Table D1 Plant species recorded in secondary woodland habitat within the Study Area (54 species recorded)
|
Species |
Growth Form |
Exotic |
Relative Abundance |
|
Acacia confusa |
T |
E |
++ |
|
Acronychia pedunculata |
T |
|
+ |
|
Bamboo |
H |
|
++ |
|
Blechnum orientale |
F |
|
+ |
|
Bridelia tomentosa |
T |
|
++ |
|
Brucea javanica |
S |
|
+ |
|
Canthium dicoccum |
T |
|
+ |
|
Celtis sinensis |
T |
|
+++ |
|
Cinnamomum camphora |
T |
|
+++ |
|
Clerodendrum cryptophyllum |
S |
|
++ |
|
Cratoxylum cochinchinensis |
T |
|
+++ |
|
Cymbopogon sp. |
G |
|
+ |
|
Cyperus spp. |
H |
|
+ |
|
Daphniphyllum calycinum |
T |
|
+ |
|
Desmos chinensis |
S |
|
+ |
|
Dicranopteris linearis |
F |
|
++ |
|
Dimocarpus longan |
T |
E |
++ |
|
Embelia laeta |
C |
|
+ |
|
Ficus hirta |
S |
|
+ |
|
Ficus hispida |
T |
|
++ |
|
Ficus microcarpa |
T |
|
+ |
|
Ficus variegata |
T |
|
+++ |
|
Helicteres angustifolia |
H |
|
+ |
|
Ischaemum sp. |
G |
|
+ |
|
Litchi chinensis |
T |
E |
+ |
|
Litsea glutinosa |
T |
|
+++ |
|
Litsea rotundifolia |
S |
|
++ |
|
Lygodium japonicum |
F |
|
+ |
|
Macaranga tanarius |
T |
|
+++ |
|
Mallotus apelta |
T |
|
++ |
|
Mallotus paniculatus |
T |
|
++ |
|
Melia azedarach |
T |
E |
+ |
|
Miscanthus sinensis |
G |
|
+ |
|
Mussaenda pubescens |
S |
|
+ |
|
Passiflora sp. |
C |
|
+ |
|
Pennisetum alopecuroides |
G |
|
+ |
|
Phyllanthus emblica |
T |
|
+ |
|
Pinus massoniana |
T |
|
++ |
|
Psychotria rubra |
S |
|
++ |
|
Pueraria lobata |
C |
E |
++ |
|
Rhaphiolepis indica |
S |
|
++ |
|
Rhodomyrtus tomentosa |
S |
|
+ |
|
Rhus chinensis |
T |
|
++ |
|
Rhus succedanea |
T |
|
+ |
|
Sapium discolor |
T |
|
++ |
|
Sapium sebiferum |
T |
|
++ |
|
Smilax china |
C |
|
+ |
|
Solidago virgo-aurea |
S |
|
+ |
|
Stephania sp. |
C |
|
+ |
|
Strophantus divaricatus |
S |
|
+ |
|
Tetracera asiatica |
C |
|
+ |
|
Tetradium glabrifolium |
T |
|
+ |
|
Uvaria microcarpa |
S |
|
+ |
|
Wikstroemia indica |
S |
|
+ |
Code for Growth Form/Exotic:
T=Tree, S=Shrub, H=Herb, C=Climber, G=Grass; E=Exotic
Code for Relative Abundance:
+++ = common, ++ = occasional, + = scarce
Table D2 Plant
species recorded in grassland/shrubland habitat within the Study Area (44
species recorded)
|
Species |
Growth Form |
Exotic |
Relative Abundance |
|
Aporusa dioica |
T |
|
+ |
|
Bidens pilosa |
H |
|
+++ |
|
Chloris batata |
G |
|
++ |
|
Cinnamomum camphora |
T |
|
+ |
|
Cirsium sp. |
H |
|
+ |
|
Cratoxylum cochinchinensis |
T |
|
+ |
|
Cynodon dactylon |
G |
|
+++ |
|
Desmodium pulchellum |
S |
|
+ |
|
Dicranopteris linearis |
F |
|
+++ |
|
Elephantopus tomentosa |
H |
|
++ |
|
Embelia laeta |
C |
|
++ |
|
Glochidion zeylanicum |
T |
|
+ |
|
Hedyotis auricularia |
H |
|
|
|
Ilex asprella |
S |
|
+ |
|
Imperata cylindrica |
G |
|
++ |
|
Lantana camara |
S |
E |
+ |
|
Leucaena leucocephala |
T |
E |
+ |
|
Litsea cubeba |
T |
|
+ |
|
Litsea glutinosa |
T |
|
+ |
|
Litsea rotundifolia |
S |
|
+ |
|
Lygodium japonicum |
F |
|
+ |
|
Mallotus apelta |
T |
|
+ |
|
Mallotus paniculatus |
T |
|
+ |
|
Melastoma candidum |
S |
|
++ |
|
Melastoma dodecandrum |
S |
|
+ |
|
Melia azedarach |
T |
E |
+ |
|
Mikania micrantha |
C |
E |
++ |
|
Mimosa pudica |
H |
|
++ |
|
Miscanthus sinensis |
G |
|
+ |
|
Panicum maximum |
G |
E |
+ |
|
Phragmites australis |
G |
|
+ |
|
Phyllanthus emblica |
T |
|
+ |
|
Psychotria rubra |
S |
|
+ |
|
Rhodomyrtus tomentosa |
S |
|
++ |
|
Rhus succedanea |
T |
|
+ |
|
Saccharum arundinaceum |
G |
|
++ |
|
Sapium discolor |
T |
|
+ |
|
Sapium sebiferum |
T |
|
+ |
|
Sesbania cochinchinensis |
H |
|
+ |
|
Smilax china |
C |
|
++ |
|
Solanum torvum |
S |
|
+ |
|
Tetradium glabrifolium |
T |
|
+ |
|
Wedelia triloba |
C |
E |
++ |
|
Wikstroemia indica |
S |
|
++ |
Code for Growth Form/Exotic:
T=Tree, S=Shrub, H=Herb, C=Climber, G=Grass; E=Exotic
Code for Relative Abundance:
+++ = common, ++ = occasional, + = scarce
Table D3 Plant species recorded in cultivated land within the Study Area (69 species recorded)
|
Species |
Growth Form |
Exotic |
Relative Abundance |
|
|
|
|
|
Active cultivated land |
Abandoned cultivated land |
|
Acacia confusa |
T |
E |
|
+ |
|
Alocasia macrorrhiza |
H |
|
|
++ |
|
Alternanthera sessilis |
H |
|
|
+ |
|
Amaranthus viridus |
H |
|
|
++ |
|
Amygdalus persica |
T |
E |
+++ |
+++ |
|
Apium graveolens |
H |
E |
|
+ |
|
Apluda mutica |
G |
|
|
+++ |
|
Archontophoenix alexandrae |
T |
E |
|
+ |
|
Asparagus officinalis |
H |
E |
|
+ |
|
Bambusa vulgaris var. striata |
T |
E |
|
+ |
|
Bauhinia blakeana |
T |
|
|
+ |
|
Bidens pilosa |
H |
|
|
+++ |
|
Brassica chinensis |
H |
|
++ |
|
|
Brassica juncea |
H |
E |
+ |
+ |
|
Bridelia tomentosa |
T |
|
|
+ |
|
Cassia tora |
S |
|
|
+ |
|
Casuarina equisetifolia |
T |
E |
|
+ |
|
Celtis sinensis |
T |
|
|
+ |
|
Clausena lansium |
T |
E |
+ |
|
|
Coix lachryma-jobi |
G |
|
|
+ |
|
Colocasia esculenta |
C |
E |
+ |
+ |
|
Conyza canadensis |
H |
E |
|
+++ |
|
Cuscuta japonica |
C |
|
|
+ |
|
Cynodon dactylon |
G |
|
|
++ |
|
Dimocarpus longan |
T |
E |
++ |
+ |
|
Eclipta prostrata |
H |
|
|
+ |
|
Ficus elastica |
T |
E |
|
+ |
|
Ficus hispida |
T |
|
|
+ |
|
Ficus variegata |
T |
|
|
+ |
|
Gladiolus gandavensis |
H |
E |
+++ |
|
|
Gossampinus malabaricum |
T |
E |
|
+ |
|
Gynura bicolor |
H |
|
|
+ |
|
Impatiens balsamina |
H |
E |
|
++ |
|
Ipomoea aquatica |
C |
E |
+++ |
++ |
|
Ipomoea batatas |
C |
E |
+ |
+ |
|
Ipomoea cairica |
C |
|
|
++ |
|
Ipomoea hederacea |
C |
|
|
+ |
|
Lactuca sativa |
H |
|
++ |
|
|
Lantana camara |
S |
E |
|
+ |
|
Leucaena leucocephala |
T |
E |
|
++ |
|
Ligustrum sinensis |
S |
|
|
+ |
|
Livistona chinense |
T |
E |
|
+ |
|
Macaranga tanarius |
T |
|
|
++ |
|
Melaleuca quinquinervia |
T |
E |
|
+ |
|
Melia azedarach |
T |
E |
|
+ |
|
Mikania micrantha |
C |
E |
|
+++ |
|
Miscanthus sinensis |
G |
|
|
+ |
|
Musa paradisiaca |
H |
E |
++ |
++ |
|
Neyraudia reynaudiana |
G |
|
|
+ |
|
Oxalis corniculatus |
H |
|
|
+ |
|
Panicum maximum |
G |
E |
|
++ |
|
Panicum repens |
G |
|
|
++ |
|
Paspalum conjugatum |
G |
|
|
++ |
|
Pennisetum alopecuroides |
G |
|
|
+ |
|
Pennisetum purpureum |
G |
|
|
+ |
|
Polygonum chinense |
H |
|
|
++ |
|
Polygonum hydropiper |
H |
|
|
+ |
|
Polygonum perfoliatum |
H |
|
|
+ |
|
Praxelis clematidea |
H |
E |
|
++ |
|
Ricinus communis |
S |
E |
|
++ |
|
Rumex maritimus |
H |
|
