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ISSN 0374-7859
THE GARDENS’ BULLETIN
SINGAPORE
Volume 41
(1988)
A periodical reflecting the interests and
activities of the Botanic Gardens
Singapore
Published by the Botanic Gardens
Parks and Recreation Department
Ministry of National Development
Cluny Road, Singapore 1025
— 3 Tha. oh
J
CONTENTS
Volume 41
PART 1 — Ist June 1988
KIEW, R. and WEBER, A.:
Two New Species (Didissandra porphyrantha and Didymocarpus
nitidus) and a New Combination (Didymocarpus breviflorus),
meemncniocede. Irom sclatigor, Malaysia... cace fl iwce- 2 Ms nccs.cscecsleccccasscccver
LEE, S.K. and RAO, A.N.:
Plantlet Production of Swietenia macrophylla King
MP REISE OOP TE IEIING 1 oe Se ta oc ctn oo vn k cine dV RE Ue Be awa ep ven bye ddd cones
FOONG, THAI WU and YANG, CHENG NOI:
Compound Fertilizer Requirements for the Establishment and
Early Growth of Popular Ornamental Shrubs between
ee RT I se cen ww sul fea Lavinais Sogatceee pean ate wweke wus «wks ode
PART 2 — Ist December 1988
VERMEULEN, J.J. and LAMB, A.:
Six New Species of Bulbophyllum Sect. Monilibulbus (Orchidaceae)
EE ee
Three New Taxa in Elaeocarpus in the Malay Peninsula ......................
BIDIN, Aziz, JAMAN, RAZALI and SALLEH, MAT KAMARUDDIN:
A New Species of Adiantum from Trus Madi Range, Sabah .................
FERNANDO, EDwINo S::
Four New Taxa of Philippine Rattans (Palmae: Calamoideae) ..............
SWAN, FREDERICK R. JR.:
Tree Distribution Patterns in the
Sete MAM TIALUEC ROESETVE, SINGAPOTC, 6.0.45 .<cocce chest sedan nasceccncacesscases
WONG, K.M., WONG, Y.S. and SAW, L.G::
Notes on the Early Exploration and Botanical Collecting
in the Endau-Rompin Area of Peninsula Malaysia ...............ccceeceeeeeeees
BIDIN, Aziz:
A Further Chromosome Count for Osmunda (Osmundales)
ANTI ARIE SI So, Dias tvkcadaduneveduscrdedeacececcsve
Book Review
CORNER, E.J.H.::
IE UR gos oo soc. sey uacdu crocs don cies sveseancuacevansesecsases
Pages
11-18
29-28
29-41
43-44
45-48
49-58
59-81
83-91
93-94
95
97-98
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INDEX
Volume 41
Page numbers in italics indicate the presence of illustrations.
Acacia auriculiformis, 19
Actinodaphne malaccensis, 71, 80
Adenanthera bicolor, 65, 66, 80
Adiantum, 45
caudatum, 47
diaphanum, 47
hispidulum, 47
lamrianum, 45, 46
Aglaonema pseudobracteatum, 20, 21, 23
Anisoptera megistocarpa, 70, 71, 79
Aporusa benthamiana, 66, 70, 79
microstachya, 71, 79
symplocoides, 67, 69, 79
Archidendron sp., 71, 80
Ardisia colorata, 71, 74, 81
teysmanniana, 68, 69, 70, 72, 74, 81
Artocarpus lanceifolius, 65, 80
lowii, 65, 80
rigidus, 66, 80
Aziz Bidin, 45, 93
Baccaurea parviflora, 68, 70, 79
Blumeodendron tokbrai, 67, 69, 80
Buchanania sessilifolia, 68, 70, 79
Bulbophyllum kestron, 29, 30, 31, 32
leproglossum, 29, 30, 31, 33, 34
nubinatum, 29, 30, 34, 35
ovalifolium, 30, 31, 34, 37
pelicanopsis, 29, 30, 34, 36
perductum, 30
phaeoneuron, 37
scabrum, 29, 30, 37, 38
sect. Monilibulbus, 29
thymophorum, 29, 30, 38, 39
tortuosum, 30
Calamus aidae, 49, 50, 51
balerensis, 49, 51, 52, 53
bicolor, 51
discolor, 51
inops, 51
