|
Maunsell 2003 |
Primary Species Ciconiiformes herons & storks are considered
to be sensitive. Despite this
the species utilizes wetland and is unlikely to fly over the study area. |
|
Cattle Egret (Bubulcus ibis) |
Not specified |
Not specified |
P |
Foraging: grassland and marshy area Breeding: woodland edge |
|
Maunsell
2003 |
Primary Species Ciconiiformes herons & storks are considered
to be sensitive. Despite this
the species utilizes wetland and is unlikely to fly over the study area. |
|
Grey Heron (Ardea cinerea) |
Not specified |
Not specified |
WV |
Foraging: wetland |
|
Maunsell
2003 |
Primary Species Ciconiiformes herons & storks are considered to be
sensitive. Despite this the
species utilizes wetland and is unlikely to fly over the study area. |
|
Yellow Bittern (Ixobrychus sinensis) |
1 |
1999 |
PM, SV |
Recorded in stream habitat |
|
Maunsell 2003 |
Primary Species Ciconiiformes herons & storks are considered
to be sensitive. Despite this
the species utilizes wetland and stream and is unlikely to fly over the study
area. |
Rallidae |
White-breasted Waterhen (Amaurornis phoenicurus) |
Up to 2 |
2004 (Apr) |
R |
Foraging: wetland Breeding: wetland |
Seen in marshy area of Pak Kok and during
this study |
So,
unpublished data |
Secondary Species The species utilizes wetland and usually
will not fly high, and is unlikely to fly over the study area. |
|
Water Cock (Gallicrex cinerea) |
Not specified |
Not specified |
PM |
Foraging: marshy area |
|
Maunsell 2003 |
Secondary Species The species utilizes wetland and is
unlikely to fly over the study area. |
Accipitridae |
Black Kite (Milvus lineatus) |
Up to 20 |
1998-1999, 2001-2002 |
WV, R |
Foraging: open area Breeding: woodland edge |
|
Walk 2001-2002; Maunsell 2003 |
Primary Species The species is the most frequently
encountered bird in the study and utilizes the study area as foraging site. |
|
Common Buzzard (Buteo buteo) |
Not specified |
1990 |
WV |
Foraging: wetland, stream |
|
HKBWS 1991 |
Primary Species The species utilizes open area and the
study area is a possible foraging site. |
|
Bonelli’s Eagle (Hieraetus fasciatus) |
1 |
1972 (Sep) |
R |
Foraging: open area Breeding: Mountainous area |
|
HKBWS 1973 |
Primary Species The species utilizes open area and the
study area is a possible foraging site. |
|
White-bellied Sea Eagle (Haliaeetus leucogaster) |
Up to 4 |
1975, 2001, 2002 |
R |
Foraging: open water Breeding: coastline |
Seen in the West Lamma Channel, and Ngai
Tau |
HKBWS 1976, Walk 2001-2002 |
Primary Species The ordinary flight line may cross the
study area |
|
Crested Goshawk (Accipiter trivirgatus) |
Not specified |
Not specified |
R |
Foraging:
woodland and woodland edge Breeding:
woodland |
|
Maunsell 2003 |
Primary Species The species
utilizes open area and the study area is a possible foraging site. |
|
Chinese Goshawk (Accipiter soloensis) |
Not specified |
Not specified |
SM |
Foraging:
woodland and woodland edge |
|
Maunsell 2003 |
Primary Species The species
utilizes open area and the study area is a possible foraging site. |
Falconidae |
Kestrel (Falco tinnunculus) |
Up to 2 |
1990 (Jan) |
AM, WV |
Foraging: open area |
|
HKBWS 1991 |
Primary Species The species utilizes open area and the
study area is a possible foraging site. |
Charadriidae |
Pacific Golden Plover (Pluvialis fulva) |
1 |
1996 (Apr) |
M, WV |
Foraging: mudflat and wetland |
Seen in East Lamma Channel |
HKBWS 1998 |
Primary Species Charadriiformes
waders are considered to be particularly, or potentially, sensitive to wind
farm. Despite the species
utilizes wetlands and is unlikely to fly over the study area, this species is
still classified as primary species. |
Scolopacidae |
Ruddy Turnstone (Arenaria interpres) |
2 |
1996 (Apr) |
M |
Foraging: mudflat and wetland |
Seen in East Lamma Channel |
HKBWS 1998 |
Secondary Species The species utilizes wetlands and is
unlikely to fly over the study area. |
|
Common Sandpiper (Actitis hypoleucos) |
Not specified |
Not specified |
M, WV |
Foraging: wetland and coastal area |
|
Maunsell 2003 |
Secondary Species The species utilizes wetlands and is
unlikely to fly over the study area. |
|
Little Stint (Calidris minuta) |
Not specified |
Not specified |
M |
Foraging: wetland and marshy area |
|
Maunsell 2003 |
Secondary Species The species utilizes wetlands and is
unlikely to fly over the study area. |
|
Red-necked Phalarope (Phalaropus lobatus) |
Not specified |
Not specified |
M |
Foraging: open water |
|
Maunsell 2003 |
Secondary Species The species utilizes wetlands and is
unlikely to fly over the study area. |
|
Eurasian Woodcock (Scolopax rusticola) |
Not specified |
Not specified |
WV |
Foraging: woodland, woodland edge and
along stream |
|
Maunsell 2003 |
Secondary Species The species is a ground-dweller and is
unlikely to fly over the study area. |
|
Curlew Sandpiper (Calidris ferruginea) |
Not specified |
Not specified |
SM |
Foraging: wetland |
|
Maunsell 2003 |
Secondary Species The species utilizes wetlands and is unlikely
to fly over the study area. |
Laridae |
Black-tailed Gull (Larus crassirostris) |
4 |
1975 (Dec) |
WV, M |
Foraging: open water |
Seen in the West Lamma Channel |
HKBWS 1976 |
Secondary Species The species utilizes open water and is
unlikely to fly over the study area. |
|
Black-headed Gull (Larus ridibundus) |
6500 |
1975 (Jan) |
WV |
Foraging: open water |
Seen roosting along the West Lamma Channel |
HKBWS 1976 |
Secondary Species The species utilizes open water and is
unlikely to fly over the study area. |
|
Whiskered Tern (Chlidonias hybridus) |
Up to 20 |
1983 (Aug), 1996 (Apr) |
M |
Foraging: open water Breeding: rocky island |
Seen in water south of Lamma |
HKBWS 1985, HKBWS 1998 |
Secondary Species The species utilizes open water and is
unlikely to fly over the study area. |
|
White-winged Tern (Chlidonias leucopterus) |
50-80 |
1975 (Sep), 1981 |
M |
Foraging: open water Breeding: rocky island |
Seen in West Lamma Channel |
HKBWS 1976, Carey et al. 2001 |
Secondary Species The species utilizes open water and is
unlikely to fly over the study area. |
|
Black-napped Tern (Sterna sumatrana) |
1 |
1993 (Aug) |
SV |
Foraging: open water Breeding: rocky island |
|
HKBWS 1994 |
Primary Species Sternidae terns are considered to be sensitive. The species utilizes open water and
is unlikely to fly over the study area. |
|
Common Tern (Sterna hirundo) |
Up to 130 |
1972 (Aug), 1983 (Sep), 1996 (Apr) |
M |
Foraging: open water Breeding: rocky island |
Seen in water south of Lamma and West
Lamma Channel |
HKBWS 1973, HKBWS 1985, HKBWS 1993, HKBWS 1995, HKBWS 1998 Carey et al. 2001 |
Primary Species Sternidae terns are considered to be sensitive. The species utilizes open water and
is unlikely to fly over the study area. |
|
Roseate Tern (Sterna dougallii) |
16 |
1978 |
SV |
Foraging: open water Breeding: rocky island |
Seen in East Lamma Channel |
Carey et al. 2001 |
Primary Species Sternidae terns are considered to be sensitive. The species utilizes open water and
is unlikely to fly over the study area. |
|
Aleutian Tern (Sterna aleutica) |
1-9 |
1993 (Aug), 1996 (Apr) |
AM |
Foraging: open water Breeding: rocky island |
Seen in East Lamma Channel |
HKBWS 1994, HKBWS 1998 |
Primary Species Sternidae terns are considered to be sensitive. The species utilizes open water and
is unlikely to fly over the study area. |
|
Gull-billed Tern (Gelochelidon nilotica) |
Up to 7 |
1980 (Apr), 1992 (Sep) |
M |
Foraging: open water |
Seen in West Lamma Channel |
HKBWS 1982, HKBWS 1993 |
Secondary Species The species utilizes open water and is
unlikely to fly over the study area. |
|
Long-tailed Jaeger (Stercorarius longicaudus) |
2 |
1996 (Apr) |
SM |
Foraging: open water |
Seen in West Lamma Channel |
HKBWS 1998 |
Secondary Species The species utilizes open water and is
unlikely to fly over the study area. |
Columbidae |
Emerald Dove (Chalcophaps indica) |
Not specified |
1990 (Nov), 2004 |
R |
Foraging: woodland Breeding: woodland |
This species is also recorded in this
study |
HKBWS 1991 |
Primary Species The species utilizes woodland and is
recorded in the study area. |
|
Spotted Dove (Streptopelia chinensis) |
8 |
1998-1999 |