|
+ |
|
Sapium sebiferum |
T |
|
|
+ |
|
Scoparia dulcis |
H |
|
|
++ |
|
Solanum mammosum |
S |
E |
+ |
+ |
|
Solanum melongena |
C |
E |
|
+ |
|
Solanum nigrum |
S |
E |
|
+ |
|
Solanum torvum |
S |
|
|
+ |
|
Sporobolus fertilis |
G |
|
|
+ |
|
Triumfetta bartramia |
S |
|
|
+ |
Code for Growth Form/Exotic:
T=Tree, S=Shrub, H=Herb, C=Climber, G=Grass; E=Exotic
Code for Relative Abundance:
+++ = common, ++ = occasional, + = scarce
Table D4 Plant
species recorded in fishpond habitat within the Study Area (49 species
recorded)
|
Species |
Growth Form |
Exotic |
Relative Abundance |
|
Acacia confusa |
T |
E |
+ |
|
Alocasia macrorrhiza |
H |
|
+ |
|
Amaranthus viridus |
H |
|
+ |
|
Amygdalus persica |
T |
E |
++ |
|
Annona squamosa |
T |
E |
+ |
|
Artocarpus heterophylla |
T |
E |
+ |
|
Bidens pilosa |
H |
|
+++ |
|
Canna indica |
H |
E |
++ |
|
Carica papaya |
T |
E |
+ |
|
Cinnamomum camphora |
T |
|
+ |
|
Clerodendrum inerme |
S |
|
+ |
|
Conyza canadensis |
H |
E |
+++ |
|
Cyclosorus interruptus |
F |
|
+ |
|
Cyperus spp. |
H |
|
++ |
|
Dimocarpus longan |
T |
E |
++ |
|
Eclipta prostrata |
C |
|
++ |
|
Eleusine indica |
G |
|
+ |
|
Emilia sonchifolia |
H |
|
+ |
|
Eriobotrya japonica |
T |
E |
+ |
|
Ficus elastica |
T |
E |
+ |
|
Ficus microcarpa |
T |
|
+ |
|
Ficus variegata |
T |
|
+ |
|
Fimbristylis spp. |
H |
|
++ |
|
Lantana camara |
S |
E |
+ |
|
Litchi chinensis |
T |
E |
+ |
|
Macaranga tanarius |
T |
|
++ |
|
Mangifera indica |
T |
E |
+ |
|
Melia azedarach |
T |
E |
+++ |
|
Mikania micrantha |
C |
E |
+++ |
|
Mimosa pudica |
H |
|
++ |
|
Miscanthus floridulus |
G |
|
++ |
|
Miscanthus sinensis |
G |
|
+ |
|
Musa paradisiaca |
H |
E |
+++ |
|
Neyraudia reynaudiana |
G |
|
++ |
|
Panicum maximum |
G |
E |
++ |
|
Panicum repens |
G |
|
+++ |
|
Paspalum conjugatum |
G |
|
+++ |
|
Passiflora sp. |
C |
|
+ |
|
Pennisetum purpureum |
G |
|
++ |
|
Phragmites australis |
G |
|
++ |
|
Podocarpus nagi |
T |
E |
+ |
|
Praxelis clematidea |
H |
E |
++ |
|
Psidium guajava |
T |
E |
++ |
|
Pteroloma triquetrum |
H |
|
+ |
|
Rhynchelytrum repens |
G |
|
++ |
|
Saccharum arundinaceum |
G |
|
+ |
|
Sesbania cochinchinensis |
S |
|
+ |
|
Solanum nigrum |
S |
E |
+ |
|
Sterculia nobilis |
T |
E |
+ |
Code for Growth Form/Exotic:
T=Tree, S=Shrub, H=Herb, C=Climber, G=Grass; E=Exotic
Code for Relative Abundance:
+++ = common, ++ = occasional, + = scarce
Table D5 Plant
species recorded in marsh habitat within the Study Area (39 species recorded)
|
Species |
Growth Form |
Exotic |
Relative Abundance |
|
Acacia auriculiformis |
T |
E |
+ |
|
Acanthus ilicifolius |
H |
|
+ |
|
Achyranthes aspera |
S |
|
++ |
|
Acrostichum aureum |
F |
|
+ |
|
Ageratum conyzoides |
H |
|
+ |
|
Alternanthera sessilis |
H |
|
+++ |
|
Amaranthus viridus |
H |
|
++ |
|
Compositae |
H |
|
+ |
|
Conyza canadensis |
H |
E |
++ |
|
Cyclosorus interruptus |
F |
|
++ |
|
Cynodon dactylon |
G |
|
++ |
|
Cyperus malaccensis |
SE |
|
++ |
|
Cyperus spp. |
H |
|
+++ |
|
Derris trifoliata |
C |
|
+ |
|
Echinochloa crus-galli |
G |
|
+ |
|
Eclipta prostrata |
C |
|
+ |
|
Fimbristylis spp. |
H |
|
++ |
|
Ipomoea cairica |
C |
|
+++ |
|
Lantana camara |
S |
E |
+ |
|
Leucaena leucocephala |
T |
E |
+ |
|
Melia azedarach |
T |
E |
+ |
|
Mikania micrantha |
C |
E |
++ |
|
Mimosa pudica |
H |
|
++ |
|
Nerium indicum |
T |
E |
+ |
|
Paliurus ramosissimus |
T |
|
+ |
|
Panicum maximum |
G |
E |
+ |
|
Paspalum conjugatum |
G |
|
++ |
|
Paspalum sp. |
G |
|
+++ |
|
Pennisetum purpureum |
G |
|
++ |
|
Phragmites australis |
G |
|
+++ |
|
Pluchea indica |
H |
|
++ |
|
Ricinus communis |
S |
E |
+ |
|
Sapium sebiferum |
T |
|
+ |
|
Scoparia dulcis |
H |
|
+ |
|
Sida rhombifolia |
S |
|
+ |
|
Stachytarpheta jamaicensis |
S |
|
+ |
|
Triumfetta bartramia |
S |
|
+ |
|
Wedelia triloba |
C |
E |
+++ |
|
Xanthium sibiricum |
S |
|
+ |
Code for Growth Form/Exotic:
T=Tree, S=Shrub, H=Herb, C=Climber, G=Grass; E=Exotic
Code for Relative Abundance:
+++ = common, ++ = occasional, + = scarce
Table D6 Plant
species recorded in stream channel/nullah habitat within the Study Area (41
species recorded)
|
Species |
Growth Form |
Exotic |
Relative Abundance |
|
Acacia confusa |
T |
E |
++ |
|
Alocasia macrorrhiza |
H |
|
++ |
|
Artocarpus heterophylla |
T |
E |
+ |
|
Bidens pilosa |
H |
|
+++ |
|
Boehmeria nivea |
S |
|
+ |
|
Bridelia tomentosa |
T |
|
+ |
|
Celtis sinensis |
T |
|
+++ |
|
Cleistocalyx operculata |
T |
|
+ |
|
Conyza canadensis |
H |
E |
+ |
|
Cynodon dactylon |
G |
|
++ |
|
Dimocarpus longan |
T |
E |
++ |
|
Euphorbia hirta |
H |
|
+ |
|
Ficus elastica |
T |
E |
+ |
|
Ficus hispida |
T |
|
+++ |
|
Ficus microcarpa |
T |
|
+ |
|
Ficus
tinctoria subsp. gibbosa |
T |
|
+ |
|
Ficus variegata |
T |
|
+ |
|
Gossampinus malabaricum |
T |
E |
+ |
|
Ilex rotunda |
T |
|
+ |
|
Lantana camara |
S |
E |
+ |
|
Leucaena leucocephala |
T |
E |
++ |
|
Ligustrum sinensis |
S |
|
+ |
|
Litsea glutinosa |
T |
|
+ |
|
Lophostemon conferta |
T |
E |
+ |
|
Macaranga tanarius |
T |
|
++ |
|
Melia azedarach |
T |
E |
+ |
|
Mikania micrantha |
C |
E |
+++ |
|
Mimosa pudica |
H |
|
+ |
|
Musa paradisiaca |
H |
E |
+ |
|
Neyraudia reynaudiana |
G |
|
++ |
|
Panicum maximum |
G |
E |
++ |
|
Pennisetum purpureum |
G |
|
++ |
|
Polygonum chinense |
H |
|
++ |
|
Rhynchelytrum repens |
G |
|
+ |
|
Rhus hypoleuca |
T |
|
+ |
|
Ricinus communis |
S |
E |
++ |
|
Sapium sebiferum |
T |
|
+ |
|
Sesbania cochinchinensis |
S |
|
+ |
|
Sida rhombifolia |
S |
|
+ |
|
Sterculia lanceolata |
T |
|
+ |
|
Triumfetta bartramia |
S |
|
+ |
Code for Growth Form/Exotic:
T=Tree, S=Shrub, H=Herb, C=Climber, G=Grass; E=Exotic
Code for Relative Abundance:
+++ = common, ++ = occasional, + = scarce
Boldface = locally
rare/restricted
Table D7 Plant
species recorded in mangrove habitat within the Study Area (14 species
recorded)
|
Species |
Growth Form |
Exotic |
Relative Abundance |
|
Acanthus ilicifolius |
H |
|
+++ |
|
Aegiceras corniculatum |
S |
|
+++ |
|
Alternanthera sessilis |
H |
|
+ |
|
Brachiaria mutica |
G |
|
+ |
|
Cyperus malaccensis |
SE |
|
++ |
|
Cyperus spp. |
H |
|
++ |
|
Derris trifoliata |
C |
|
+ |
|
Excoecaria agallocha |
T |
|
+ |
|
Fimbristylis spp. |
H |
|
++ |
|
Ipomoea cairica |
C |
|
++ |
|
Kandelia candel |
T |
|
+++ |
|
Mikania micrantha |
C |
E |
++ |