ornatus var. pulverulentus, 49, 53, 54, 55
ornatus, 55
ornatus var. philippinensis, 55
sp., 64
usitatus, 53
Calamus-Daemonorops, 67, 68, 81
Callosciurus notatus, 61
Calophyllum ferrugineum, 65, 71, 80
tetrapterum, 68, 70, 80
Canarium sp., 69, 79
Castanopsis lucida, 65, 80
Cnestis platantha, 71, 79
Corner, E.J.H., 95
Crypteronia cumingii, 66, 80
Cyathocalyx remuliflorus, 66, 68, 70, 79
Cynocephalus variegatus, 61
Dacryodes rostrata, 67, 69, 79
sp., 66, 79
Daemonorops polita, 49, 56, 57, 58
ruptilis var. accaulescens, 58
ruptilis var. ruptilis, 58
sp., 64
Dalbergia parviflora, 65, 80
Dehaasia sp., 69, 80
Dicrurus paradiseus, 61
Didissandra breviflora, 7, 9
porphyrantha, 1, 2, 3, 4, 6
Didymocarpus atrocyanea, 4
atropurpurea, 4
breviflorus, 1, 6, 7, 8, 9
cf. albinus, 1
hirta, 4
longisepala, 4
malayanus, 1, 7
morgani, 4
nitidus, 1, 4, 5, 6
petiolata, 4
platypus, 1, 7
serratifolius, 6, 8, 9
violaceae, 4
Dillenia grandifolia, 66, 79
Dipterocarpus penangianus, 65, 67, 69, 79
Dracaena surculosa punctulata, 20, 22
Dyera costulata, 68, 70, 72, 79
Elaeocarpus, 43
nitidus var. velutinus, 43, 44
sallehiana, 43
symingtonii, 43
Endau-Rompin Area, 83
Eugenia densiflora, 65, 81
duthieana, 64, 66, 68, 70, 84, 81
longiflora, 65, 71, 74, 81
Euodia glabra, 66, 81
Fernando, Edwino S., 49
Foong Thai Wu, 19
Gaertnera grisea, 71, 81
Ganua kingiana, 67, 68, 69, 70, 81
Garcinia griffithii, 66, 71, 80
Gironniera parvifolia, 64, 65, 66, 67, 68, 69, 70,
72, 81
Gluta wallichii, 65, 66, 68, 70, 79
Glycosmis chlorosperma, 68, 70, 81
Gomphandra quadrifida, 70, 81
Gonystylus confusus, 68, 70, 80
Gynotroches axillaris, 68, 70, 81
of
98
Hopea mengarawan, 67, 69, 71, 79
Horsfieldia sp., 69, 80
Ixonanthes icosandra, 64, 65, 66, 72, 80
Ixora javanica, 20, 27
Kamaruddin Mat Salleh, 45
Kiew, R., 1
Knema laurina, 66, 67, 68, 69, 70, 72, 80
sp., 80
Koilodepas wallichianum, 67, 68, 69, 70, 80
Lamb, A., 29
Bees ok, 14
Licania splendens, 65, 81
Liptopteris, 93
Litsea accedens, 70, 80
_ castanea, 65, 80
Macaca fasicularis, 61
Macaranga triloba, 65, 67, 69, 70, 72 80
Medusanthera affinis, 69, 81
Meiogyne virgata, 65, 79
Memecylon megacarpum, 66, 71, 80
Microcos blattaefolia, 71, 81
Myristica cinnamomea, 65, 67, 68, 69, 70, 80
Ng, F.S.P., 43
Oncosperma, 64
horridum, 64, 65, 67, 69, 81
Osmunda, 93
javanica, 93, 94
vachellii, 93, 94
Palaquium microphyllum, 71, 81
Parishia sp., 71, 79
Parkia speciosa, 71, 80
Payena lucida, 71, 81
Pellacalyx saccardianus, 65, 67, 69, 81
Pentaca triptera, 72, 81
Pertusadina eurhyncha, 65, 81
Phaeanthus ophthalmicus, 68, 70, 79
Philodendron selloum, 20, 25
Phyllanthus watsonii, 85
Pimeleodendron griffithianum, 59, 68, 70, 73, 80
Planchonella maingayi, 66, 71, 81
Gard. Bull. Sing. 41 (1988)
Polyalthia angustissima, 65, 71, 79
sp., 67; 79
sumatrana, 71, 79
Polyscias filicifolia, 20, 21, 24
Popowia fusca, 68, 70, 79
Prunus polystachya, 71, 81
Ptychosperma macarthurii, 20, 21, 26
Randia densiflora, 71, 81
Rao, A.N., 11
Razali Jaman, 45
Samanea saman, 19
Santiria apiculata, 64, 65, 67, 68, 69, 70, 79
griffithii, 66, 79
laevigata, 68, 70, 72, 79
sp., 65
Saw, L.G., 83