R |
Foraging: open area, woodland edge Breeding: woodland edge |
|
Maunsell 2003 |
Primary Species The species utilizes habitats similar to
those in the study area and may fly over them |
|
Rock Dove (Columba livia) |
Not specified |
Not specified |
R |
Foraging: open area near human settlement |
|
Maunsell 2003 |
Secondary Species There is only limited human settlement
around the study area |
Cuculidae |
Common Koel (Eudynamys scolopacea) |
Not specified |
1998 (Nov-Dec) |
SV, R |
Foraging: woodland Breeding: woodland |
|
HKBWS 2002 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Chestnut-winged Cuckoo (Clamator coromandus) |
1 |
2004 |
SV |
Foraging: woodland Breeding: woodland |
Observer per. obs. |
|
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Black-winged Cuckoo (Coracina melaschistos) |
3 |
1998 |
WV |
Foraging: woodland Breeding: woodland |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Indian Cuckoo (Cuculus micropterus) |
Not specified |
Not specified |
SV |
Foraging: woodland Breeding: woodland |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Greater Coucal (Centropus sinensis) |
2 |
1998-1999 |
R |
Foraging: woodland edge and shrubland Breeding: woodland and shrubland |
|
Maunsell 2003 |
Primary Sepcies The species utilizes habitat types
provided by the study area. |
|
Lesser Coucal (Centropus bengalensis) |
Not specified |
Not specified |
R |
Foraging: woodland edge and shrubland Breeding: woodland and shrubland |
|
Maunsell 2003 |
Primary Sepcies The species utilizes habitat types
provided by the study area. |
Alcedinidae |
Common Kingfisher (Alcedo atthis) |
Not specified |
1972 |
AM, P |
Foraging: Rocky coastline, wetland Breeding: edge of pond or stream |
|
HKBWS 1973 |
Secondary Species The study area does not contain suitable
habitat for the species. |
|
White-throated Kingfisher (Halcyon symrnensis) |
Up to 4 |
1998-1998 |
AM, P |
Foraging: wetland and woodland edge Breeding: rocky area |
|
Maunsell 2003 |
Primary Species The proposed site for the wind turbine is
a possible foraging site and breeding site for the species. |
|
Pied Kingfisher (Ceryle rudis) |
Not specified |
Not specified |
R |
Foraging: wetland Breeding: edge of pond or stream |
|
Maunsell 2003 |
Secondary Species The study area does not contain suitable
habitat for the species. |
|
Hoopoe (Upupa epops) |
Not specified |
Not specified |
OV |
Favours lawns and open grassland |
Upupidae are unique ground-feeding birds |
Maunsell 2003 |
Secondary Species This species is ground-feeding bird with
curious flapping flight. |
Coracidae |
Dollarbird (Eurystomus orientalis) |
1 |
1991 (Oct) |
M |
Foraging: woodland and open area |
|
HKBWS 1992 |
Primary Species The species utilizes open area and may fly
over the study area. |
Apodidae |
Pacific Swift (Apus pacificus) |
Up to 11 |
1992 (Jul), 1995 (Jul) 1999 (Mar) |
SM, SV |
Foraging: in the air |
|
HKBWS 1993, HKBWS 1996, Maunsell 2003 |
Primary Species The species is an aerial-forager and may
fly over the study area. |
|
Little Swift (Apus
affinis) |
Not specified |
Not specified |
R, SM |
Foraging: in the air Breeding: cliff and roof of building |
|
Maunsell 2003 |
Primary Species The species is an aerial-forager and may
fly over the study area. |
Hirundinidae |
Barn Swallow (Hirundo rustica) |
Up to 7 |
1999 |
SV, SM |
Foraging: in the air Breeding: building |
|
Maunsell 2003 |
Primary Species The species is an aerial-forager and may
fly over the study area. |
Passeridae |
Tree Sparrow (Passer montanus) |
37 |
1998-1999 |
R |
Recorded in shrubland/grassland |
This species is familiar of urban areas |
Maunsell 2003 |
Secondary Species Ths species is low-flying bird. |
Motacillidae |
Yellow Wagtail (Motacilla flava) |
Not specified |
Not specified |
M, WV |
Foraging: wetland |
|
Maunsell 2003 |
Secondary Species The study area does not contain suitable
habitat for the species. |
|
White Wagtail
(Motacilla alba) |
6 |
1998 (Sept & Dec) |
WV |
Foraging: wetland |
This species
is recorded in coastlines (including rocky shore and mudflat exposed in low
tide) |
Maunsell 2003 |
Secondary Species The study area does not contain suitable
habitat for the species. |
|
Grey Wagtail (Motacilla cinerea) |
1 |
1999 (Mar) |
WV |
Foraging: wetland |
This species
is recorded in coastlines (including rocky shore and mudflat exposed in low
tide) |
Maunsell 2003 |
Secondary Species The study area does not contain suitable
habitat for the species. |
Campephagidae |
Black-winged Cuckoo-shrike (Coracina melaschistos) |
1 |
1998 (Sep) |
AM, WV |
Foraging: woodland |
Seen at Sok Kwu Wan |
HKBWS 2002 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
Laniidae |
Brown Shrike (Lanius cristatus) |
1 |
1990 (Oct), 1991 (Oct) |
SM |
Foraging: woodland edge, open area |
|
HKBWS 1991, HKBWS 1992 |
Primary Species The study area has suitable foraging area
for the species and it may fly over the study area. |
|
Long-tailed Shrike (Lanius schach) |
1 |
1998 |
R |
Foraging: open area Breeding: shrubland |
|
Maunsell 2003 |
Primary Species The study area has suitable foraging area
for the species and it may fly over the study area. |
Pycnonotidae |
Red-whiskered Bulbul (Pycnonotus jocosus) |
Up to 25 |
2004 |
R |
Foraging: wide range of habitats Breeding: wide range of habitats |
|
Maunsell 2003 |
Primary Species The species utilizes habitats similar to
the study area and may fly over the study area. |
|
Chinese Bulbul (Pycnonotus sinensis) |
Up to 17 |
2004 |
R |
Foraging: wide range of habitats Breeding: wide range of habitats |
|
Maunsell 2003 |
Primary Species The species utilizes habitats similar to
the study area and may fly over the study area. |
|
Sooty-headed Bulbul (Pycnonotus aurigaster) |
Not specified |
Not specified |
R |
Foraging: woodland edge and shrubland Breeding: shrubland |
|
Maunsell 2003 |
Primary Species The species utilizes habitats similar to
the study area and may fly over the study area. |
Turdidae |
Grey Bushchat (Saxicola ferrea) |
Not specified |
Not specified |
AM, WV |
Foraging: woodland and shrubland |
|
Maunsell 2003 |
Primary Species The species utilizes habitats similar to
the study area and may fly over the study area. |
|
Siberian Rubythroat (Luscinia calliope) |
Not specified |
Not specified |
WV |
Foraging: woodland edge and shrubland |
|
Maunsell 2003 |
Primary Species The species utilizes habitats similar to
the study area and may fly over the study area. |
|
Blue Rock Thrush (Monticola solitarius) |
Up to 3 |
1975 (Sep), 1991 (Apr) |
WV, M |
Foraging: rocky area |
|
HKBWS 1976, HKBWS 1992 |
Primary Species The study area has suitable foraging area
for the species and it may fly over the study area. |
|
Scaly Thrush (Zoothera dauma) |
Not specified |
1990 (Jan) |
WV |
Foraging: woodland |
|
HKBWS 1991 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Grey-backed Thrush (Turdus hortulorum) |
12 |
1998 (Dec) |
WV |
Foraging: woodland |
Seen at Pak Kok |
HKBWS 2002 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Pale Thrush (Turdus pallidus) |
5 |
1998 (Dec) |
WV, M |
Foraging: woodland |
Seen at Pak Kok |
HKBWS 2002 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Blue Whistling Thrush (Myiophoneus caeruleus) |
Not specified |
Not specified |
R |
Foraging: woodland and along stream Breeding: woodland and along stream |
|
Maunsell 2003 |
Secondary Species The study area does not have suitable
habitat for this species. |
|
Daurian Redstart (Phoenicurus auroreus) |
Not specified |
Not specified |
WV |
Foraging: woodland, woodland edge and
shrubland |
|
Maunsell 2003 |
Primary Species The species utilizes habitats similar to
the study area and may fly over the study area. |
|
Oriental Magpie Robin (Copsychus saularis) |
Up to 6 |
1998-1999 |
R |
Foraging: woodland and woodland edge Breeding: woodland and woodland edge |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and woodland
edge and is unlikely to fly over the study area. |
Muscicapidae |
Verditer Flycatcher (Eumyias thalassina) |
1 |
1990 (Nov) |
WV |
Foraging: woodland |
Male |
HKBWS 1991 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Grey-streaked
Flycatcher (Muscicapa griseisticta) |
Not specified |
Not specified |