|
Phragmites australis |
G |
|
+++ |
|
Pongamia pinnata |
T |
|
++ |
Code for Growth Form/Exotic: T=Tree,
S=Shrub, H=Herb, C=Climber, G=Grass; E=Exotic
Code for Relative Abundance:
+++ = common, ++ = occasional, + = scarce
Table D8 Plant
species recorded in disturbed/urbanised area habitat within the Study Area (137
species recorded)
|
Species |
Growth Form |
Exotic |
Relative Abundance |
|
Acacia auriculiformis |
T |
E |
++ |
|
Acacia confusa |
T |
E |
+++ |
|
Acacia mangium |
T |
E |
+ |
|
Aglaia odorata |
S |
E |
+ |
|
Ailanthus fordii |
T |
|
+ |
|
Albizia lebbeck |
T |
E |
+ |
|
Aleurites moluccana |
T |
E |
+ |
|
Allamanda cathartica |
S |
E |
++ |
|
Alocasia macrorrhiza |
H |
|
+ |
|
Alpinia zerumbet
'Variegata' |
H |
E |
+ |
|
Amaranthus viridus |
S |
|
+ |
|
Aporusa dioica |
T |
|
+ |
|
Araucaria heterophylla |
T |
E |
+ |
|
Archontophoenix alexandrae |
T |
E |
++ |
|
Artocarpus heterophylla |
T |
E |
+ |
|
Averrhoa carambola |
T |
E |
+ |
|
Bamboo |
H |
|
++ |
|
Bauhinia blakeana |
T |
|
++ |
|
Bauhinia variegata |
T |
|
++ |
|
Bidens pilosa |
H |
|
++ |
|
Bischofia javanica |
T |
|
+ |
|
Bougainvillea glabra |
C |
E |
+ |
|
Breynia fruticosa |
S |
|
+ |
|
Bridelia tomentosa |
T |
|
++ |
|
Calliandra haematocephala |
S |
E |
++ |
|
Caryota ochlandra |
S |
E |
++ |
|
Casuarina equisetifolia |
T |
E |
+++ |
|
Casuarina stricta |
T |
E |
+ |
|
Catharanthus roseus |
S |
E |
+ |
|
Celosia argentea |
H |
|
+ |
|
Celtis sinensis |
T |
|
+++ |
|
Chrysalidocarpus lutescens |
T |
E |
+ |
|
Cinnamomum burmanni |
T |
|
+ |
|
Cinnamomum camphora |
T |
|
+ |
|
Citrus maximum |
T |
E |
+ |
|
Clausena lansium |
T |
E |
+ |
|
Clerodendrum inerme |
S |
|
+ |
|
Clerodendrum viscosum |
S |
E |
+ |
|
Codiaeum variegatum |
S |
E |
+ |
|
Commelina nudiflora |
H |
|
+ |
|
Conyza canadensis |
H |
|
+ |
|
Cordyline terminalis |
H |
E |
+ |
|
Crataeva religiosa |
T |
E |
+ |
|
Cynodon dactylon |
G |
|
+++ |
|
Cyrtococcum patens |
G |
|
+ |
|
Delonix regia |
T |
E |
++ |
|
Desmodium triflorum |
C |
|
++ |
|
Dimocarpus longan |
T |
E |
+++ |
|
Diospyros kaki |
T |
E |
+ |
|
Duranta repens |
S |
E |
+ |
|
Eleusine indica |
G |
|
+ |
|
Eriobotrya japonica |
T |
E |
+ |
|
Eucalyptus citriodora |
T |
E |
++ |
|
Eucalyptus robusta |
T |
E |
+ |
|
Eucalyptus tereticornis |
T |
E |
+ |
|
Euphorbia hirta |
H |
|
+ |
|
Excoecaria cochinchinensis |
S |
E |
+ |
|
Ficus elastica |
T |
E |
++ |
|
Ficus hispida |
T |
|
++ |
|
Ficus microcarpa |
T |
|
+++ |
|
Ficus microcarpa 'Variety" |
T |
E |
+ |
|
Ficus rumphii |
T |
E |
+ |
|
Ficus superba |
T |
|
+ |
|
Ficus variegata |
T |
|
+ |
|
Fimbristylis sp. |
H |
|
+ |
|
Gossampinus malabaricum |
T |
E |
+++ |
|
Grevillea robusta |
T |
E |
+ |
|
Hibiscus spp. |
S |
E |
++ |
|
Hibiscus tiliaceus |
T |
|
++ |
|
Hymenocallis littoralis |
H |
E |
+ |
|
Imperata cylindrica |
G |
|
+ |
|
Ipomoea cairica |
C |
|
++ |
|
Ipomoea sp. |
C |
|
+ |
|
Ixora coccina var. lutea |
S |
E |
+ |
|
Jasminum mesnyi |
S |
E |
+ |
|
Juniperus chinensis |
T |
E |
+ |
|
Kyllinga sp. |
H |
|
+ |
|
Lagerstroemia speciosa |
T |
E |
+ |
|
Lantana camara |
S |
E |
+ |
|
Leucaena leucocephala |
T |
E |
++ |
|
Ligustrum sinensis |
S |
|
+ |
|
Liriope spicata |
H |
|
+ |
|
Litchi chinensis |
T |
E |
+ |
|
Litsea glutinosa |
T |
|
+ |
|
Lophostemon conferta |
T |
E |
++ |
|
Macaranga tanarius |
T |
|
+++ |
|
Mangifera indica |
T |
E |
++ |
|
Manihot esculenta |
H |
E |
+ |
|
Melaleuca quinquenervia |
T |
E |
+++ |
|
Melastoma candidum |
S |
|
+ |
|
Melia azedarach |
T |
E |
++ |
|
Michelia alba |
T |
E |
+ |
|
Mikania micrantha |
C |
E |
+++ |
|
Mimosa pudica |
H |
|
++ |
|
Musa paradisiaca |
H |
E |
+ |
|
Nephrolepis cordifolia |
F |
|
+ |
|
Nerium indicum |
T |
E |
+ |
|
Neyraudia reynaudiana |
G |
|
++ |
|
Oxalis corymbosa |
H |
|
+ |
|
Panicum maximum |
G |
E |
++ |
|
Panicum repens |
G |
|
+ |
|
Peltophorum pterocarpum |
T |
E |
++ |
|
Pennisetum purpureum |
G |
E |
+ |
|
Phoenix roebelenii |
T |
E |
+ |
|
Pinus massoniana |
T |
|
+ |
|
Plumeria rubra |
T |
E |
+ |
|
Praxelis climatidae |
H |
E |
+ |
|
Psidium guajava |
T |
E |
++ |
|
Psychotria serpens |
C |
|
‘+ |
|
Pyrostegia ignea |
C |
E |
+ |
|
Ravenala madagascariensis |
T |
E |
+ |
|
Rhaphiolepis indica |
S |
|
+ |
|
Rhapis excelsa |
H |
|
+ |
|
Rhododendron sp. |
S |
E |
+ |
|
Rhodomyrtus tomentosa |
S |
|
++ |
|
Rhoeo discolor |
H |
E |
+ |
|
Rhus chinensis |
T |
|
+ |
|
Ricinus communis |
S |
E |
+ |
|
Roystonea regia |
T |
E |
+ |
|
Saccharum arundinaceum |
G |
|
+ |
|
Sagetaria theezans |
S |
|
+ |
|
Salix babylonica |
T |
E |
+ |
|
Sansevieria trifasciata |
H |
E |
+ |
|
Sapindus mukorossi |
T |
E |
+ |
|
Sapium sebiferum |
T |
|
+ |
|
Schefflera arboricola |
S |
E |
++ |
|
Scindapsus aureus |
C |
|
+ |
|
Sesbania cochinchinensis |
H |
|
++ |
|
Solanum nigrum |
S |
|
+ |
|
Spathodea campanulata |
T |
E |
+ |
|
Sterculia lanceolata |
T |
|
+ |
|
Syzygium jambos |
T |
E |
+ |
|
Taxodium distichum |
T |
E |
+ |
|
Thevetia peruviana |
T |
E |
+ |
|
Triumfetta bartramia |
S |
|
+ |
|
Uraria crinata |
S |
|
+ |
|
Wedelia triloba |
C |
E |
+ |
Code for Growth Form/Exotic:
T=Tree, S=Shrub, H=Herb, C=Climber, G=Grass; E=Exotic
Code for Relative Abundance:
+++ = common, ++ = occasional, + = scarce
Table D9 Bird species recorded in Sha Po marsh by HKBWS (between 1995 and 1997) and by ERM (in spring 1997)(Carey 1996, 1998; Carey & Tai 1999; ERM 1998)
|
Common name |
Species name |
Commonness & Distribution |
|
White-breasted Waterhen 1 2 |
Amaurornis phoenicurus |
CW |
|
Teal 1 |
Anas crecca |
U |
|
Mallard 1 |
Anas platyrhynchos |
R |
|
Pintail 1 |
Anas acuta |
R |
|
Little Ringed Plover 1 |
Charadrius dubius |
CW |
|
Wood Sandpiper 1 |
Tringa glareola |
U |
|
Common Sandpiper 1 |
Actitis hypoleucos |
CW |
|
Plain Prinia 2 |
Prinia inornata |
U |
|
Yellow-bellied Prinia 2 |
Prinia flaviventris |
CW |
|
Magpie Robin 2 |
Copsychus saularis |
CW |
|
Rufous-backed Shrike 2 |
Lanius schach |
CW |
|
Black-necked Starling 2 |
Sturnus nigricollis |
CW |
|
Crested Myna 2 |
Acridotheres cristatellus |
CW |
|
Red-billed Starling 1 |
Sturnus sericeus |
U |
1 recorded by HKBWS between
1995 and 1997
2 recorded breeding in spring
1997 by ERM
Code for Commonness &
Distribution: CW = common & widespread, U = uncommon & localised, R =
rare & localised.