Scorodocarpus borneensis, 66, 81
Shorea curtisil, 59, 62, 64, 65, 66, 67, 68, 69, 70,
42, 33, Fo
gratissima, 66, 79
macroptera, 65, 71, 79
parvifolia, 66, 79
Streblus elongatus, 67, 69, 80
Strombosia ceylanica, 66, 68, 70, 81
Swan, Frederick R., JR., 59
Swietenia macrophylla, 11
Tabernaemontana peduncularis, 65, 67, 69, 79
Tan Wee Kiat, 95
Todea, 93
Urophyllum, 74
glabrum, 67, 69, 81
hirsutum, 64, 67, 68, 69, 70, 72, 74, 81
streptopodium, 67, 69, 74, 81
Vermeulen, J.J., 29
Weber, A., |
Wong, K.M., 83
Wong, Y.S., 83
Xanthophyllum eurhynchum, 69, 81
Xylopia malayana, 66, 79
Yang Cheng Noi, 19
Fores ine sararer
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ISSN 0374-7859
~ EER EERO IEE DIEPPE
M© ‘
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THE GARDENS’ BULLETIN
SINGAPORE
VOL. 41 (Part 1) 1 June 1988
\
a
CONTENTS
. KIEW, R and WEBER, A.:
a Two New Species (Didissandra porphyrantha and Didymocarpus
nitidus) and a New Combination (Didymocarpus breviflorus),
See eae. FTO) Selangor, MALAYSIA. 6.56.5. cdencadece ane obidbewtivacedsacsecsceces
_ LEE, S.K. and RAO, A.N.:
Plantlet Production of Swietenia macrophylla King
a RENT UA Sg go dc) aa ca Re cceacs dbs vaek's tie cds Ges neve dptences
_ FOONG, THAI Wu and YANG, CHENG NOI:
1 Compound Fertilizer Requirements for the Establishment and
Early Growth of Popular Ornamental Shrubs between
a LER LIE yl a 21.) Sea” ak Page PB d sr, 5 “wisn av'vcwladed <ocvacesncccces
Published by the Botanic Gardens
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THE GARDENS’ BULLETIN
VOL. 41 (Part 1)
SINGAPORE
CONTENTS
KIEW, R and WEBER, A.:
Two New Species (Didissandra porphyrantha and Didymocarpus
nitidus) and a New Combination (Didymocarpus breviflorus),
SeMeeeeoese, ATOMS SClINPOT, Widlaysia. =). 2226. occcoi secs sts vawleecescetickccecocecs
LEE, S.K. and RAO, A.N.:
Plantlet Production of Swietenia macrophylla King
Pn SMES IN a NG oa a! 6d sc thw uns wSon akc detddos sucimavececmertsccds
FOONG, THAI WU and YANG, CHENG NOI:
Compound Fertilizer Requirements for the Establishment and
Early Growth of Popular Ornamental Shrubs between
Road-side Trees
SSS HTS EEE HE ESTEE SES SEE HEHEHE EHEE HEHEHE ESTHET HEHEHE EEHE EEE HEHEHE EEE HEHEHE EE EEEEEEE
Published by the Botanic Gardens
Parks and Recreation Department
Ministry of National Development
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av
June 1988
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19-28
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Two New Species (Didissandra porphyrantha and
Didymocarpus nitidus) and a New Combination
(Didymocarpus breviflorus), Gesneriaceae,
from Selangor, Malaysia
R. KIEW' and A. WEBER?
‘Department of Biology, Universiti Pertanian Malaysia, 43400
Serdang, Selangor, Malaysia
Institute of Botany, University of Vienna, Vienna, Austria
EFFECTIVE PUBLICATION DATE: 23 SEPT. 1988
Abstract
Two new species of Gesneriaceae, Didissandra porphyrantha (Section Speciosae) and Didymocarpus
nitidus are described and illustrated. A new combination, Didymocarpus breviflorus, is made for a species
previously included in Didissandra.