PM |
Foraging: woodland |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Red-throated Flycatcher (Ficedula albicilla) |
1 |
1974 (Feb), 1991 |
AM, WV |
Foraging: Woodland |
|
HKBWS 1975, HKBWS 1992 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Black-naped Monarch (Hypothymis azurea) |
1 |
1995 |
WV, M |
Foraging: woodland |
|
HKBWS 1996 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
Paridae |
Great Tit (Parus major) |
1 |
1998 (Dec) |
R |
Foraging: woodland and woodland edge Breeding: woodland and woodland edge |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
Timaliidae |
White-browed Laughing Thrush (Garrulax sannio) |
Not specified |
1990 (Sep) |
R |
Foraging: woodland and shrubland Breeding: woodland and woodland edge |
|
HKBWS 1991 |
Secondary Species The species forages at the undergrowth and
it unlikely to fly over the area. |
|
Masked Laughing Thrush (Garrulax perspillatus) |
Not specified |
Not specified |
R |
Foraging: woodland and shrubland Breeding: woodland and woodland edge |
|
Maunsell 2003 |
Secondary Species The species moves around in the
undergrowth and is unlikely to fly over the study area. |
|
Hwamei (Garrulax canorus) |
1 |
1999 |
R |
Foraging: shrubland and woodland edge Breeding: shrubland and woodland edge |
|
Maunsell 2003 |
Secondary Species The species moves around in the
undergrowth and is unlikely to fly over the study area. |
Sylviidae |
Lanceolated Warbler (Locustella lanceolata) |
1 |
1990 (Nov) |
AM |
Foraging: wetland |
Found dead at Yung Shue Long Tsuen |
HKBWS 1991 |
Secondary Species The species utilizes wetland and is
unlikely to fly over the study area. |
|
Plain Prinia (Prinia inornata) |
12 |
1991 (Dec) |
R |
Foraging: shrubland Breeding: shrubland |
|
HKBWS 1992 |
Secondary Species The species moves around by flying short
distance and low about ground, and is unlikely to fly over the study area. |
|
Yellow-bellied
Prinia (Prinia flaviventris) |
Not specified |
Not specified |
R |
Foraging: shrubland Breeding: shrubland |
|
Maunsell 2003 |
Secondary Species The species moves around by flying short
distance and low about ground, and is unlikely to fly over the study area. |
|
Artic Warbler (Phylloscopus borealoides) |
Up to 6 |
1998 (Sep) |
AM |
Foraging:
woodland and woodland edge |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Yellow-browed
Warbler (Phylloscopus inornatus) |
Up to 4 |
1998 (Dec), 1999 (Mar) |
WV |
Foraging:
woodland and woodland edge |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Pallas’s Leaf Warbler (Phylloscopus proregulus) |
Not specified |
1998 |
WV |
Foraging: woodland |
|
HKBWS 2002 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Pale-legged Leaf Warbler (Phylloscopus tenellipes) |
1 |
1998 (Dec) |
AM |
Foraging: woodland |
Seen at Pak Kok |
HKBWS 2002 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Dusky Warbler (Phylloscopus fuscatus) |
1 |
1998 (Dec) |
WV |
Foraging: woodland and woodland edge |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
|
Common Tailorbird (Orthotomus sutorius) |
4 |
1998 |
R |
Foraging: woodland and shrubland Breeding: woodland and shrubland |
|
Maunsell 2003 |
Secondary Species The species is not a strong flyer and is
unlikely to fly over the study area. |
Emberizidae |
Crested Bunting (Melophus lathami) |
1 |
1975, 1980 (May), 1992 (Dec) |
R |
Foraging: paddy field and grassland Breeding: rocky area |
|
HKBWS 1976, HKBWS 1982, HKBWS 1993 |
Secondary Species Although there had been records of this species
found on Lamma Island, it is rare and the surveys did not record it in the
study area. |
|
Black-faced Bunting (Emberiza spodocephala) |
Not specified |
1996 |
M, WV |
Foraging: open area and shrubland |
Observer per. obs. |
|
Secondary Species Although the species utilizes habitat
similar to the study area, it usually forages close to the ground. |
|
Little Bunting (Emberiza pusilla) |
Not specified |
1996 |
WV |
Foraging: open area |
Observer per. obs. |
|
Secondary Species Although the species utilizes habitat
similar to the study area, it usually forages close to the ground. |
Nectariniidae |
Fork-tailed Sunbird (Aethopyga christinae) |
1 |
1995 (Jan) |
R |
Foraging: woodland Breeding: woodland |
Heard |
HKBWS 1996 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
Zosteropidae |
Japanese White-eye (Zosterops japonica) |
8 |
1998 |
R, W |
Foraging: woodland and woodland edge Breeding: woodland |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
Estrildidae |
Scaly-breasted Munia (Lonchura punctulata) |
2 |
1998 |
R |
Foraging: woodland edge and open area |
|
Maunsell 2003 |
Secondary Species This species usually forages along lower
growth of vegetation or on the ground. |
Sturnidae |
Black-collared Starling (Sturnus nigricollis) |
28 |
1998-1999 |
R |
Foraging: woodland edge and open area |
|
Maunsell 2003 |
Primary Species The study area has suitable habitats for
the species and it may fly over the study area. |
|
Crested Myna (Acridotheres cristatellus) |
33 |
1998-1999 |
R |
Foraging: shrubland and woodland edge |
|
Maunsell 2003 |
Primary Species The study area has suitable habitats for
the species and it may fly over the study area. |
|
Hill Myna (Gracula religiosa) |
Not specified |
Not specified |
I |
Foraging: woodland and woodland edge |
|
Maunsell 2003 |
Secondary Species The species utilizes woodland and is
unlikely to fly over the study area. |
Dicruridae |
Black Drongo (Dicrurus macrocercus) |
1 |
1994 |
M, SV |
Foraging: woodland edge and open area |
|
HKBWS 2002 |
Primary Species The study area has suitable habitats for
the species and it may fly over the study area. |
Corvidae |
Common Magpie (Pica pica) |
4 |
1998-1999 |
R |
Foraging: open area and woodland edge |
|
Maunsell 2003 |
Primary Species The species utilizes habitats similar to
the study area and may fly over the study area. |
|
Large-billed Crow (Corvus macrorhynchus) |
Not specified |
Not specified |
R |
Foraging: open area |
|
Maunsell 2003 |
Primary Species The species utilizes habitats similar to
the study area and may fly over the study area. |
Principle
Status: OV=Occasional Visitor
P=Present all year, SM=Spring Migrant, AM=Autumn Migrant, M=Migrant,
SV=Summer Visitor, WV=Winter Visitor, R=Resident and I=Introduced.
The Principle
Status of the birds follow Carey et al (2001).
Table 3 Butterfly
Species Recorded Previously in Lamma Island (From Literature Review)
Common Name |
Species Name |
Abundance |
Angled Castor |
Ariadne ariadne |
C |
Baron |
Euthalia
phemius |
UC |
Birdwing |
Troides helena |
UC |
Blue Glassy Tiger |
Ideopsis
similes |
VC |
Blue Pansy |
Junonia orithya |
UC |
Blue Spotted Crow |
Euploea midamus |
VC |
Chinese Peacock |
Papilio bianor |
C |
Common Black Jezebel |
Delias pasithoe |
C |
Common Faun |
Faunis eumeus |
C |
Common Grass Yellow |
Eurema hecabe |
VC |
Common Lascar |
Pantoporia
hordonia |
C |
Common Mormon |
Papilio polytes |
VC |
Common White |
Artogeia
canidia |
VC |
Common White-banded Brown |
Lethe confusa |
C |
Cornelian |
Deudorix
epijarbas |
R |
Dark Brand Bush Brown |
Mycalesis
mineus |
VC |
Dark Veined Tiger |
Danaus genutia |
VC |
Fivebar Swordtail |
Graphium
antiphates |
C |
Golden Birdwing |
Troides aeacus |
R |
Grass Demon |
Udaspes folus |
R |
Great Eggfly |
Hypolimnas
bolina |
C |
Great Orange Tip |
Hebomoia
glaucippe |
C |
Grey Pansy |
Junonia atlites |
C |
Hong Kong Cupid |
Everes
lacturnus |
C |
Hong Kong Fritillary |
Argyreus
hyperbius |
VC |
Hong Kong Lacewing |
Cethosia biblis |
UC |
Lemon Pansy |
Junonia lemonias |
UC |
Long-banded Silverline |
Spindasis
lohita |
UC |
Orange Awlet |
Bibasis
oedipodea |
R |
Painted Lady |
Vanessa cardui |
R |
Paris Peacock |
Papilio paris |
VC |
Punchinello |
Zemeros flegyas |
C |
Red Admiral |
Vanessa indica |
UC |
Red Helen |
Papilio helenus |
VC |
Short-banded Sailor |
Phaedyma
columella |
C |
Small White |
Artogeia rapae |
R |
Striped Blue Crow |
Euploea
mulciber |
UC |
Swallowtail |
Papilio xuthus |
UC |
Tailed Green Jay |
Graphium
agamemnon |
VC |
Yellow Orange Tip |
Ixias pyrene |
UC |
Abundance (Walthew
1997) : C = common, VC = very common, UN = uncommon, R = rare Information
Extracted from Maunsell 2003.