Table D10 Bird species with conservation value recorded in Meanders A and B near Ko Po Tsuen (Ecosystems Ltd. 2000a, 2000b)
|
Common names |
Species names |
Commonness |
Distribution |
Rarity |
Protection
status |
Meanders |
|
Chinese Pond Heron |
Ardeola bacchus |
C |
Occur in wetland habitats in Hong Kong, East Asia |
Local population declining |
None |
B |
|
Cattle Egret |
Bubulcus ibis |
C |
Occur in wetland habitats in Hong Kong, worldwide |
Local population declining |
None |
B |
|
Grey-headed Lapwing |
Vanellus cinereus |
R |
Found mostly in freshwater wetlands,
East Asia |
Local abundance declining Classified as “near-threatened” by Collar et al. (1994) |
None |
A |
|
Black-eared Kite |
Milvus lineatus |
C |
Occur in a wide range of habitats in Hong Kong, East Eurasia |
Local breeding population declining |
Class 2 Protected Animal of PRC, Appendix 2 of CITES |
A, B |
|
Kestrel |
Falco tinnunculus |
U |
Found in open country, Eurasia and Africa |
|
Class 2 Protected Animal of PRC, Appendix 2 of CITES |
B |
|
Greater Coucal |
Centropus sinensis |
C |
Occur in a wide range of habitats in Hong Kong, Oriental |
Very rare in China |
Class 2 Protected Animal of PRC |
B |
|
Lesser Coucal |
Centropus bengalensis |
U |
Occur in scrub- and tree-covered hillsides, Oriental |
|
Class 2 Protected Animal of PRC |
B |
Code for Commonness: C =
common and widespread, U = uncommon and localized, R = rare and localised
Table D11 Bird
species with conservation value recorded in Channels 60 CD (Contract B) and 43
CD. (Ecosystems Ltd. 2000b)
|
Common name |
Species name |
Commonness |
Distribution |
Rarity |
Protection status |
Channels |
|
Black-faced Spoonbill |
Platalea minor |
R |
Found mostly in the Deep Bay area, East
Asia |
Global population estimated to be about
600 birds in 2000, classified as “critically endangered” by Collar et al. (1994) |
Class 2 Protected Animal of PRC |
60CD |
|
Pheasant-tailed Jacana |
Hydrophasianus chirurgus |
R |
Found in marshes, South Asia |
Locally extinct as a breeding species |
None |
60CD |
|
Grey-headed Lapwing |
Vanellus cinereus |
R |
Found mostly in freshwater wetlands, East Asia |
Local abundance declining Classified as “near-threatened” by Collar et al. (1994) |
None |
43CD |
|
Buzzard |
Buteo buteo |
U |
Occur in a wide range of habitats in Hong Kong, Eurasia and Africa |
|
Class 2 Protected Animal of PRC Appendix 2 of CITES |
60CD |
|
Black-eared Kite |
Milvus lineatus |
C |
Occur in a wide range of habitats in Hong Kong, East Eurasia |
Local breeding population declining |
Class 2 Protected Animal of PRC Appendix 2 of CITES |
60CD |
|
Spotted Munia |
Lonchura punctulata |
U |
Occur almost everywhere except thick woodland, Oriental |
Local abundance declining |
|
43CD |
Code for Commonness: C =
common and widespread, U = uncommon and localised, R = rare and localised
Table D12 Nesting populations at Shui Mei and Au
Tau egretries in the 2000 breeding season (Kwok et al. 2001).
|
|
Little Egrets |
Chinese Pond Herons |
Total nests (% of total nests in Hong Kong) |
|
Au Tau |
21 |
7 |
28, (3.8) |
|
Shui Mei |
1 |
15 |
16, (2.1) |
Table D13 Bird
species and their abundance (no. of birds per ha) recorded in selected habitats
within the Study Area for the present study during April 2000 to March 2001.
|
Common name |
Species name |
Roadside plantation |
Cultivated land |
Fish ponds |
Marsh |
Stream channel |
Woodland |
Commonness |
|
Species recorded within
counting points |
|
|
|
|
|
|
|
|
|
Little Grebe * |
Tachybaptus ruficollis |
- |
- |
0.37 |
0.29 |
- |
- |
CW |
|
Cormorant * |
Phalacrocorax carbo |
- |
- |
0.52 |
- |
- |
- |
U |
|
Chinese Pond Heron * |
Ardeola bacchus |
- |
1.57 |
0.96 |
2.50 |
0.29 |
0.29 |
CW |
|
Little Egret * |
Egretta garzetta |
- |
0.59 |
1.99 |
1.47 |
- |
- |
CW |
|
Cattle Egret * |
Bubulcus ibis |
- |
0.79 |
- |
0.59 |
- |
- |
CW |
|
Intermediate Egret * |
Mesophoyx intermedia |
- |
- |
0.07 |
0.15 |
- |
- |
R |
|
Night Heron * |
Nycticorax nycticorax |
- |
- |
- |
0.59 |
- |
- |
U |
|
Great Egret * |
Casmerodius albus |
- |
- |
0.37 |
0.29 |
- |
- |
U |
|
Grey Heron * |
Ardea cinerea |
- |
- |
0.37 |
0.15 |
- |
- |
U |
|
Buzzard |
Buteo buteo |
- |
- |
0.07 |
0.15 |
- |
- |
U |
|
Black-eared Kite |
Milvus lineatus |
- |
- |
0.22 |
- |
- |
- |
CW |
|
Hobby |
Falco subbuteo |
- |
- |
0.07 |
- |
- |
- |
R |
|
White-breasted Waterhen * |
Amaurornis phoenicurus |
- |
0.79 |
0.29 |
0.59 |
0.44 |
- |
CW |
|
Moorhen * |
Gallinula chloropus |
- |
- |
0.29 |
- |
- |
- |
U |
|
Green Sandpiper * |
Tringa glareola |
- |
- |
0.29 |
0.59 |
- |
- |
CW |
|
Common Sandpiper * |
Actitis hypoleucos |
- |
- |
0.22 |
0.59 |
- |
- |
CW |
|
Little Ringed Plover* |
Charadrius dubius |
- |
- |
0.07 |
0.15 |
- |
- |
CW |
|
Fantail Snipe * |
Gallinago gallinago |
- |
- |
- |
0.74 |
- |
- |
U |
|
Redshank * |
Tringa totanus |
- |
- |
0.88 |
- |
- |
- |
U |
|
Black-headed Gull * |
Larus ridibundus |
- |
- |
1.40 |
- |
- |
- |
CW |
|
Greater Coucal |
Centropus sinensis |
0.29 |
- |
- |
- |
0.15 |
- |
CW |
|
Large Hawk Cuckoo |
Cuculus sparverioides |
0.29 |
- |
- |
- |
- |
0.59 |
CW |
|
Plaintive Cuckoo |
Cacomantis merulinus |
- |
- |
- |
- |
0.15 |
- |
U |
|
Koel |