Introduction
During the course of field work in Selangor, one of us (RK) located populations
of several interesting species of Gesneriaceae. Two of these, on further investigation,
were found to be new species, Didissandra porphyrantha and Didymocarpus nitidus,
and another, Didissandra breviflorus Ridl., with the collection of flowering material,
proved to be a species of Didymocarpus.
The new Didissandra species is particularly striking with large violet-purple flowers
with an almost black limb, and so earns the epithet porphyrantha. It is a handsome
plant worthy of cultivation. The new Didymocarpus species is notable for its shiny,
rather fleshy leaves and is therefore called D. nitidus. Its flowers are white and are
rather small. This species seems to flower rather rarely and is usually encountered
sterile.
Both Didissandra porphyrantha and Didymocarpus nitidus are found in montane
forest on a steep slope east of the summit of Gunung Bunga Buah where they grow
in a richly developed herb layer, which includes other species of Gesneriaceae such
as Didymocarpus cf. albinus, D. malayanus and D. platypus (a form with purplish
corolla lobes illustrated by Kiew, 1982). Didymocarpus nitidus is as yet known only
from this locality but Didissandra porphyrantha has been found lower down the
Gombak valley. As yet Didymocarpus breviflorus is only known from Selangor from
several places in the Gombak valley as well as from Genting Peras.
Didissandra porphyrantha A. Weber & R. Kiew, sp. nov. Figi*t;: 2.
Planta lignosa, 20-50 cm alta. Caulis simplex vel ramosus, in parte inferiore decumbens et radicatus.
Folia in apice caulis laxe aggregata, per internodia c. 2 cm longa et pilis rubro-brunneis obsita separata,
Opposita; petiolus 2-3 cm longus, e pilis rubro-brunneis villosus; lamina 10-20 x 3-6 cm, oblanceolata,
partim subfalcata, apice acuminato, basi attenuata, margine grosse serrato-crenato (dentes 1.5 mm longi,
l
2 Gard. Bull. Sing. 41(1) (1988)
Fig. 1. Didissandra porphyrantha. a,b flower; c fruiting specimen. (Photo. A. Weber)
c. 1 cm distantes); pagina superior glabra (in foliis juvenilibus glandulis minutissimis 2-cellularibus
obsita), pagina inferior in nervis laxe villosus. Pedunculi axillares, 5-8 cm longi, subglabri, 1-2 flori; bracteae
2, lanceolatae; pedicellus 1-1.5 cm. Sepala 5, anguste triangularia, in dimidio inferiore connata, subglabra.
Corolla c. 5 cm longa, infundibuliformis, basin versus anguste cylindrica; tubus extra glaber, violaceus,
intus atro-violaceus, lineis albis longitudinalibus 8 ornatus; limbus atro-violaceus, fere ater. Stamina 4,
didynamia, per paribus cohaerentes. Discus cylindricus, brevis, 5-lobatus. Ovarium cylindricum, basin
versus angustatum; stylus brevis; stigma unilabiatum, planum, triangulare vel reverse cordatum. Fructus
capsularis, elongato-linearis, carnoso-cartilagineus, 6-8 cm longus, leviter curvatus, in latere superiore
rima longitudinali dehiscens. Semina numerosa, parva, atrobrunnea, elliptica vel late fusiformia, striata.
Two New Species and a New Combination of Gesneriaceae 3
Fig. 2. Didissandra porphyrantha. a,b. glands on juvenile leaf; c. seed; d. testa surface enlarged.
SEM-micrographs bar: a,c. 100um; b,d. 10um.
Type: Peninsular Malaysia, Selangor, Gunung Bunga Buah, on ridge east of summit, 1300-1400m, Weber
& Anthonysamy 840711-1/3 (WU; iso E, K, KLU, L, WU, UPM).