Table 4 Category (Primary or Secondary) of the Bird Species Recorded within Lamma Island (Records from the Literature)
Family |
Category |
Criteria |
Fregatidae |
Secondary Species |
The Frigate Birds are oceanic birds which are also long-distant migrants. There were 2 published records of Frigate Birds from Lamma, including one identified Fregata ariel flying over Hung Shing Yeh Wan (HKBWS 1976, 1991). Despite this the species is now classified as ‘Occasional Visitor’ to Hong Kong, the species is not regularly reported in Hong Kong waters. Therefore it is classified as secondary species in the study. |
Ardeidae |
Primary Species |
The group includes the egrets, herons and bitterns. There are previous records of the group with a majority of records on Pacific Reef Egret (HKBWS 1973, 1992, 1994, 1995, 1998, 1999 and 2002). Purple Heron has also been recorded in the close vicinity of Lamma, which single bird was seen flying over the West Lamma Channel (HKBWS 1976). Although not formally published, Black-crowned Night Heron, Little Egret and Striated Heron were recorded in the study site (So, unpublished data). Chinese Pond Heron, Cattle Egret, Grey Heron and Yellow Bittern are also recorded by Maunsell (2003). Ciconiiformes herons & storks terns are considered to be particularly, or potentially, sensitive to wind farm. Despite the species utilizes habitat irrelevant to the Study Area and is unlikely to fly over the study area, this species is still classified as primary species. |
Rallidae |
Secondary Species |
Up to two individuals of the White-breasted Waterhen (Amaurornis phoenicurus) was recorded in 2004, in Pak Kok (so, unpublished data). The species was also recorded in this study. The rare Hong Kong passage migrant Water Cock was also recorded. As these species utilizes wetland and usually will not fly high, and are unlikely to fly over the study area, therefore they are classified as secondary species. |
Accipitridae |
Primary Species |
Six species were previous reported, which are Black-eared Kite, Common Buzzard, Crested Goshawk, Chinese Goshawk, Bonelli’s Eagle and White-bellied Sea Eagle (HKBWS 1973, 1976 and 1991, Maunsell 2003). The residential bird White-bellied Sea Eagle was also recorded flying below 100m above the study area and the Black Kite is also recorded in this study. Accipitridae raptors are considered to be particularly, or potentially, sensitive to wind farm, and therefore they are all classified as primary species. |
Falconidae |
Primary Species |
Up to two individuals were seen on Lamma Island (HKBWS 1991). As the species utilizes open area and the study area is a possible foraging habitat, it is classified as primary species. |
Charadriidae |
Primary Species |
A single record of one Pacific Golden Plover being seen in East Lamma Channel (HKBWS 1998). Charadriiformes waders are considered to be particularly, or potentially, sensitive to wind farm. Despite the species utilizes wetlands and is unlikely to fly over the study area, this species is still classified as primary species. |
Scolopacidae |
Secondary Species |
A Ruddy Turnstone was seen in the East Lamma Channel (HKBWS 1998). The species utilizes wetlands and is unlikely to fly over the study area, therefore it is classified as secondary species. Other members from this family include the Common Sandpiper, Little Stint, Red-necked Phalarope, Curlew Sandpiper and Eurasian Woodcock. As the study area does not contain suitable habitat for these species, they are all classified as secondary species. |
Laridae |
Primary/ Secondary Species |
This group includes gulls, terns and Jaeger. A total of 9 species were recorded in West and East Lamma Channels, and water south of Lamma Island. They are the Black-tailed Gull, Black-headed Gull, Whiskered Tern, White-winged Tern, Common Tern, Roseate Tern, Aleutian Tern, Gull-billed Tern and Long-tailed Jaeger (HKBWS 1973, 1976, 1985, 1992, 1993, 1994, 1995, 1998, Carey et al. 2001). There was also one record of Black-napped Tern from Lamma Island with unspecified location (HKBWS 1994). Sternidae terns are considered to be particularly, or potentially, sensitive to wind farm. Despite those species utilize open water and are unlikely to fly over the study area, those species are still classified as primary species. As the remaining species recorded in this group utilize open water and are unlikely to fly over the study area, they are all classified as secondary species. |
Columbidae |
Primary/ Secondary Species |
There was record of Emerald Dove from Lamma Island (HKBWS 1991), which was also recorded in this study. The species utilizes woodland and had been recorded in the study area during this study, and therefore may fly over the study area. It is classified as primary species. Another species Spotted Dove had been recorded in Lamma Island (Maunsell 2003). This species utilizes habitats similar to those in the study area and may fly over them, it is classified as primary species. Rock Dove utilizes open area near human settlement. As there is only limited human settlement around the study area, it is classified as secondary species. |
Alcedinidae |
Primary/ Secondary Species |
Four species from this group had been recorded on Lamma Island,
including Common Kingfisher, the White-throated Kingfisher, the Pied Kingfisher
and Hoopoe (HKBWS 1973 and 2002, Maunsell 2003). The White-throated Kingfisher utilizes habitat similar to
the study area, and is also recorded in this study in the close vicinity of
the proposed site of the construction of wind turbine. Therefore it is classified as primary
species. The study area does not
contain suitable habitat for the Common Kingfisher and the Pied Kingfisher,
and therefore they are classified as secondary species. Hoopoe is a ground
feeding bird on open lawn and grassland and is therefore classified as
secondary species. |
Coracidae |
Primary Species |
Dollarbirdr was recorded previous (HKBWS 1992). As the species also utilizes similar habitats as those in the study area, and therefore it is also classified as primary species. |
Cuculidae |
Primary/ Secondary Species |
This group consists of koel, cuckoos and coucals. The Common Koel (Eudynays scolopacea) was recorded on Lamma Island (HKBWS 2002), and was also recorded in this study. The Chestnut-winged Cuckoo (Clamator coromandus) was recorded in Sok Kwu Bay in 2004 (So, unpublished data). Indian Cuckoo was recorded in this study with up to 2 individuals and the Black-winged Cuckoo was also recorded. As all of these species utilize woodland habitat and are unlikely to fly over the study area, they are classified as secondary species. Greater Coucal and Lesser Coucal were recorded in this study. They utilize shrubland and woodland edge which also provided by the study area. The possibilities of these species flying over the study area lead to their primary species status. |
Apodidae |
Primary Species |
Pacific Swift was recorded previously on Lamma Island (HKBWS 1992 and 1996), and was also recorded in this study. Little Swift was also recorded in this study. As both species are aerial-forager and may fly over the study area, they are classified as primary species. |
Hirundinidae |
Primary Species |
Barn Swallow was recorded in this study. As the species is aerial-forager and may fly over the study area, it is classified as primary species. |
Passeridae |
Secondary Species |
Tree Sparrow was recorded previously near Sok Kwu Wan (Maunsell 2003). Although the study area has suitable foraging habitat for this species, it is not a strong flyer and is unlikely to fly over the study area and is classified as secondary species. |
Motacillidae |
Secondary Species |
This group contains the wagtails. Yellow Wagtail, White Wagtail and Grey Wagtail were recorded on the island (Maunsell 2003). As the study area does not contain suitable habitat for the species, it is therefore classified as secondary species. |
Campephagidae |
Secondary Species |
Black-winged Cuckoo-shrike had been recorded at Sok Kwu Wan in 1998 (HKBWS 2002). The species utilizes woodland and is unlikely to fly over the study area, therefore it is classified as secondary species. |
Laniidae |
Primary Species |
Brown Shrike was recorded in the study area in 1990 and 1991 (HKBWS 1991 and 1992). Long-tailed Shrike was recorded in this study. The study area has suitable foraging area for both species and they may fly over the study area, therefore they are classified as primary species. |
Pycnonotidae |
Primary Species |
Three
species from the group were recorded in this study, which are Red-whiskered
Bulbul, Chinese Bulbul and Sooty-headed Bulbul. As these species utilize
habitats similar to the study area and may fly over the proposed site for
wind turbine, they are classified as primary species. |
Turdidae |
Primary/ Secondary Species |
This
group includes bushchat, rubythroat, robins, redstart and thrushes. Blue Rock Thrush was recorded on
Lamma Island with up to three individuals seen (HKBWS 1976 and 1992). The species forages in rocky area and
the study area has suitable foraging area for the species, and it may fly
over the study area. Therefore
it is classified as primary species.
Grey Bushchat, Siberian Rubythroat and Daurian Redstart were recorded
previously on Lamma (Maunsell 2003).
As they utilize habitats similar to the study area and may fly over
the proposed wind turbine, they are classified as primary species. Other thrushes such as Scaly Thrush,
Grey-backed Thrush, Pale Thrush and Blue Whistling Thrush were also recorded
on the island (HKBWS 1991, 2002, Maunsell 2003). In addition the Oriental Magpie Robin was also recorded in
this study. As these species
utilize woodland and is unlikely to fly over the study area, therefore they
are classified as secondary species. |
Muscicapidae |
Secondary Species |
This
group includes the flycathers and monarch. There were records of Verditer Flycatcher, Red-throated
Flycatcher, Black-naped Monarch and Grey-streaked Flycatcher on Lamma Island
(HKBWS 1975, 1991, 1992, 1996 and Maunsell 2003). Those species utilize woodland and are unlikely to fly
over the study area, and therefore are classified as secondary species. |
Paridae |
Secondary Species |
Great
Tit was recorded in the Sok Kwu Wan (Maunsell 2003). As the species utilizes woodland and
is unlikely to fly over the study area, it is classified as secondary
species. |
Timaliidae |
Secondary Species |
White-browed
Laughing was recorded on Lamma Island (HKBWS 1991). In addition, Masked Laughing Thrush and Hwamei were
recorded in this study. As these
species forage at the undergrowth and it unlikely to fly over the area,
therefore they are classified as secondary species. |
Sylviidae |
Secondary Species |
Lanceolated
Warbler, a rare autumn migrant, had been record on Lamma Island in 1990
(HKBWS 1991). Up to 12 Plain
Prinia were recorded on the Island (HKBWS 1992) and it was recorded in this
study. Although this species utilizes
habitats similar to the study area, it usually moves around by flying short
distance and low about ground, and is unlikely to fly over the study
area. It is therefore classified
as secondary species. Pallas’s
Leaf Warbler and Pale-legged Leaf Warbler were also recorded (HKBWS
2002). In addition, Common
Tailorbird was recorded in this study.
Artic Warbler, Yellow-bellied Prinia, Yellow-browed Warbler and Dusky
Warbler were all reported in Sok Kwu Wan (Maunsell 2003). As these species forage in woodland
area and are unlikely to fly over the study are, therefore they are all
classified as secondary species. |
Emberizidae |
Secondary Species |
Both
Black-faced Bunting and Little Bunting had been recorded in 1996 (So,
unpublished data). Although the
species utilizes habitat similar to the study area, it usually forages close
to the ground and are classified as secondary species. There were previous records of
Crested Bunting on the island which utilized habitats similar to the study
area (HKBWS 1976, 1981 and 1993).
However, the Crested Bunting has now become very rare due to the
disappearance of paddy field in Hong Kong, and therefore it is classified as
secondary species. |
Nectariniidae |
Secondary Species |
There
was a single record of Fork-tailed Sunbird in 1995 (HKBWS 1996). The species utilizes woodland and is
unlikely to fly over the study area.
It is classified as secondary species. |
Zosteropidae |
Secondary Species |
The
Japanese White-eye was recorded in this study. However, as the species utilizes woodland and is unlikely
to fly over the study area, it is therefore classified as secondary species. |
Estrildidae |
Secondary Species |
Scaly-breasted
Munia was recorded previously (Maunsell 2003). As this species usually forage
in the lower growth of vegetation, they are classified as secondary species. |
Sturnidae |
Primary/ Secondary Species |
The
introduced Hill Myna was recorded previously on the island (Maunsell
2003). As the species utilizes
woodland and is unlikely to fly over the study area, it is classified as
secondary species.