Eudynamis scolopacea |
0.29 |
- |
0.07 |
- |
0.15 |
0.29 |
CW |
|
Black-capped Kingfisher * |
Halcyon pileata |
- |
- |
- |
0.15 |
- |
- |
U |
|
White-breasted
Kingfisher * |
Halcyon smyrnensis |
- |
- |
0.29 |
- |
- |
0.29 |
CW |
|
Common Kingfisher* |
Alcedo atthis |
- |
- |
0.07 |
- |
- |
- |
CW |
|
House Swift |
Apus nipalensis |
0.59 |
0.39 |
0.22 |
- |
- |
0.29 |
CW |
|
Feral Pigeon |
Columbia livia |
- |
0.20 |
- |
- |
- |
- |
U |
|
Spotted Dove |
Streptopelia chinensis |
- |
1.57 |
0.37 |
0.29 |
0.74 |
1.18 |
CW |
|
Barn Swallow |
Hirundo rustica |
0.29 |
1.18 |
1.10 |
0.44 |
0.59 |
0.29 |
CW |
|
Richard’s Pipit |
Anthus richardi |
- |
- |
0.66 |
- |
- |
- |
CW |
|
Red-throated Pipit |
Anthus cervinus |
- |
0.20 |
0.07 |
- |
- |
- |
U |
|
Olive-backed Pipit |
Anthus hodgsoni |
- |
0.20 |
- |
0.29 |
- |
- |
CW |
|
White Wagtail |
Motacilla alba |
- |
0.39 |
0.74 |
0.44 |
- |
- |
CW |
|
Yellow Wagtail * |
Motacilla flava |
- |
0.59 |
0.22 |
- |
- |
- |
CW |
|
Crested Bulbul |
Pycnonotus jocosus |
0.88 |
1.37 |
0.22 |
0.15 |
2.06 |
2.06 |
CW |
|
Chinese Bulbul |
Pycnonotus sinensis |
0.88 |
1.96 |
0.81 |
1.03 |
2.36 |
3.53 |
CW |
|
Red-vented Bulbul |
Pycnonotus aurigaster |
- |
0.20 |
- |
0.15 |
0.15 |
- |
CW |
|
Siberian Stonechat * |
Saxicola maura |
- |
0.39 |
0.22 |
0.15 |
- |
- |
U |
|
Grey Bushchat |
Saxicola caprata |
- |
0.20 |
- |
- |
- |
- |
|
|
Magpie Robin |
Copsychus saularis |
1.47 |
1.37 |
0.29 |
0.44 |
1.18 |
0.29 |
CW |
|
Siberian Rubythroat |
Luscinia calliope |
- |
0.20 |
- |
- |
- |
- |
U |
|
Blackbird |
Turdus merula |
- |
0.39 |
- |
- |
- |
- |
U |
|
Grey-backed Thrush |
Turdus hortulorum |
- |
0.20 |
- |
- |
- |
- |
U |
|
Asian Brown Flycatcher |
Muscicapa dauurica |
0.29 |
- |
- |
- |
- |
- |
U |
|
Plain Prinia |
Prinia inornata |
0.29 |
0.20 |
1.62 |
1.18 |
- |
- |
U |
|
Yellow-bellied Prinia |
Prinia flaviventris |
0.29 |
0.79 |
1.18 |
2.36 |
1.03 |
0.29 |
CW |
|
Arctic Warbler |
Phylloscopus borealis |
0.29 |
- |
- |
- |
- |
- |
U |
|
Yellow-browed Warbler |
Phylloscopus inornata |
0.29 |
0.39 |
- |
- |
0.15 |
0.29 |
CW |
|
Common Tailorbird |
Orthotomus sutorius |
0.88 |
- |
0.29 |
0.15 |
0.59 |
0.59 |
CW |
|
Dusky Warbler |
Phylloscopus fuscatus |
- |
- |
- |
0.29 |
- |
- |
U |
|
Black-faced Laughingthrush |
Garrulax perspicillatus |
- |
1.57 |
- |
0.44 |
- |
- |
CW |
|
Great Tit |
Parus major |
0.88 |
- |
- |
- |
0.74 |
- |
CW |
|
Rufous-backed Shrike |
Lanius schach |
0.59 |
0.59 |
0.44 |
0.88 |
- |
0.29 |
CW |
|
Japanese White-eye |
Zosterops japonica |
0.88 |
0.98 |
0.15 |
0.15 |
2.50 |
2.94 |
CW |
|
Fork-tailed sunbird |
Aethopyga christinae |
0.29 |
- |
- |
- |
- |
- |
U |
|
Hair-crested Drongo |
Dicrurus hottentottus |
0.29 |
- |
- |
- |
- |
- |
U |
|
Black Drongo |
Dicrurus macrocercus |
- |
- |
0.29 |
0.29 |
0.15 |
- |
CW |
|
Collared Crow |
Corvus torquata |
- |
- |
0.15 |
- |
- |
- |
U |
|
Jungle Crow |
Corvus macrorhynchus |
- |
- |
0.07 |
- |
- |
- |
CW |
|
Magpie |
Pica pica |
- |
0.20 |
0.07 |
0.15 |
- |
1.18 |
CW |
|
Crested Myna |
Acridotheres cristatellus |
0.29 |
1.37 |
0.44 |
1.47 |
0.15 |
0.88 |
CW |
|
Common Myna |
Acridotheres tristis |
- |
0.98 |
- |
0.29 |
0.15 |
- |
R |
|
Black-necked Starling |
Sturnus nigricollis |
- |
1.57 |
1.40 |
0.15 |
0.15 |
0.29 |
CW |
|
Red-billed Starling |
Sturnus sericeus |
- |
- |
8.10 |
- |
- |
- |
U |
|
Tree Sparrow |
Passer montanus |
0.59 |
4.71 |
0.44 |
0.29 |
1.77 |
0.59 |
CW |
|
White-backed Munia |
Lonchura striata |
- |
- |
- |
- |
0.15 |
- |
U |
|
Spotted Munia |
Lonchura punctulata |
- |
- |
- |
0.29 |
2.50 |
- |
U |
|
Masked Bunting |
Emberiza spodocephala |
- |
- |
0.07 |
- |
- |
- |
CW |
|
|
|
|
|
|
|
|
|
|
|
Species recorded outside
counting points |
|
|
|
|
|
|
|
|
|
#Chinese Pond Heron * |
Ardeola bacchus |
|
|
|
|
|
|
CW |
|
#Little Egret * |
Egretta garzetta |
|
|
|
|
|
|
CW |
|
Avocet * |
Recurvirostra avosetta |
|
|
|
|
|
|
R |
|
Black-faced Spoonbill * |
Platalea minor |
|
|
|
|
|
|
R |
|
Imperial Eagle |
Aquila heliaca |
|
|
|
|
|
|
R |
|
#White-breasted
#Waterhen * |
Amaurornis phoenicurus |
|
|
|
|
|
|
CW |
|
#Common Sandpiper* |
Actitis hypoleucos |
|
|
|
|
|
|
CW |
|
#Feral Pigeon |
Columbia livia |
|
|
|
|
|
|
U |
|
#Spotted Dove |
Streptopelia chinensis |
|
|
|
|
|
|
CW |
|
#Barn Swallow |
Hirundo rustica |
|
|
|
|
|
|
CW |
|
#Olive-backed Pipit |
Anthus hodgsoni |
|
|
|
|
|
|
CW |
|
#White Wagtail |
Motacilla alba |
|
|
|
|
|
|
CW |
|
#Crested Bulbul |
Pycnonotus jocosus |
|
|
|
|
|
|
CW |
|
#Chinese Bulbul |
Pycnonotus sinensis |
|
|
|
|
|
|
CW |
|
#Yellow-bellied Prinia |
Prinia flaviventris |
|
|
|
|
|
|
CW |
|
#Yellow-browed Warbler |
Phylloscopus inornata |
|
|
|
|
|
|
CW |
|
#Common Tailorbird |
Orthotomus sutorius |
|
|
|
|
|
|
CW |
|
#Magpie |
Pica pica |
|
|
|
|
|
|
CW |
|
#Tree Sparrow |
Passer montanus |
|
|
|
|
|
|
CW |
Total species = 73
Wetland dependent species are
indicated by *.
Species recorded in and
outside counting points are indicated by #
Code for Commonness &
Distribution: CW
= common and widespread, U = uncommon and localised, R = rare and localised.
Table D14 Bird
species and their abundance recorded within the Study Area during April 2000 to
March 2001.