Woody plant, 20-50 cm tall. Stem unbranched or branched, decumbent and
rooting, the upper, erect leaf-bearing part villous with red-brown hairs. Leaves op-
posite, loosely tufted, internodes c. 2 cm. Petiole 2-3 cm, red-brown hairy. Lamina
10-20 by 3-6 cm, oblanceolate, partly subfalcate, tip acuminate, base narrowed,
margin coarsely serrate-crenate (teeth c. 1.5 mm long, c. 1 cm distant), angles bet-
ween teeth raised, giving the margin an undulate appearance, upper surface glabrous
(young leaves with minute, 2-celled glands, which later collapse, scarcely visible with
a lens), lower surface with veins sparsely hairy on the flanks.
Peduncles axillary, 5-8 mm long, glabrous or sparsely hairy, 1 to 2-flowered, bracts
2, lanceolate, sparsely hairy, pedicel 1-1.5 cm. Sepals 5, connate in the lower part,
lobes narrowly triangular, tip blunt, (sub)glabrous. Corolla c. 5 cm long, broadly
cylindric, somewhat compressed, base narrow cylindric, limb slightly bilabiate, lobes
5, rounded, tube glabrous outside, violet, limb dark violet, nearly black, throat with
8 white lines running from the mouth to the interior. Stamens 4, white, didynamous,
cohering in pairs by the apex of the anthers at right angles to the filaments. Disc
shortly cylindrical, shallowly 5-lobed. Ovary cylindrical, tapering towards the base,
style short, stigma formed from the lower carpel alone, flat, broadly triangular to
(reversely) heart-shaped. Capsule slender, 6-8 cm long, hard and thickly fleshy, slightly
curved, tapering towards the base, splitting on the upper side by a longitudinal slit.
Seeds small, numerous, blackish-brown, elliptic to broadly spindle-shaped, testa with
longitudinal bars (thickenings).
Other collections: Selangor: Comp. 25, Ulu Gombak F. R., 1973, Kochummen FRI 16722 (KEP); type
locality Anthonysamy 1980 SA 337 (UPM), R. Kiew 6 June 1981 RK 1040 (UPM); Waterfall on Sungai
Batu at 200m Kiew BH. 2 Feb 1986 RK 2096 (UPM).
Habitat: Locally common, forming clumps in undisturbed forest, on slopes in shade
and at lower altitudes (200m) in shaded forest in the same valley system.
4 Gard. Bull. Sing. 41(1) (1988)
Notes: Didissandra porphyrantha is a handsome plant with large, beautiful, dark
purple flowers (Fig. 1). The floral tube is violet outside (paler towards the base), the
limb is deep violet almost verging on black. Eight white lines in the throat run from
the mouth to the base, contrasting sharply with alternating dark lines.
It belongs to Section Speciosae, which presently numbers 15 species in Peninsular
Malaysia. It can be told apart from other species in this section by its coarsely serrate-
crenate leaves, which are glabrous on the upper surface (though they are sparsely
studded with two-celled glands when young, (Fig. 2a, b), the more or less glabrous
sepals, which are connate in the lower part, and the glabrous corolla.
The large (5 cm long) deep purple flowers are not unique in the genus or section.
Two species, D. atrocyanea and D. atropurpurea, share these features and their specific
epithets reflect the striking colour of their flowers. The flower of D. atrocyanea is
described by Ridley (1923) as ‘‘black purple, mouth nearly black’’ and must therefore
be very similar to D. porphyrantha. D. atrocyanea is, however, easily distinguished
~ by vegetative characters: its leaves are conspicuously hairy and appear punctate on
the lower surface; the leaf margin is closely serrate with a hair on each tooth and
the plant appears to be smaller with a more rosette-like habit. D. atropurpurea is
distinguished by having more or less entire leaves (the margin is very obscurely crenate)
and very short pedicels so that the bracts are placed close to the calyx.
Several other species are described by Ridley as having violet flowers (D. hirta,
D. longisepala, D. morgani, D. petiolata and D. violacea) but their flowers are smaller _
(2.5 to 3.5 cm long) except for D. longisepala which has flowers 5 cm long. —
D. longisepala, however, differs from D. porphyrantha by having, according to Ridley,
long petioles (7 cm long) and exceptionally long peduncles (10 cm long).