Black-collared Starling and Crested Myna were also recorded in
Lamma. These species utilize
open area and woodland edge. The study area has suitable habitats for the
species and they may fly over the proposed site for the wind turbine and
therefore they are classified as primary species. |
Dicruridae |
Primary Species |
Black
Drongo had been recorded in 1994 (HKBWS 2002) as well as in this study. As the study area has suitable
habitats for the species and it may fly over the proposed wind turbine, it is
therefore classified as primary species. |
Corvidae |
Primary Species |
Common Magpie and Large-billed Crow were recorded in this study. As both species may fly over the study area when foraging, therefore they are classified as primary species. |
Table 5 Plant
Species Recorded Within the Study Area
|
|
|
|
Local Abundance |
|||||
Species |
Growth Form |
Origin |
Status |
Secondary Woodland |
Shrubland |
Shrubby Grassland |
Village/Developed Area |
Stream |
Project Area |
Acacia confusa |
T |
E |
VC |
A |
O |
|
|
F |
|
Ageratum conyzoides |
H |
N |
VC |
|
A |
|
|
|
|
Albizia lebbeck |
T |
N |
C |
F |
|
|
|
F |
|
Alocasia macrorrhiza |
H |
N |
VC |
O |
|
|
F |
|
|
Annona squamosa |
S |
E |
C |
F |
|
|
|
|
|
Antidesma bunius |
S |
N |
C |
|
O |
|
|
|
|
Aporusa dioica |
S |
N |
VC |
F |
F |
O |
|
F |
|
Aquilaria sinensis |
T |
N |
C |
F |
|
|
|
O |
|
Archidendron lucidum |
S |
N |
VC |
|
F |
|
|
F |
|
Artocarpus heterophyllus |
T |
E |
C |
|
|
|
F |
|
|
Asparagus cochinchinensis |
H |
N |
C |
O |
|
|
|
|
|
Averrhoa carambola |
S |
N |
C |
|
|
|
F |
|
|
Bambusa spp. |
T |
N |
C |
O |
|
|
|
S |
|
Breynia fruticosa |
S |
N |
VC |
|
F |
O |
|
F |
|
Bridelia tomentosa |
S |
N |
VC |
F |
F |
|
F |
|
F |
Callicarpa cathayana |
S |
N |
C |
F |
|
|
|
|
|
Carex chinensis |
G |
N |
C |
|
O |
|
|
F |
|
Cassytha filiformis |
C |
N |
VC |
|
F |
F |
|
|
F |
Casuarina equisetifolia |
T |
E |
VC |
O |
|
|
|
|
|
Celtis sinensis |
T |
N |
C |
|
O |
|
|
O |
|
Centella asiatica |
H |
N |
VC |
|
O |
|
|
|
|
Cerbera manghas |
T |
E |
C |
S |
|
|
|
|
|
Chrysanthemum indicum |
S |
N |
C |
|
O |
|
|
|
O |
Cinnamomum camphora |
T |
N |
C |
F |
|
|
O |
|
|
Cinnamomum parthenoxylon |
T |
N |
C |
O |
|
|
|
|
|
Citrus sinensis |
S |
E |
C |
|
|
|
F |
|
|
Clausena lansium |
S |
N |
VC |
O |
|
|
F |
|
|
Clerodendrum fortunatum |
S |
N |
VC |
O |
O |
|
|
|
O |
Clerodendrum inerme |
S |
N |
C |
O |
|
|
|
|
|
Cocculus orbiculatus |
C |
N |
C |
O |
F |
|
|
|
|
Cratoxylumcochinchinensis |
S |
N |
VC |
O |
F |
|
|
F |
|
Cyperus rotundus |
G |
N |
VC |
|
O |
F |
|
F |
|
Dalbergia benthami |
C |
N |
C |
F |
F |
|
|
F |
|
Dalbergia millettii |
C |
N |
VC |
F |
F |
|
|
F |
|
Daphniphyllum calycinum |
T |
N |
C |
|
O |
|
|
|
|
Dianella ensifolia |
H |
N |
VC |
|
F |
O |
|
|
|
Dicranopteris linearis |
F |
N |
VC |
|
O |
O |
|
O |
O |
Digitaria sanquinalis |
G |
N |
C |
|
O |
|
|
|
|
Dimocarpus longan |
T |
N |
C |
F |
O |
|
O |
|
|
Duranta repens |
S |
E |
C |
F |
|
|
|
|
|
Embelia laeta |
C |
N |
VC |
|
F |
O |
|
F |
O |
Embelia ribes |
C |
N |
C |
|
F |
|
|
F |
|
Eriachne pallescens |
G |
N |
C |
|
|
A |
|
|
|
Erigeron floribundus |
H |
N |
VC |
|
|
|
|
|
O |
Eurya nitida |
S |
N |
VC |
|
F |
F |
|
F |
O |
Ficus hirta |
T |
N |
VC |
O |
|
|
|
|
|
Ficus hispida |
T |
N |
VC |
F |
|
|
F |
|
|
Ficus microcarpa |
T |
N |
VC |
O |
F |
|
|
O |
|
Ficus variegata |
T |
N |
C |
F |
|
|
|
|
|
Garcinia oblongifolia |
T |
N |
C |
F |
|
|
|
|
|
Glochidion lanceolatum |
S |
N |
C |
F |
|
|
|
|
O |
Gnetum montanum |
C |
N |
C |
F |
|
|
|
O |
|
Gardenia jasminoides |
S |
N |
C |
F |
|
|
|
|
|
Gordonia axillaris |
S |
N |
C |
O |
O |
|
|
O |
|
Gymnema sylvestre |
C |
N |
C |
|
F |
O |
|
O |
O |
Hedyotis acutangula |
H |
N |
VC |
|
F |
|
|
|
|
Helicteres angustifolia |
H |
N |
VC |
|
F |
F |
|
O |
F |
Ilex asprella |
S |
N |
VC |
F |
F |
F |
|
O |
F |
Inula cappa |
H |
N |
VC |
|
F |
F |
|
F |
|
Ipomoea cairica |
C |
N |
VC |
|
O |
|
|
|
O |
Ischaemum aristatum |
G |
N |
VC |
|
F |
D |
|
O |
A |
Lantana camara |
S |
E |
VC |
O |
F |
|
|
F |
O |
Leucaena leucocephala |
S |
N |
VC |
F |
|
|
|
|
|
Ligustrum sinensis |
S |
N |
VC |
F |
F |
|
|
|
|
Litchi chinensis |
T |
N |
C |
|
|
|
O |
|
|
Litsea cubeba |
T |
N |
C |
|
F |
|
|
|
|
Litsea glutinosa |
T |
N |
VC |
F |
|
O |
|
O |
F |
Litsea rotundifolia |
S |
N |
VC |
O |
F |
O |
|
O |
F |
Livistona chinensis |
P |
N |
VC |
O |
|
|
O |
S |
|
Lygodium dichotomum |
C |
N |
VC |
O |
O |
F |
|
|
O |
Macaranga tanarius |
T |
N |
VC |
F |
O |
|
F |
|
O |
Machilus velutina |
T |
N |
C |
O |
|
|
|
|
|
Macroptilium atropurpureum |
S |
E |
C |
|
F |
|
|
|
|
Mallotus paniculatus |
T |
N |
C |
F |
F |
|
|
S |
|
Mangifera indica |
T |
N |
VC |
O |
|
|
|
|
|
Melaleuca leucadendron |
T |
E |
C |
A |
|
|
|
|
|
Melastoma candidum |
S |
N |
VC |
|
F |
F |
|
F |
F |
Melodinus monogynus |
C |
N |
C |
F |
|
|
|
|
|
Michelia alba |
T |
E |
C |
|
|
|
F |
|
|
Microcos paniculata |
S |
N |
C |
F |
|
|
|
|
|
Mikania micrantha |
C |
E |
VC |
|
O |
|
F |
|
|
Millettia reticulata |
C |
N |
VC |
|
F |
|
|
F |
|
Miscanthus sinensis |
G |
N |
VC |
|
|
|
|
O |
|
Morus alba |
S |
N |
C |
|
O |
|
|
O |
|
Musa paradisiaca |
S |
N |
C |
O |
|
|
F |
|
|
Mussaenda pubescens |
S |
N |
VC |
O |
F |
|
|
F |
|
Nerium indicum |
S |
E |
VC |
|
O |
|
|
|
|
Neyraudia arundinacea |
G |
N |
VC |
|
O |
|
|
O |
O |
Paederia scandens |
C |
N |
C |
F |
O |
|
|
|
|