|
Common name |
Apr 00 |
May 00 |
June 00 |
July 00 |
Aug 00 |
Sept 00 |
Oct 00 |
Nov 00 |
Dec 00 |
Jan 01 |
Feb 01 |
Mar 01 |
|
Little Grebe |
|
1 |
|
1 |
|
|
1 |
|
1 |
|
|
|
|
Cormorant |
|
|
|
|
|
|
|
|
1 |
|
1 |
2 |
|
Chinese Pond Heron |
4 |
5 |
4 |
2 |
2 |
2 |
2 |
5 |
|
8 |
2 |
5 |
|
Little Egret |
1 |
4 |
3 |
1 |
1 |
1 |
3 |
15 |
|
|
8 |
3 |
|
Cattle Egret |
2 |
3 |
3 |
|
|
|
|
|
|
|
|
|
|
Intermediate Egret |
|
2 |
|
|
|
|
|
|
|
|
|
|
|
Night Heron |
|
|
|
2 |
|
2 |
|
|
|
|
|
|
|
Great Egret |
|
1 |
|
2 |
1 |
1 |
2 |
|
|
|
|
|
|
Grey Heron |
|
|
|
|
|
|
1 |
|
1 |
2 |
|
2 |
|
Buzzard |
|
|
|
|
|
|
|
|
1 |
|
|
1 |
|
Black-eared Kite |
|
|
|
|
|
|
|
1 |
|
|
1 |
1 |
|
Hobby |
|
1 |
|
|
|
|
|
|
|
|
|
|
|
White-breasted Waterhen |
2 |
1 |
3 |
2 |
|
1 |
3 |
1 |
2 |
|
|
|
|
Moorhen |
|
|
|
|
|
|
|
3 |
|
1 |
|
|
|
Green Sandpiper |
|
|
|
|
3 |
|
|
|
|
3 |
|
2 |
|
Common Sandpiper |
|
1 |
|
|
1 |
2 |
1 |
2 |
|
|
|
|
|
Little Ringed Plover |
|
|
|
|
|
|
|
|
|
|
|
1 |
|
Fantail Snipe |
2 |
|
|
|
|
|
|
2 |
|
|
|
1 |
|
Redshank |
6 |
|
|
|
|
|
6 |
|
|
|
|
|
|
Black-headed Gull |
|
|
|
|
|
|
|
|
19 |
|
|
|
|
Greater Coucal |
|
|
|
1 |
|
|
|
|
|
|
|
|
|
Large Hawk Cuckoo |
|
1 |
1 |
|
|
|
|
|
|
|
|
|
|
Plaintive Cuckoo |
|
|
1 |
|
|
|
|
|
|
|
|
|
|
Koel |
|
2 |
2 |
|
|
|
|
|
|
|
|
|
|
Black-capped Kingfisher |
|
|
|
1 |
|
|
|
|
|
|
|
|
|
White-breasted Kingfisher |
|
|
|
1 |
2 |
|
|
1 |
|
|
|
1 |
|
Common Kingfisher |
|
|
|
|
|
|
|
|
|
|
|
|
|
House Swift |
|
1 |
|
1 |
|
2 |
4 |
|
|
|
|
|
|
Feral Pigeon |
|
|
|
|
|
|
1 |
|
|
|
|
|
|
Spotted Dove |
2 |
2 |
4 |
4 |
3 |
2 |
|
3 |
|
|
3 |
1 |
|
Barn Swallow |
16 |
3 |
5 |
2 |
2 |
1 |
1 |
|
|
|
|
|
|
Richard’s Pipit |
7 |
1 |
|
|
|
|
|
1 |
|
|
|
|
|
Red-throated Pipit |
2 |
|
|
|
|
|
|
|
|
|
|
|
|
Olive-backed Pipit |
|
|
|
|
|
|
|
3 |
|
|
|
|
|
White Wagtail |
|
|
|
2 |
1 |
3 |
4 |
4 |
|
1 |
|
|
|
Yellow Wagtail |
|
|
|
|
|
|
|
|
|
1 |
4 |
|
|
Crested Bulbul |
|
14 |
2 |
6 |
2 |
1 |
|
2 |
|
4 |
1 |
3 |
|
Chinese Bulbul |
10 |
11 |
1 |
8 |
3 |
1 |
7 |
5 |
5 |
2 |
3 |
3 |
|
Red-vented Bulbul |
|
|
|
1 |
|
1 |
|
1 |
|
|
|
|
|
Siberian Stonechat |
1 |
|
|
|
|
|
1 |
|
1 |
1 |
|
1 |
|
Grey Bushchat |
|
|
|
|
|
|
|
|
|
1 |
|
|
|
Magpie Robin |
4 |
8 |
1 |
3 |
1 |
3 |
|
3 |
3 |
1 |
1 |
|
|
Siberian Rubythroat |
|
|
|
|
|
|
|
|
1 |
|
|
|
|
Blackbird |
|
|
|
|
|
|
|
|
2 |
|
|
|
|
Grey-backed Thrush |
|
|
|
|
|
|
|
|
1 |
|
|
|
|
Asian Brown Flycatcher |
|
|
|
|
|
|
1 |
|
|
|
|
|
|
Plain Prinia |
5 |
5 |
6 |
6 |
2 |
1 |
|
|
|
2 |
2 |
3 |
|
Yellow-bellied Prinia |
3 |
9 |
5 |
4 |
2 |
2 |
4 |
4 |
2 |
2 |
4 |
4 |
|
Arctic Warbler |
|
|
|
|
|
|
1 |
|
|
|
|
|
|
Yellow-browed Warbler |
|
|
|
|
|
|
|
3 |
|
|
2 |
|
|
Common Tailorbird |
|
2 |
1 |
1 |
2 |
5 |
1 |
|
|
2 |
|
|
|
Dusky Warbler |
|
|
|
|
|
|
|
1 |
|
|
1 |
|
|
Black-faced Laughingthrush |
|
|
11 |
|
|
|
|
|
|
|
|
|
|
Great Tit |
1 |
1 |
|
1 |
|
1 |
2 |
|
|
1 |
1 |
|
|
Rufous-backed Shrike |
1 |
1 |
4 |
4 |
2 |
1 |
|
2 |
|
2 |
|
1 |
|
Japanese White-eye |
2 |
3 |
5 |
10 |
2 |
3 |
|
1 |
|
6 |
6 |
|
|
Fork-tailed sunbird |
|
|
|
|
1 |
|
|
|
|
|
|
|
|
Hair-crested Drongo |
|
|
|
1 |
|
|
|
|
|
|
|
|
|
Black Drongo |
|
3 |
|
1 |
2 |
1 |
|
|
|
|
|
|
|
Collared Crow |
|
|
|
|
|
2 |
|
|
|
|
|
|
|
Jungle Crow |
|
|
|
1 |
|
|
|
|
|
|
|
|
|
Magpie |
2 |
1 |
|
1 |
|
|
|
|
3 |
|
|
|
|
Crested Myna |
1 |
2 |
2 |
6 |
|
|
|
|
|
2 |
|
15 |
|
Common Myna |
|
2 |
|
1 |
|
|
|
|
|
|
|
|
|
Black-necked Starling |
5 |
2 |
3 |
1 |
1 |
|
4 |
|
13 |
1 |
|
|
|
Red-billed Starling |
|
|
|
|
|
|
|
|
110 |
|
|
|
|
Tree Sparrow |
8 |
11 |
6 |
5 |
1 |
5 |
|
|
|
|
|
12 |
|
White-backed Munia |
|
|
|
|
|
|
|
1 |
|
|
|
|
|
Spotted Munia |
|
|
|
1 |
|
|
2 |
|
6 |
|
|
10 |
|
Masked Bunting |
|
|
|
|
|
|
|
|
1 |
|
|
|
Table D15 Rare
and conservationally important bird species recorded in the Study Area during April 2000
to March 2001.
|
Species |
Location (refer to Figure 8.4f) |
Commonness |
Distribution |
Rarity (Viney et al. 1996; Yan et al. 1996) |
Protection status * |
|
Black-eared Kite |
Middle of S6 |
C |
Occur in a wide range of habitats in Hong Kong, East Eurasia |
Local breeding population declining |
Class 2 Protected Animal of PRC Appendix 2 of CITES |
|
Buzzard |
Near Lut Chau on S6 and P2 |
U |
Occur in a wide range of habitats in Hong Kong, Eurasia and Africa |
Locally uncommon |
Class 2 Protected Animal of PRC Appendix 2 of CITES |
|
Hobby |
Near Lut Chau on S6 |
R |
Occur in open areas in Hong Kong, Eurasia and Africa |
Locally rare |
Class 2 Protected Animal of PRC Appendix 2 of CITES |
|
Intermediate Egret 1 |
Near |
R |
Deep Bay area in Hong Kong, Asia, Africa and Australasia |
Regionally rare |
|
|
Avocet 1, 2 |
Lut Chau |
R |
Mainly in Deep Bay area, Eurasia and Africa |
Locally |
|
|
Black-faced Spoonbill 1, 2 |
Lut Chau |
R |
Found mostly in the Deep Bay area, East Asia |
Locally rare; Global population estimated to be about 600 birds,
classified as “endangered” by BirdLife International (2000) |
Class 2 Protected Animal of PRC |
|
Imperial Eagle 2 |
Lut Chau |
U |
Northern New Territories, Eurasia and Africa |
Locally uncommon; Classified as “vulnerable” by BirdLife
International (2000) |
Class 1 Protected Animal of PRC Appendix 1 of CITES |
*
All birds in Hong Kong are protected under the Wild Animals Protection
Ordinance (Cap. 170).
Wetland dependent species are
indicated by 1
Species recorded outside
counting points but within the Study Area are indicated by 2
P = pumping station
S = sewer/rising main
Commonness: U = uncommon and
localised, R = rare and localised.