Nothing is known about the pollination of these peculiarly coloured flowers. One
wonders which animal (probably largish insects) are attracted to the dark purple
colour.
Didymocarpus nitidus R. Kiew & A. Weber, sp. nov. Fig. 3, 4a, b & c.
Planta lignosa, 30-40 cm alta. Caulis simplex, 40-70 cm longus, 0.5 cm in diametro; pars inferior
decumbens et radicatus. Folia opposita, in parte superiore caulis aggregata, internodiis 0.5-2 cm longis
separata; petiolus 1.5-2.5 cm, pilis + adpressis obsitus; lamina lanceolata, 10-15 x 2-3.5 cm, in apice
et in basi attenuata, margine crenulata; pagina superior atrovirens, glabra, nitida; pagina inferior pallide
viridis vel albidus, nervis perspicuis; nervi e pilis + adpressis hirti; nervi laterales 15-10, oppositi vel
suboppositi, arcuati. Pedunculi axillares, 6-10 cm, pubescentes, bracteis minutis linearibus 2 in parte
superiore, 1-flori. Sepala 5, c. 2 mm, anguste triangularia, obtusa, e pilis brevibus hispida. Corolla 13-15
mm, alba; tubus et limbus extra e pilis minutis pubescentes; limbus bilabiatus, 5-partitus, lobis rotun-
datis. Stamina 2, antheris globularibus cohaerentes. Discus annularis. Ovarium cylindricum, c. 6 mm,
pilis brevibus et glandulis minutis obsitum; stylus 3 mm; stigma inconspicue capitatum. Fructus capsularis,
cylindricus, 4-4.5 cm, e pilis erectis nigris laxe strigosus, in latere superiore rima longitudinali dehiscens.
Type: Peninsular Malaysia, Selangor. Gunung Bunga Buah, east of summit, 1300-1400 m, Weber &
Anthonysamy 840711-1/1 (WU; iso E, K, KLU, L, WU, UPM).
Woody, unbranched plant 30-40 cm tall. Stem 40-70 cm long, 0.5 cm thick,
strongly woody, decumbent and rooting. Leaves paired, forming a loose tuft at the
top of the stem, internodes 0.5-2 cm. Petiole 1.5-2.5 cm with short, + appressed,
brownish hairs. Lamina lanceolate, 10-15 by 2-3.5 cm, gradually narrowed at both
ends, margin obscurely crenulate, upper surface in vivo deep-green and shiny, —
glabrous; lower surface pale green to whitish (copper-brown when dry), with promi-
nent, hairy veins, veins 15-20 pairs, opposite or subopposite, arched. .
Peduniles axillary, 6-10 cm, shortly hairy, with 2 minute, linear bracts on t
upper part, single flowered. Sepals 5, c. 2 mm, narrow-triangular, blunt, shortly hispi
Two New Species and a New Combination of Gesneriaceae 5
Fig. 3. Didymocarpus nitidus in its natural habitat. (Photo. A. Weber).
Corolla 13-15 mm long, white, outside of tube and limb pubescent with short hairs,
limb bilabiate, S—partite, lobes rounded, lower lobe projecting straight forward.
Stamens 2, anthers globose, cohering at the tips. Disc annular. Ovary cylindrical,
c. 6 mm long with short hairs and minute glands, stigma inconspicuously capitate.
Capsule 2-5 cm long, straight, sparsely strigose with black, erect hairs, opening by
a longitudinal slit on the upper surface.
Other collections: Selangor, type locality: R. Kiew 22 Sept 1978 RK 666 (UPM), Anthonysamy 1980
SA 338 (UPM), R. Kiew 16 May 1982 RK 1166 (UPM), R. Kiew 18 March 1984 RK 1285 (UPM).
Habitat: Common in one locality in undisturbed montane forest, on steep slopes near
the top of a ridge, in shade.
Notes: Didymocarpus nitidus can be distinguished from other Didymocarpus species
by the following combination of characters (for measurements see description):
unbranched, woody stem with rather short internodes; leaves lanceolate, deep green,
glabrous and shiny on the upper surface, pale green to whitish on the under side
6 Gard. Bull. Sing. 41(1) (1988)
Fig. 4. | a-c. Didymocarpus nitidus, flower and leaf. d—f. Didymocarpus breviflorus, flower and leaf.
g-i. Didymocarpus serratifolius, inflorescence, portion of leaf, and leaf. Bar 5 mm flowers;
and 3 cm leaves.