Pandanus tectorius |
S |
N |
VC |
|
S |
|
|
|
|
Panicum maximum |
G |
N |
C |
O |
O |
|
|
|
|
Paspalum conjugatum |
G |
N |
C |
|
O |
|
|
|
|
Pavetta hongkongensis* |
S |
N |
P |
S |
|
|
|
|
|
Pennisetum purpureum |
G |
N |
C |
|
O |
|
|
|
|
Phoenix hanceana |
P |
N |
C |
|
O |
|
|
|
|
Phyllanthus emblica |
T |
N |
C |
|
F |
|
|
F |
O |
Phyllanthus cochinchinensis |
S |
N |
VC |
O |
|
F |
|
|
|
Psychotria rubra |
S |
N |
VC |
F |
F |
|
|
F |
|
Pteroloma triquetrum |
H |
N |
VC |
|
F |
|
|
|
|
Punica granatum |
S |
N |
C |
|
|
|
F |
|
|
Rhaphiolepis indica |
S |
N |
VC |
|
F |
F |
|
|
|
Rhodomyrtus tomentosa |
S |
N |
VC |
|
A |
F |
|
|
F |
Rhus chinensis |
S |
N |
VC |
|
|
|
|
F |
F |
Rhus succedanea |
S |
N |
VC |
F |
F |
|
|
F |
|
Rhynchelytrum repens |
G |
N |
VC |
|
|
F |
|
|
O |
Saccharum officinarum |
S |
N |
C |
|
|
|
O |
|
|
Sapium discolor |
S |
N |
C |
O |
O |
|
|
|
|
Sapium sebiferum |
S |
N |
C |
|
F |
|
|
|
|
Schefflera octophylla |
S |
N |
VC |
F |
F |
|
|
F |
|
Setaria glauca |
G |
N |
C |
|
O |
F |
|
|
|
Stachytarpheta jamaicensis |
H |
N |
VC |
|
F |
O |
|
|
|
Sterculia lanceolata |
T |
N |
C |
F |
|
|
|
|
|
Strobbilanthes alata |
S |
N |
C |
|
O |
|
|
|
|
Strophanthus divaricatus |
C |
N |
VC |
F |
|
O |
|
|
|
Thevetia peruviana |
S |
E |
VC |
|
O |
|
|
|
|
Trema orientalis |
S |
N |
VC |
|
F |
|
|
F |
|
Tricalysia dubia |
S |
N |
VC |
O |
|
|
F |
|
|
Wedelia chinensis |
C |
N |
VC |
|
F |
|
|
|
|
Wikstroemia chinensis |
S |
N |
VC |
F |
F |
|
|
|
|
Uvaria microcarpa |
C |
N |
C |
F |
O |
|
|
|
|
Vitex negundo |
S |
N |
C |
O |
F |
|
|
|
|
Zanthoxylum avicennae |
S |
N |
VC |
F |
|
|
|
|
|
Total no. of Species |
|
|
|
64 |
74 |
25 |
18 |
42 |
25 |
Abundance: A=Abundant; F=Frequent; O=Occasional; S=Scarce
Status: C=Common; VC=Very Common; P=Protected
Plant Form: G=Grass; Climber; H=Herb; P=Palm; S=Shrub; T=Tree
Origin: N=Native; E=Exotic
* Indicated Species of Conservation Interest
Table 6 Bird Species Recorded during
Point Count Surveys
|
|
Point Count Location |
||||||||||
Bird Species |
Scientific Names |
Status |
Activities |
W1 |
W2 |
W3 |
S1 |
S2 |
S3 |
G1 |
G2 |
G3 |
Black Kite* |
Milvus migrans |
WV, R |
Fl, Fr |
O |
O |
O |
O |
O |
O |
O |
O |
O |
White-bellied Sea
Eagle* |
Haliaeetus
leucogaster |
R |
Fl |
|
|
|
|
|
|
|
|
|
Chinese Francolin |
Francolinus
pintadeanus |
R |
P, Br |
|
|
|
O |
O |
O |
|
O |
O |
White-breasted
Waterhen |
Amaurornis
phoenicurus |
R |
Fr |
O |
|
|
|
|
|
|
|
|
Spotted Dove |
Streptopelia
chinensis |
R |
P, Fr |
O |
O |
O |
O |
|
|
|
|
|
Oriental Turtel Dove |
Streptopelia
orientalis |
WV |
P |
O |
|
|
|
|
|
|
|
|
Emerald Dove* |
Chalcophaps indica |
R |
P |
|
O |
O |
|
|
|
|
|
|
Large Hawk Cuckoo |
Cuculus
sparverioides |
SV |
Br |
|
|
|
|
|
|
|
|
|
Indian Cuckoo |
Cuculus micropterus |
SV |
Br, Fl |
O |
O |
O |
|
|
|
|
O |
|
Chestnut-winged
Cuckoo |
Clamator coromandus |
SV |
Br |
|
|
O |
|
|
|
|
|
|
Common Koel |
Eudynamis scolopacea |
SV, R |
Br |
O |
O |
O |
|
|
|
|
|
|
Greater Coucal* |
Centropus sinensis |
R |
P, Fr |
O |
|
|
O |
|
|
|
|
|
Lesser Coucal* |
Centropus
bengalensis |
R |
P, Fr |
O |
O |
O |
O |
O |
|
|
O |
|
Savanna Nightjar |
Caprimulgus affinis |
SV, WV |
Fl |
|
|
|
|
|
|
|
O |
|
Pacific Swift |
Apus pacificus |
SM, SV |
Fl |
|
|
|
|
|
|
|
|
|
Little Swift |
Apus affinis |
R, SM |
Fl |
|
|
|
O |
|
|
|
|
|
Barn Swallow |
Hirundo rustica |
SM, SV |
Fl |
O |
|
O |
O |
|
|
O |
O |
|
Red-rumped Swallow |
Hirundo daurica |
M |
Fl |
O |
|
|
|
|
|
O |
|
|
White-throated
Kingfisher |
Halcyon smyrnensis |
AM, P |
P, Fl |
|
|
O |
O |
|
|
|
|
|
Eurasian
Tree Sparrow |
Passer monttanus |
R |
P, Fr, Br |
O |
|
|
|
|
|
|
|
|
Red-whiskered Bulbul |
Pycnonotus jocosus |
R |
P, Fr, Br |
O |
O |
O |
|
|
O |
O |
O |
O |
Chinese Bulbul |
Pyconotus sinensis |
R |
P, Fr, Br |
O |
O |
O |
O |
O |
|
O |
O |
O |
Sooty-headed Bulbul |
Pyconotus aurigaster |
R |
P, Fr |
|
|
O |
O |
O |
O |
O |
O |
O |
Oriental Magpie
Robin |
Copsychus saularis |
R |
P, Fr, Br |
O |
O |
O |
|
|
O |
O |
|
|
Yellow-bellied
Prinia |
Prinia flaviventris |
R |
P |
|
|
|
O |
|
O |
|
|
|
Plain
Prinia |
Prinia inornata |
R |
P |
|
|
|
|
|
|
|
|
|
Common Tailorbird |
Orthotomus sutorius |
R |
P, Fr |
O |
O |
O |
|
|
|
|
|
O |
Masked Laughing
Thrush |
Garrulax
perspicillatus |
R |
P, Fr |
|
O |
O |
|
|
O |
|
|
|
Hwamei |
Garrulax canorus |
R |
P, Br |
|
O |
|
O |
O |
O |
O |
O |
O |
Japanese White-eye |
Zosterops japonica |
R, WV |
Fl |
O |
O |
|
|
|
|
|
|
|
Long-tailed Shrike |
Lanius schach |
R |
P |
|
|
O |
|
O |
O |
|
O |
O |
Black Drongo |
Dicrurus macrocercus |
M, SV |
P, Fl |
O |
|
O |
O |
O |
O |
|
|
|
Common Magpie |
Pica pica |
R |
P, Fl |
|
|
O |
|
|
|
O |
|
|
Large -billed Crow |
Corvus macrorhynchus |
R |
Fl |
|
|
O |
|
|
|
|
|
|
Black-collared
Starling |
Sturnus nigricollis |
R |
P, Fl |
O |
O |
O |
|
O |
O |
O |
|
|
White-shouldered
Starling |
Sturnus sinensis |
M, WV, SV |
P |
O |
|
|
|
|
|
|
|
|
Crested Myna |
Acridotheres
cristatellus |
R |
P, Fl |
O |
O |
|
O |
|
|
O |
|
O |
White-rumped Munia |
Lonchura striata |
R |
Fr, Br |
O |
|
|
|
|
O |
|
|
|
‘O’
sign indicates that the species was encountered at the particular sampled point
during the surveys.
Principle Status:
P=Present all year, SM=Spring Migrant, AM=Autumn Migrant, M=Migrant, SV=Summer
Visitor, WV=Winter Visitor, R=Resident.
Activities
P = perching/preening, Fr = foraging, Fl = Flying above, Br = Breeding
activities.