Table D16 Records of birds showing breeding activity within the Study Area during April 2000 to March 2001.
|
Common name |
Location |
Habitat type |
Commonness |
Observation |
|
Common Myna |
S2 |
Cultivated lands |
U |
Recently fledged juveniles |
|
Plain Prinia |
S6 |
Fish ponds |
U |
Recently fledged juveniles |
|
Yellow-bellied Prinia |
S6 |
Fish ponds |
CW |
Recently fledged juveniles |
P = pumping station
S = sewer/rising main
Commonness: CW = common and
widespread, U = uncommon and localised
Table D17 Butterfly species recorded within the Study Area for the present study during April 2000 to March 2001 (11 species recorded).
|
Common name |
Latin name |
Commonness |
Element recorded |
Relative abundance |
|
Blue Spotted Crow |
Euploea midamus |
VC |
P4 |
I |
|
|
|
|
P6 |
I |
|
Great Eggfly |
Hypolimnas bolina |
C |
S2 |
I |
|
|
|
|
S6 |
I |
|
|
|
|
P6 |
I |
|
Peacock Pansy |
Junonia almana |
C |
S6 |
I |
|
Blue Pansy |
Junonia orithya |
UC |
Along S2 |
I |
|
Angled Castor |
Ariadne ariadne |
C |
S2 |
II |
|
|
|
|
P4 |
I |
|
Common Mormon |
Papilio polytes |
VC |
P3 |
I |
|
|
|
|
P4 |
I |
|
|
|
|
P6 |
I |
|
Common Bluebottle |
Graphium sarpedon |
VC |
S6 |
I |
|
|
|
|
P4 |
I |
|
Great Orange Tip |
Hebomoia glaucippe |
C |
P4 |
I |
|
Common White |
Artogeia canidia |
VC |
P2 |
I |
|
|
|
|
P3 |
I |
|
|
|
|
P5 |
I |
|
|
|
|
P6 |
I |
|
|
|
|
S2 |
II |
|
Common Yellow |
Eurema hecabe |
VC |
S6 |
I |
|
|
|
|
S2 |
II |
|
|
|
|
P2 |
I |
|
|
|
|
P3 |
I |
|
|
|
|
P4 |
I |
|
|
|
|
P6 |
I |
|
Common Black Jezebel |
Delias pasithoe |
C |
S2 |
II |
|
|
|
|
P4 |
I |
|
|
|
|
P6 |
I |
Commonness: C = common, VC = very common
(Walthew 1997)
P = pumping station
S = sewer/rising main
Relative abundance: I =
1-10 individuals
II
= 11-30 individuals
Table D18 Dragonfly species recorded within the Study Area by Wilson (1997) and by the present study during April 2000 to March 2001 (12 species recorded).
|
|
Species |
Commonness |
Recording Location |
Relative abundance |
|
Wilson 1997 |
Epopthalmia elegans |
FC, W |
Au Tau |
|
|
|
Crocothemis servilia |
C, W |
Au Tau |
|
|
|
Tholymis tillarga |
C, W |
Au Tau |
|
|
|
Zyxomma petiolatum |
FC, W |
Au Tau |
|
|
|
Brachydiplax chalybea* |
C, W |
Au Tau |
|
|
The present study |
Ischnura senegalensis |
A, W |
P4 |
I |
|
|
|
|
P2 |
I |
|
|
|
|
P6 |
I |
|
|
|
|
S2 |
I |
|
|
|
|
S6 |
I |
|
|
Ictinogomphus pertinax |
FC, W |
S6 |
I |
|
|
Brachythemis contaminata |
A, W |
P4 |
I |
|
|
|
|
P6 |
I |
|
|
|
|
S2 |
I |
|
|
Orthetrum glaucum |
A, W |
P4 |
I |
|
|
Orthetrum chrysis |
C, W |
P5 |
I |
|
|
Orthetrum pruinosum |
A, W |
P4 |
I |
|
|
Orthetrum sabina |
A, W |
P4 |
I |
|
|
|
|
P5 |
I |
|
|
|
|
P6 |
I |
|
|
|
|
S2 |
I |
|
|
|
|
S6 |
I |
|
|
Rhyothemis variegata |
C, W |
P2 |
I |
|
|
|
|
P4 |
I |
|
|
|
|
P5 |
I |
|
|
|
|
P6 |
I |
|
|
|
|
S6 |
I |
|
|
Trithemis aurora |
A, W |
P4 |
I |
|
|
Neurothemis fulvia |
FC, W |
S6 |
I |
|
|
Pantala flavescens |
A, W |
S6 |
II |
|
|
|
|
P2 |
I |
|
|
|
|
P5 |
|
|
|
|
|
P6 |
I |
|
|
|
|
S2 |
I |
|
|
Tramea virginia |
C, W |
P2 |
I |
|
|
|
|
P5 |
I |
|
|
|
|
P6 |
I |
|
|
|
|
S6 |
I |
* recorded by both Wilson
(1997) and the present study
Commonness: A = abundant, C =
common, FC = fairly common, W = widespread (Wilson 1997)
P = pumping station
S = sewer/rising main
Relative abundance: I =
1-10 individuals
II
= 11-30 individuals
Table D19 Mammals recorded within the Study Area between 1992 and 1996 (Reels 1996; Babtie 1996) and during the present study (April 2000 to March 2001).
|
|
Common name |
Species name |
Location within the Study Area |
Distribution in Hong Kong |
Protection status |
|
1992 - 1996 |
Javan Mongoose 1 |
Herpestes javanicus |
Fishponds near S6 |
Widely recorded in lowland northwest New Territories |
WAPO |
|
|
Common Otter 1 |
Lutra lutra |
Fishponds near S6 |
Rare and restricted to the wetlands of the Deep Bay area |
WAPO, Class 2 Protected Animal of PRC, Appendix 1 of CITES |
|
|
Chinese Pangolin 1 |
Manis pentadactyla |
Hillside near P1 |
A few records in the central New Territories |
WAPO, Class 2 Protected Animal of PRC, Appendix 2 of CITES |
|
|
Chinese Leopard Cat 1 |
Prionailurus bengalensis |
Hillside near P1 |
Widely distributed across the northwest, central and northeast New
Territories |
WAPO, Class 2 Protected Animal of PRC, Appendix 2 of CITES |
|
|
Japanese Pipistrelle 2 |
Pipistrellus abramus |
Fishponds, streams and marshes between Tung Shing Lei and Kam Hing
Wai |
Widely distributed in Hong Kong |
WAPO |
|
|
Noctule Bat 2 |
Nyctalus noctula |
Fishponds, streams and marshes between Tung Shing Lei and Kam Hing
Wai |
Uncertain, only a few specimens are collected in Hong Kong |
WAPO |
|
|
|
|
|
|
|
|
The present study |
Japanese Pipistrelle |
Pipistrellus abramus |
S6 |
Widely distributed in Hong Kong |
WAPO |
1 Reels (1996)
2 Babtie BMT Hong
Kong Ltd (1996)
Distribution in Hong Kong:
Reels (1996)
Protection status: Wang
(1998)
Table D20 Amphibian species reported within the Study Area by Lau and Dudgeon (1999).
|
Common name |
Species name |
Locations within the Study
Area |
Distribution |
Commonness |
|
Asian Common Toad |
Bufo melanostictus |
Au Tau |
Occur all over the New Territories. from central to southeast Asia |
C, W |
|
Gunther’s Frog |
Rana guentheri |
Au Tau |
Very widespread in Hong Kong, Widely distributed in southern China to southeast Asia |
C, W |
|
Chinese Bullfrog |
Rana rugulosa |
Au Tau |
Occur throughout the New Territories, Central China to Southeast Asia
|
U, W |
Distribution: Lau and Dudgeon
(1999)
Commonness: C = common, U =
uncommon, L = localised, W = widespread (Lau and Dudgeon 1999)
Table D21 Amphibian species recorded within the Study Area for the present study during April 2000 to March 2001.
|
Common name |
Species name |
Distribution in Hong Kong |
Element recorded |
|
|
|
Asian Common Toad |
Bufo melanostictus |
Common and occur all over the New Territories |
S2, P6 |
|||
|
Gunther’s Frog |
Rana guentheri |
Very widespread in Hong Kong |
S1, S6, P5 |
|||
|
Brown Tree Frog |
Polypedates megacehalus |
Very widespread in Hong Kong |
S6 |
|||
Distribution in Hong Kong
(Lau and Dudgeon 1999)
P = pumping station
S = sewer/rising main
Table D22 Reptile species recorded within the Study Area by the present study.
|
Common name |
Species name |
Distribution in Hong Kong |
Element recorded |
|
|
Changeable Lizard |
Calotes versicolor |
Common and occurs in many types of habitats, except in dense forest
and mountain grasslands |
S6 |
||
|
Red-necked Keelback |
Rhabdophis subminiatus |
Common and widespread, usually found in forested or shrubby hills and
near water |
P4 |
||
Distribution in Hong Kong
(Karsen et al. 1998)
P = pumping station
S = sewer/rising main
Table D23
Results of the channel survey for the present study during April 2000 to March
2001.