(Fig. 3); margin obscurely crenulate (Fig. 4c); peduncles half (or more than half) as
long as the leaves, single flowered; flowers small with a rather broad, straight tube,
pure white (Fig. 4a, b).
The shiny leaf surface may in part be attributed to a lack of non-glandular uniseriate
hairs which are common in other species of Didymocarpus (Norana, 1982). (These
non-glandular hairs are also absent from the upper surface of Didissandra porphy-
rantha). Both these species possess stalked glandular hairs, acommon feature of both
Didissandra and Didymocarpus.
Didymocarpus nitidus is unique among Didymocarpus species (Norana, 1982) in
that these glandular hairs are completely sunken below the leaf surface which is flat —
:
a
Two New Species and a New Combination of Gesneriaceae 7
and these two features contribute to the leaf’s gloss. Some species of Didymocarpus
do not have a flat leaf surface but instead are mammillate, e.g. D. platypus, or have
a papillose epidermis, e.g. D. malayanus.
Didymocarpus breviflorus (Ridl.) A. Weber & R. Kiew, comb. nov. Fig. 5.
Didissandra breviflora Ridl. Kew Bull. 10 (1926) 474.
Holotype: Peninsular Malaysia, Selangor, Ulu Gombak, c. 1500 ft., 23 Sept 1921, Hume 8437 (SING).
Stem erect, woody, usually unbranched. 10-25 cm tall and 3-6 mm thick, in the
upper part densely covered by long, brown hairs (grey-brown when dry). Leaves
obscurely decussate, crowded at the top of the stem and forming a tuft. Petiole
1-2.5 cm long, densely covered by long (grey-) brown hairs. Lamina oblanceolate
(to lanceolate), partly subfalcate, 9-20 cm long by 2.5-5.5 cm wide, light green in
vivo, margins strongly serrate, teeth c. 3 mm long and 1.5-2 mm wide at base, tip
obtuse, with 14-19 teeth per 5 cm, in vivo the base of the tooth slightly raised (pouched)
with the tooth directed downwards, lateral veins opposite or subopposite, forming
a conspicuous succession 3-4 mm apart, parallel, slightly curved, each vein forking
just below a marginal tooth, the strands of adjacent veins anastomosing and sending
a short strand into the sinus between two teeth, upper surface glabrous, midrib
sometimes with sparse, long hairs, lower surface whitish (grey-brown when dry), with
loose long hairs on midrib and lateral veins.
Peduncle axillary, one to several (in a row) arising from a leaf axil, 8-10 cm long,
purple, sparsely covered by long hairs, single flowered. Bract pair subopposite, green,
c. 5-10 mm below the flower, linear-obtuse. Sepals 5, linear, obtuse, 3 mm long,
Y¥
iM
et
Seite ly
Fig.5. | Didymocarpus breviflorus. a. Fruiting plant in natural habitat. b. Flower of cultivated specimen.
(Photo. A. Weber).
8 Gard. Bull. Sing. 41(1) (1988)
Table 1
Diagnostic characters for Didymocarpus breviflorus and D. serratifolius.
Hairs on stem pale fawn, long, silky ferrugineous, hispid
Petiole length (cm) 1.2.5 + decurrent
(—4 in lower leaves) (—1.5 in lower leaves)
Leaf oblanceolate narrowly lanceolate
(— lanceolate)
Leaf width (cm) 2.5 - 5.5 1.5 -3
Leaf width: length 1 : 2-4 1: 5-8
Indumentum on lower pale fawn, short, dense ferrugineus, long
surface of midrib
No. vein pairs 20 - 33 40 - 50
Marginal teeth
length (mm) 3-5 2-3
apex rounded jagged
No. flowers per peduncle | several (— 4)
Sepals linear, tip blunt ovate, tip acute
Corolla form shortly and broadly trumpet-shaped,
tubular base narrowed
Corolla length (mm) 10 - 14 13 - 22
Fruit indumentum none shortly pubescent
Two New Species and a New Combination of Gesneriaceae 7]
purple, with sparse + appressed hairs. Corolla 10-14 mm long, tube broad-tubular,
c. 4 mm in diameter, curved, lobes 5, rounded, nearly equal, pale violet to nearly
white, very shortly hairy outside (scarsely visible in dry flower). Stamens 2, c. 3 mm
long, anther c. 1.5 mm long, thecae widely divaricate. Disc shortly cylindric, sur-
rounding the ovary base. Ovary oblong with minute, stalked glands. Style strongly
curved down in the upper part, stigma capitate. Capsule linear, glabrous, 3-5.5 cm
long, opening by a longitudinal slit on the upper side, making an angle of 60-120°
with the peduncle. Seeds numerous, minute, elliptic, testa reticulate, with fine pustules.