* Indicates Species of Conservation Interest
Table 7a Details
of Bird Survey Record in Woodland
|
W1 |
W2 |
W3 |
||||||||||||||||
Bird Species |
Scientific Names |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
Black Kite |
Milvus migrans |
6 |
4 |
|
|
1 |
|
7 |
|
|
6 |
1 |
|
2 |
4 |
6 |
1 |
8 |
|
White-bellied Sea
Eagle |
Haliaeetus
leucogaster |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Chinese Francolin |
Francolinus
pintadeanus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
White-breasted
Waterhen |
Amaurornis
phoenicurus |
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Spotted Dove |
Streptopelia
chinensis |
2 |
2 |
1 |
1 |
1 |
1 |
|
1 |
|
1 |
2 |
|
1 |
1 |
|
2 |
2 |
|
Oriental Turtel Dove |
Streptopelia
orientalis |
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Emerald Dove |
Chalcophaps indica |
|
|
|
|
|
|
|
1 |
1 |
1 |
|
1 |
|
|
|
|
1 |
|
Large Hawk Cuckoo |
Cuculus
sparverioides |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Indian Cuckoo |
Cuculus micropterus |
1 |
|
|
|
|
1 |
1 |
|
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
|
Chestnut-winged
Cuckoo |
Clamator coromandus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1 |
|
|
|
Common Koel |
Eudynamis scolopacea |
1 |
|
|
|
|
|
|
1 |
|
|
|
|
1 |
|
|
1 |
1 |
|
Greater Coucal |
Centropus sinensis |
1 |
1 |
1 |
2 |
|
1 |
|
1 |
2 |
1 |
|
|
1 |
1 |
1 |
1 |
2 |
|
Lesser Coucal |
Centropus bengalensis |
1 |
|
2 |
|
1 |
|
1 |
|
1 |
|
1 |
|
|
1 |
|
|
|
|
Savanna Nightjar |
Caprimulgus affinis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Pacific Swift |
Apus pacificus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Little Swift |
Apus affinis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Barn Swallow |
Hirundo rustica |
|
|
|
|
4 |
|
|
|
|
|
|
|
|
|
|
|
2 |
|
Red-rumped Swallow |
Hirundo daurica |
|
|
|
|
2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
White-throated
Kingfisher |
Halcyon smyrnensis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1 |
|
Eurasian Tree
Sparrow |
Passer monttanus |
|
3 |
|
2 |
4 |
1 |
|
|
|
|
|
|
|
|
|
|
|
|
Red-whiskered Bulbul |
Pycnonotus jocosus |
2 |
2 |
|
3 |
2 |
3 |
1 |
2 |
2 |
5 |
2 |
|
2 |
2 |
|
2 |
1 |
2 |
Chinese Bulbul |
Pyconotus sinensis |
2 |
2 |
|
2 |
2 |
2 |
4 |
|
|
|
|
3 |
|
|
|
1 |
2 |
1 |
Sooty-headed Bulbul |
Pyconotus aurigaster |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
2 |
|
Oriental Magpie
Robin |
Copsychus saularis |
1 |
2 |
1 |
2 |
1 |
2 |
|
1 |
1 |
2 |
3 |
1 |
1 |
1 |
|
1 |
|
|
Yellow-bellied
Prinia |
Prinia flaviventris |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Plain Prinia |
Prinia inornata |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Tailorbird |
Orthotomus sutorius |
2 |
|
|
1 |
1 |
|
|
1 |
2 |
1 |
1 |
1 |
1 |
2 |
|
|
1 |
|
Masked Laughing
Thrush |
Garrulax
perspicillatus |
|
|
|
|
|
|
|
|
|
2 |
|
|
|
3 |
|
|
|
|
Hwamei |
Garrulax canorus |
|
|
|
|
|
|
|
1 |
|
|
1 |
1 |
|
|
|
|
|
|
Japanese White-eye |
Zosterops japonica |
|
|
1 |
3 |
|
3 |
|
|
|
|
|
2 |
|
|
|
|
|
|
Long-tailed Shrike |
Lanius schach |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1 |
Black Drongo |
Dicrurus macrocercus |
2 |
|
1 |
1 |
|
|
|
|
|
|
|
|
1 |
1 |
|
|
|
|
Common Magpie |
Pica pica |
|
|
|
|
|
|
|
|
|
|
|
|
2 |
1 |
|
|
1 |
|
Large -billed Crow |
Corvus macrorhynchus |
|
|
|
|
|
|
|
|
|
|
|
|
1 |
|
|
|
|
|
Black-collared Starling |
Sturnus nigricollis |
|
|
|
2 |
|
|
1 |
1 |
|
|
|
|
|
|
|
|
|
|
White-shouldered
Starling |
Sturnus sinensis |
|
|
|
2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Crested Myna |
Acridotheres
cristatellus |
2 |
|
|
2 |
3 |
1 |
2 |
|
|
|
|
|
|
|
|
|
|
|
White-rumped Munia |
Lonchura striata |
|
1 |
2 |
2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Table 7b Details
of Bird Survey Record in Shrubland
|
S1 |
S2 |
S3 |
||||||||||||||||
Bird Species |
Scientific Names |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
Black Kite |
Milvus migrans |
23 |
15 |
11 |
15 |
|
|
18 |
8 |
18 |
|
|
|
|
|
10 |
|
|
|
White-bellied Sea Eagle |
Haliaeetus
leucogaster |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Chinese Francolin |
Francolinus
pintadeanus |
|
1 |
1 |
|
|
1 |
1 |
1 |
1 |
1 |
1 |
|
|
|
1 |
|
1 |
|
White-breasted
Waterhen |
Amaurornis
phoenicurus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Spotted Dove |
Streptopelia
chinensis |
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Oriental Turtel Dove |
Streptopelia
orientalis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Emerald Dove |
Chalcophaps indica |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Large Hawk Cuckoo |
Cuculus
sparverioides |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Indian Cuckoo |
Cuculus micropterus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Chestnut-winged
Cuckoo |
Clamator coromandus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Koel |
Eudynamis scolopacea |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Greater Coucal |
Centropus sinensis |
|
|
|
|
|
2 |
|
|
|
|
|
|
|
|
|
|
|
|
Lesser Coucal |
Centropus
bengalensis |
1 |
1 |
|
3 |
1 |
1 |
|
1 |
1 |
1 |
|
1 |
|
|
|
|
|
|
Savanna Nightjar |
Caprimulgus affinis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Pacific Swift |
Apus pacificus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Little Swift |
Apus affinis |
|
|
|
|
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
Barn Swallow |
Hirundo rustica |
|
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|
Red-rumped Swallow |
Hirundo daurica |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
White-throated
Kingfisher |
Halcyon smyrnensis |
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Tree
Sparrow |
Passer monttanus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Red-whiskered Bulbul |
Pycnonotus jocosus |
|
|
4 |
|
|
|
|
|
|
|
|
|
|
|
2 |
3 |
|
1 |
Chinese Bulbul |
Pyconotus sinensis |
|
2 |
3 |
4 |
|
|
4 |
3 |
|
|
|
2 |
|
|
|
|
|
|
Sooty-headed Bulbul |
Pyconotus aurigaster |
|
|
|
|
3 |
|
2 |
|
|
|
|
|
|
|
|
|
|
1 |
Oriental Magpie Robin |
Copsychus saularis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1 |
|
1 |
Yellow-bellied
Prinia |
Prinia flaviventris |
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|
1 |
|
Plain Prinia |
Prinia inornata |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Tailorbird |
Orthotomus sutorius |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Masked Laughing
Thrush |
Garrulax
perspicillatus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
4 |
Hwamei |
Garrulax canorus |
|
|
2 |
1 |
|
1 |
|
1 |
1 |
1 |
1 |
1 |
|
|
|
1 |
|
|
Japanese White-eye |
Zosterops japonica |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Long-tailed Shrike |
Lanius schach |
|
|
|
|
|
|
|
1 |
|
1 |
|
|
|
|
1 |
|
|
|
Black Drongo |
Dicrurus macrocercus |
|
|
|
|
|
|
|
|
1 |
|
|
|
|
|
|
1 |
|
1 |
Common Magpie |
Pica pica |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Large -billed Crow |
Corvus macrorhynchus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-collared
Starling |
Sturnus nigricollis |
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
2 |
2 |
2 |
White-shouldered
Starling |
Sturnus sinensis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Crested Myna |
Acridotheres
cristatellus |
|
1 |
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
1 |
White-rumped Munia |
Lonchura striata |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
2 |
|
Table 7c Details
of Bird Survey Record in Shrubby Grassland
|
G1 |
G2 |
G3 |
||||||||||||||||
Bird Species |
Scientific Names |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
Black Kite |
Milvus migrans |
2 |
2 |
|
|
2 |
|
2 |
4 |
|
|
|
|
1 |
|
|
1 |
|
|
White-bellied Sea
Eagle |
Haliaeetus
leucogaster |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Chinese Francolin |
Francolinus
pintadeanus |
|
|
|
|
|
|
|
1 |
|
1 |
|
|
1 |
|
|
|
|
|
White-breasted
Waterhen |
Amaurornis
phoenicurus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Spotted Dove |
Streptopelia
chinensis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Oriental Turtel Dove |
Streptopelia
orientalis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Emerald Dove |
Chalcophaps indica |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Large Hawk Cuckoo |
Cuculus
sparverioides |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Indian Cuckoo |
Cuculus micropterus |
|
|
|
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
Chestnut-winged
Cuckoo |
Clamator coromandus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Koel |
Eudynamis scolopacea |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Greater Coucal |
Centropus sinensis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Lesser Coucal |
Centropus
bengalensis |
|
|
|
|
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
Savanna Nightjar |
Caprimulgus affinis |
|
|
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
Pacific Swift |
Apus pacificus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Little Swift |
Apus affinis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Barn Swallow |
Hirundo rustica |
|
1 |
|
|
|
|
|
|
|
|
|
1 |
|
|
|
|
|
|
Red-rumped Swallow |
Hirundo daurica |
2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
White-throated
Kingfisher |
Halcyon smyrnensis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Eurasian Tree
Sparrow |
Passer monttanus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Red-whiskered Bulbul |
Pycnonotus jocosus |
|
|
2 |
|
|
|
|
|
|
|
|
2 |
3 |
|
|
|
|
2 |
Chinese Bulbul |
Pyconotus sinensis |
3 |
|
|
|
|
|
|
|
|
|
1 |
|
|
4 |
|
3 |
|
1 |
Sooty-headed Bulbul |
Pyconotus aurigaster |
3 |
|
|
|
3 |
|
|
3 |
|
|
|
|
2 |
|
|
3 |
|
3 |
Oriental Magpie
Robin |
Copsychus saularis |
|
|
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Yellow-bellied
Prinia |
Prinia flaviventris |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Plain Prinia |
Prinia inornata |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Tailorbird |
Orthotomus sutorius |
|
|
|
|
|
|
|
|
|
|
|
|
1 |
|
1 |
|
1 |
|
Masked Laughing
Thrush |
Garrulax
perspicillatus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Hwamei |
Garrulax canorus |
1 |
|
|
|
|
|
|
|
|
|
|
1 |
|
|
|
|
|
1 |
Japanese White-eye |
Zosterops japonica |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Long-tailed Shrike |
Lanius schach |
|
|
|
|
|
|
|
|
|
|
1 |
|
|
|
|
1 |
|
|
Black Drongo |
Dicrurus macrocercus |
|
|
|
1 |
1 |
|
|
|
|
|
|
|
|
|
|
|
|
|
Common Magpie |
Pica pica |
|
|
1 |
|
|
|
|
|
|
|
2 |
|
|
|
|
1 |
|
|
Large -billed Crow |
Corvus macrorhynchus |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black-collared
Starling |
Sturnus nigricollis |
|
|
2 |
|
|
|
|
|
|
2 |
|
|
|
|
|
|
|
|
White-shouldered
Starling |
Sturnus sinensis |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Crested Myna |
Acridotheres
cristatellus |
2 |
|
|
|
|
|
2 |
|
|
|
|
|
2 |
|
|
|
2 |
|
White-rumped Munia |
Lonchura striata |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Table
8 Flight Attempts of All Primary Bird Species
Recorded within Zone 5 (Total Number of Individuals was presented in
Brackets). Observation time
was 6 hours (360 minutes) per day.