|
|
Wet
season survey |
Dry
Season survey |
||||||
|
Sampling
locations & replicates |
Common
name |
Scientific
name |
Weight |
Length |
Common
name |
Scientific
name |
Weight |
Length |
|
1 |
|
|
|
|
|
|
|
|
|
a |
Tilapia |
Oreochromis
sp. |
350 |
214 |
Tilapia |
Oreochromis
sp. |
136 |
120 |
|
|
Tilapia |
Oreochromis
sp. |
125 |
113 |
Tilapia |
Oreochromis
sp. |
145 |
131 |
|
|
|
|
|
|
Tilapia |
Oreochromis
sp. |
155 |
129 |
|
|
|
|
|
|
Tilapia |
Oreochromis
sp. |
320 |
201 |
|
|
|
|
|
|
Mullet |
Mugil
affinis |
210 |
265 |
|
b |
Tilapia |
Oreochromis
sp. |
410 |
215 |
Tilapia |
Oreochromis
sp. |
310 |
195 |
|
|
Tilapia |
Oreochromis
sp. |
270 |
186 |
Tilapia |
Oreochromis
sp. |
300 |
190 |
|
|
Tilapia |
Oreochromis
sp. |
180 |
175 |
Tilapia |
Oreochromis
sp. |
250 |
173 |
|
|
Tilapia |
Oreochromis
sp. |
150 |
133 |
Tilapia |
Oreochromis
sp. |
210 |
164 |
|
|
Mud carp |
Cirrhinus
molitorella |
400 |
268 |
|
|
|
|
|
|
Mullet |
Mugil
affinis |
100 |
166 |
|
|
|
|
|
c |
Tilapia |
Oreochromis
sp. |
400 |
218 |
Tilapia |
Oreochromis
sp. |
340 |
221 |
|
|
Tilapia |
Oreochromis
sp. |
250 |
173 |
Tilapia |
Oreochromis
sp. |
275 |
184 |
|
|
Tilapia |
Oreochromis
sp. |
125 |
195 |
Tilapia |
Oreochromis
sp. |
135 |
177 |
|
|
Tilapia |
Oreochromis
sp. |
180 |
156 |
Mullet |
Mugil
affinis |
125 |
193 |
|
|
Tilapia |
Oreochromis
sp. |
120 |
137 |
|
|
|
|
|
2 |
|
|
|
|
|
|
|
|
|
a |
Tilapia |
Oreochromis
sp. |
300 |
193 |
Mud crab |
Scylla
serrata |
|
55 |
|
|
Mud crab |
Scylla
serrata |
|
43 |
|
|
|
|
|
b |
- |
- |
- |
- |
Tilapia |
Oreochromis
sp. |
240 |
162 |
|
|
|
|
|
|
Tilapia |
Oreochromis
sp. |
210 |
142 |
|
c |
- |
- |
- |
- |
Tilapia |
Oreochromis
sp. |
120 |
121 |
|
|
|
|
|
|
Mud crab |
Scylla
serrata |
|
64 |
|
3 |
|
|
|
|
|
|
|
|
|
a |
Tilapia |
Oreochromis
sp. |
460 |
224 |
Tilapia |
Oreochromis
sp. |
405 |
214 |
|
|
|
|
|
|
Tilapia |
Oreochromis
sp. |
145 |
133 |
|
|
|
|
|
|
Tilapia |
Oreochromis
sp. |
110 |
102 |
|
b |
Tilapia |
Oreochromis
sp. |
420 |
206 |
Tilapia |
Oreochromis
sp. |
355 |
186 |
|
|
Tilapia |
Oreochromis
sp. |
410 |
223 |
|
|
|
|
|
|
Tilapia |
Oreochromis
sp. |
210 |
165 |
|
|
|
|
|
c |
- |
- |
- |
- |
Tilapia |
Oreochromis
sp. |
135 |
155 |
Table D24 Plant species recorded within and near to the proposed pumping stations P1 to P7
|
1.
1. Species |
Habit |
Exotic |
Location |
||||||
|
|
|
|
P1 |
P2 |
P3 |
P4 |
P5 |
P6 |
P7 |
|
Alocasia macrorrhiza |
H |
|
|
+ |
|
|
+ |
+ |
+ |
|
Alternanthera
sessilis |
H |
|
|
|
|
|
|
+ |
|
|
Amaranthus
viridus |
H |
|
|
+ |
|
+ |
|
+ |
+ |
|
Bambusa
vulgaris var. striata |
G |
Exotic |
|
|
|
|
+ |
|
|
|
Bauhinia
variegata |
T |
|
|
|
|
|
|
|
+ |
|
Bidens pilosa |
H |
|
+ |
+ |
+ |
|
|
+ |
+ |
|
Bridelia
tomentosa |
T |
|
|
|
|
|
|
|
+ |
|
Calliandra
haematocephala |
S |
Exotic |
|
|
|
+ |
|
|
|
|
Casuarina
stricta |
T |
Exotic |
|
|
+ |
|
|
|
|
|
Celtis sinensis |
T |
|
+ |
|
|
|
+ |
+ |
+ |
|
Chrisalidocarpus
lutescens |
T |
Exotic |
|
|
|
+ |
+ |
|
|
|
Clausena
lansium |
T |
|
|
|
|
|
|
|
+ |
|
Clerodendrum
viscosum |
S |
Exotic |
|
+ |
|
|
|
|
|
|
Conyza
canadensis |
H |
Exotic |
+ |
|
|
|
|
+ |
|
|
Cuscuta
japonica |
C |
|
|
|
|
|
|
|
|
|
Cyclosorus
interruptus |
F |
|
|
+ |
|
|
|
|
|
|
Cynodon
dactylon |
G |
|
|
+ |
+ |
|
|
|
|
|
Dimocarpus
longan |
T |
Exotic |
|
|
|
|
+ |
+ |
+ |
|
Eclipta
prostrata |
H |
|
|
|
+ |
|
|
|
|
|
Eleusine indica |
G |
|
|
+ |
|
|
|
|
|
|
Ficus elastica |
T |
Exotic |
|
+ |
|
|
|
|
|
|
Ficus hispida |
T |
|
|
|
|
+ |
|
|
|
|
Ficus
microcarpa |
T |
|
|
|
|
+ |
|
|
+ |
|
Fimbristylis
sp. |
H |
|
+ |
|
|
|
|
|
|
|
Gossapinus
malabaricum |
T |
Exotic |
+ |
|
|
|
|
|
|
|
Hibiscus sp. |
T |
Exotic |
|
|
|
+ |
|
|
|
|
Imperata
cylindrica |
G |
|
+ |
|
|
|
|
|
|
|
Ipomoea cairica |
C |
Exotic |
|
+ |
|
+ |
|
+ |
|
|
Ipomoea sp. |
C |
Exotic |
|
|
+ |
|
|
|
|
|
Lantana camara |
S |
Exotic |
|
+ |
|
|
|
|
+ |
|
Leucaena leucocephala |
T |
Exotic |
+ |
|
|
|
|
|
|
|
Litsea
glutinosa |
T |
|
|
|
|
|
|
|
+ |
|
Macaranga
tanarius |
T |
|
|
+ |
|
|
+ |
|
+ |
|
Melaleuca
quinquinervia |
T |
Exotic |
|
|
|
|
|
|
+ |
|
Melia azedarach |
T |
Exotic |
|
|
+ |
+ |
|
|
|
|
Mikania
micrantha |
C |
Exotic |
|
+ |
|
|
|
|
+ |
|
Mimosa pudica |
H |
|
+ |
|
+ |
|
|
|
|
|
Musa
paradisiaca |
T |
|
|
|
|
|
|
|
+ |
|
Panicum maximum |
G |
Exotic |
|
|
|
|
|
|
+ |
|
Paspalum
conjugatum |
G |
|
|
+ |
|
|
|
+ |
|
|
Polygonum
hydropiper |
H |
|
|
|
|
|
|
+ |
|
|
Polygonum
perfoliatum |
H |
|
|
|
|
|
|
+ |
|
|
Praxelis
clematidea |
H |
Exotic |
+ |
|
+ |
|
|
|
|
|
Ricinus
communis |
S |
Exotic |
|
|
|
|
|
+ |
+ |
|
Sansevieria trifasciata |
H |
Exotic |
|
|
|
|
|
|
+ |
|
Sapium
sebiferum |
T |
|
|
|
|
|
|
+ |
|
|
Schefflera
arboricola |
S |
Exotic |
|
|
|
|
+ |
|
|
|
Sesbania
cochinchinensis |
S |
Exotic |
+ |
|
+ |
|
|
|
|
|
Solanum nigrum |
H |
|
|
|
|
+ |
|
|
|
|
Triumfetta
bartramia |
S |
|
|
+ |
|
|
|
|
|
|
Wedelia triloba |
C |
Exotic |
|
|
|
+ |
|
|
|
G = grass, H = herb, S =
shrub, T = tree, C = cultivated species, + = present
Table D25 Bird species recorded in the proposed pumping station sites. (Wetland dependent species are indicated by "*").
|
Common name |
Latin name |
P1 |
P2 |
P3 |
P4 |
P5 |
P6 |
P7 |
Commonness &
Distribution |
|
|||||||||
|
Little Egret * |
Egretta garzetta |
|
|
+ |
|
|
|
|
CW |
||||||||||
|
Spotted Dove |
Streptopelia chinensis |
|
|
+ |
|
|
|
+ |
CW |
||||||||||
|
Crested Bulbul |
Pycnonotus jocosus |
+ |
|
|
|
|
|
+ |
CW |
||||||||||
|
Chinese Bulbul |
Pycnonotus sinenisi |
|
+ |
|
|
+ |
|
+ |
CW |
||||||||||
|
Yellow-bellied Prinia |
Prinia flaviventris |
|
|
|
|
|
|
|
CW |
||||||||||
|
Common Tailorbird |
Orthotomus sutorius |
|
|
|
|
|
+ |
|
CW |
||||||||||
|
Crested Myna |
Acridotheres cristatellus |
|
|
|
+ |
|
+ |
|
CW |
||||||||||
|
Black-necked Starling |
Sturnus nigricollis |
|
|
|
+ |
|
|
|
CW |
||||||||||
|
Tree Sparrow |
Passer montanus |
+ |
|
|
|
+ |
|
|
CW |
||||||||||
Commonness &
Distribution: CW =
common and widespread.