Each of the Flight Attempt has lasted for not more than 30 seconds.
|
|
Mean
Utilisation Rate (Birds/min) |
Day 1 (20th May 2004) |
Day 2 (23rd May 2004) |
Day 3 (26th May 2004) |
Day 4 (29th May 2004) |
Day 5 (30th May 2004) |
Day 6 (6th June 2004) |
||||||||||||
Weather |
|
|
Overcast |
Sunny |
Sunny |
Sunny |
Rainy |
Cloudy |
||||||||||||
Wind Direction |
|
|
45° |
45° |
45° |
45° |
45° |
45° |
||||||||||||
Visibility |
|
|
>2km |
>2km |
>2km |
>2km |
>2km |
>2km |
||||||||||||
Flight height |
|
Height above10 and below100m |
<10m |
>10m<100m |
>100m |
<10m |
>10m<100m |
>100m |
<10m |
>10m<100m |
>100m |
<10m |
>10m<100m |
>100m |
<10m |
>10m<100m |
>100m |
<10m |
>10m<100m |
>100m |
Bird
Species |
Behaviour
recorded |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Black Kite Milvus migrans |
Foraging and soaring |
0.0333 |
|
14 (23) |
4 (23) |
|
19 (19) |
10 (19) |
|
13 (21) |
7 (21) |
|
19 (18) |
|
|
72 (21) |
2 (21) |
|
7 (16) |
|
White-bellied Sea Eagle Haliaeetus leucogaster |
Flying pass over the Study Area |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1 (1) |
|
|
|
Spotted Dove Streptopelia chinensis |
Flying pass over the Study Area |
|
3 (3) |
|
|
|
|
|
|
|
|
4 (4) |
|
|
|
|
|
1 (1) |
|
|
Greater Coucal Centropus sinensis |
Flying pass over the Study Area |
|
|
|
|
|
|
|
|
|
|
1 (1) |
|
|
|
|
|
|
|
|
Little Swift Apus affinis |
Foraing and Flying |
0.0004 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
2 (2) |
|
Barn Swallow Hirundo rustica |
Foraing and Flying |
0.0007 |
|
|
1 (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
3 (3) |
|
White-throated Kingfisher Halcyon smyrnensis |
Flying pass over the Study Area |
|
1 (1) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Chinese Bulbul Pyconotus sinensis |
Flying pass over the Study Area |
|
4
(4) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Sooty-headed Bulbul Pyconotus aurigaster |
Flying pass over the Study Area |
|
18
(18) |
|
|
|
|
|
2 (2) |
|
|
|
|
|
|
|
|
|
|
|
Common Magpie Pica pica |
Flying pass over the Study Area |
|
1
(1) |
|
|
|
|
|
|
|
|
|
|
|
1 (1) |
|
|
|
|
|
Black-collared Starling Sturnus nigricollis |
Flying pass over the Study Area |
|
4
(4) |
|
|
|
|
|
|
|
|
2 (2) |
|
|
|
|
|
|
|
|
Crested Myna Acridotheres cristatellus |
Flying pass over the Study Area |
|
|
|
|
3 (3) |
|
|
4 (4) |
|
|
|
|
|
|
|
|
3 (3) |
|
|
Table 9 Butterfly Species Recorded in
the Study Area
Common Name |
Species Name |
Relative
Abundance |
Commonness |
||||
|
|
Secondary
Woodland |
Shrubland |
Shrubby
Grassland |
Village/
Developed Areas |
Stream |
|
Plum Judy |
Abisara echerius |
A |
A |
A |
|
|
VC |
Common Hedge Blue |
Actyolepis puspa |
A |
C |
|
|
|
C |
Bush Hopper* |
Ampittia dioscorides |
S |
|
|
|
|
UC |
Angled Castor |
Ariadne ariadne |
C |
|
|
|
|
C |
Common White |
Artogeia canidia |
C |
O |
O |
|
|
VC |
Colour Sergeant |
Athyma nefte |
C |
|
|
|
|
C |
Common Sergeant |
Athyma perius |
C |
|
|
|
|
C |
Lemon Emigrant |
Catopsilia pomona |
S |
O |
|
|
|
C |
Mottled Emigrant |
Catopsilia pyranthe |
S |
O |
|
|
|
C |
Common Gull |
Cepora nerissa |
C |
S |
S |
|
|
C |
Red Lacewing* |
Cethosia biblis |
S |
|
|
|
|
UC |
Lime Blue |
Chilades lajus |
O |
O |
O |
|
|
VC |
Common Mine |
Chilasa clytia |
A |
O |
O |
|
|
C |
Rustic |
Cupha erymanthis |
O |
|
|
|
|
VC |
Common Mapwing |
Cyrestis thyodamas |
S |
|
|
|
|
C |
Red-based Jezebel |
Delias pasithoe |
O |
O |
|
|
|
VC |
Common Duffer* |
Discophora sondaica |
C |
|
|
|
|
UC |
Common Palmfly |
Elymnias hypermnestra |
S |
|
|
|
|
C |
Blue-spotted Crow |
Euploea midamus |
O |
|
|
|
|
VC |
Common Grass Yellow |
Eureman hecabe |
C |
O |
O |
|
|
VC |
White-edged Blue Baron* |
Euthalia phemius |
S |
|
|
|
|
UC |
Tailed Cupid |
Everes lacturnus |
C |
O |
|
|
|
C |
Large Faun |
Faunis eumeus |
O |
S |
|
|
|
VC |
Tailed Jay |
Graphium agamemnon |
O |
|
O |
|
|
VC |
Common Jay |
Graphium doson |
S
|
|
|
|
|
C |
Common Blue bottle |
Graphium sarpedono |
A |
O |
S |
S |
|
VC |
Great Orange Tip |
Hebomoia glaucippe |
O |
|
O |
|
|
C |
Purple Sapphire |
Heliophorous epicles |
S |
|
|
|
|
C |
Red Ring Skirt |
Hestina assimilis |
O |
S |
|
|
|
C |
Tree Flitter* |
Hyarotis adrastus |
O |
|
|
|
|
UC |
Great Egg-fly |
Hypolimnas bolina |
C |
|
|
|
|
VC |
Ceylon Blue Tiger |
Ideopsis similes |
C |
|
O |
|
|
VC |
Yellow Orange Tip* |
Ixias pyrene |
O |
O |
|
|
|
UC |
Dark Cerulean |
Jamides bochus |
S |
|
|
|
|
C |
Grey Pansy |
Junonia atlites |
A |
|
|
|
|
C |
Lemon Pansy |
Junonia lemonias |
C |
O |
O |
|
|
C |
Banded Tree Brown |
Lethe confusa |
C |
S |
O |
|
|
VC |
Common Evening Brown |
Melanitis leda |
C |
|
|
|
|
C |
Dark-band Bush Brown |
Mycalesis mineus |
O |
O |
O |
|
|
VC |
South Sullied Sailer |
Neptis clinia |
O |
|
|
|
|
C |
Common Sailer |
Neptis hylas |
O |
|
O |
|
|
VC |
Chestnut Angle |
Odontoptilum augulatum |
S |
|
|
|
|
C |
Common Lascar |
Pantoporia hordonia |
S |
|
|
|
|
C |
Chinese Peacock |
Papilio bianor |
O |
|
S |
|
|
VC |
Lime Butterfly |
Papilio demoleus |
|
C |
C |
|
|
C |
Red Helen |
Papilio helenus |
O |
S |
|
|
|
VC |
Great Mormon |
Papilio memnon |
O |
|
S |
|
|
VC |
Paris Peacock |
Papilio paris |
O |
O |
S |
S |
|
VC |
Common Mormon |
Papilio polytes |
A |
C |
O |
S |
|
VC |
Spangle |
Papilio protentor |
O |
|
|
|
|
VC |
Swallowtail* |
Papilio xuthus |
S |
|
|
|
|
UC |
Glassy Tiger |
Parantica aglea |
O |
O |
O |
|
|
VC |
Oriental Straight Swift |
Parnara bada |
O |
|
|
|
|
C |
Five-bar Swordtail |
Pathysa antiphates |
S |
|
|
|
|
C |
Little Banded Swift |
Pelopidas agna |
O |
|
|
|
|
C |
Indian Cabbage White |
Pieris canidia |
C |
|
S |
|
|
VC |
Small Cabbage White* |
Pieris rapae |
C |
|
|
|
|
UC |
Pale Grass Blue |
Psedozizeeria maha |
A |
C |
|
|
|
VC |
Common Jester |
Symbrenthia lilaea |
S |
|
|
|
|
C |
Water Snow Flat |
Tagiades litigiosus |
O |
|
|
|
|
C |
Blue Tiger |
Tirumala limniace |
C |
O |
O |
|
|
C |
Common Five-ring |
Ypthima baldus |
|
A |
A |
|
|
VC |
Punchinello |
Zemeros flegyas |
O |
|
|
|
|
C |
Total Species |
|
61 |
26 |
23 |
3 |
|
|
Relative Abundance: A= Abundant; C
= Common; O = Occasional; S = Scarce.
Commonness
(Walthew 1997): UC = uncommon; C = common; VC = very common.
*
Indicates Species of Conservation Interest
Table 10 Dragonfly Recorded in
the Study Area
Common Names |
Species Name |
Relative Abundance |
Commonness |
||||
|
|
Secondary Woodland |
Shrubland |
Shrubby Grassland |
Village/ Developed Area |
Stream |
|
Orange-tailed Sprite |
Ceriagrion auranticum ryukyuanum |
|
|
|
|
S |
Abundant |
Common Blue Skimmer |
Orthetrum glaucum |
|
S |
|
S |
S |
Abundant |
Common Red Skimmer |
Orthetrum pruinosum neglectum |
|
|
|
|
S |
Abundant |
Wandering Glider |
Pantala flavescens |
|
O |
O |
|
|
Abundant |
Relative Abundance: A=
Abundant; C = Common; O = Occasional; S = Scarce.