Specimens examined: Selangor — Genting Simpah 700 m, 29.10.1937 Md. Nur SFN 34298 (E); Old
Gombak Road, 17th milestone upwards to Genting Simpah 330-500 m, Allen 345] (SING); Waterfall
on Old Gombak Road, 12.7.1984 Weber & Anthonysamy 841207-1/1 (WU); 25.11.1984 Kiew RKI551
(UPM); Genting Peras, 10.2.1985 Kiew RK 1614 (UPM).
Habitat: Hill forest, on vertical rock faces or steep banks. (Ridley (1926) incorrectly
quotes the altitude of the type specimen as 500 ft).
Notes: Ridley’s description of Didissandra breviflora is not only brief but also does
not include a description of the stamens which he was ‘‘unable to see’’ in the ‘‘one
crushed flower’’ available to him. Here a comprehensive description is given based
on a wider range of specimens, including fresh material.
As the stamen number is two (instead of four, which characterises Didissandra),
the species is transferred to Didymocarpus. It fits neatly into Section Pectinati as
its leaves are bunched in a tuft at the top of a woody stem and have a serrate margin
(Fig. 5a) and it has short, tubular flowers (Fig. 5b).
Didymocarpus breviflorus most closely resembles D. serratifolius (Fig. 4g-i) in its
venation and conspicuously serrate margin. It is distinguished from D. serratifolius
by the characters listed in Table 1.
It occupies a distinct habitat. It grows on vertical rock faces or steep earth banks
which are bare of other vegetation or leaf litter. In this habitat, it may be common
but it is not found in other habitats in the vicinity. This suggests that its seedlings
are intolerant to being covered by leaf litter.
Acknowledgements
The authors thank Mr S. Anthonysamy (UPM) for his assistance in the field;
Mag. S. Klenner and Dr E. Vitek (WU) for their technical assistance; and the Curators
of the herbaria at E, K, L, SING for permission to examine specimens in their keeping.
References
Kiew, R. (1982). Didymocarpus platypus (purple form). Malayan Naturalist 35 (3):24.
Norana Ghazali (1982). Comparative anatomy of common species of Didissandra,
Didymocarpus and Chirita (Gesneriaceae). Unpublished project thesis, Depart-
ment of Biology, Universiti Pertanian Malaysia.
Ridley, H.N. (1923). Flora of the Malay Peninsula. Vol. II. Reeve & Co., London.
Ridley, H.N. (1926). Additions to the Flora of Malaya. Didissandra breviflora. Kew
Bull. 10:474.
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Mnbnes, 70-7 & ivath,
Plantlet Production of Swietenia macrophylla King
through Tissue Culture
S.K. LEE' and A.N. RAO?
'c/o Parks and Recreation Department
National Development Building Annexe B, Maxwell Road, Singapore 0106.
*Botany Department, National University of Singapore,
Kent Ridge, Singapore 0511.
Abstract
Different vegetative parts of Swietenia macrophylla King were used as explants in in-vitro studies. They
were cultured in MS medium supplemented with various plant growth regulators. Adventitious shoots
could be obtained from the friable callus when the seedling nodal segments were cultured on BA (2, 5
ppm) media. The regenerated shoots could be rooted to form whole plantlets which could be transferred
to soil.
Introduction
There has been considerable progress made recently in regenerating plantlets of
tropical hardwood trees through tissue culture (Lee & Rao, 1981; 1986; 1987, Rao
& Lee, 1986, Rao, 1988). The technique has great potential for exploitation in the
mass production of propagules of forest tree species to implement afforestation and
reforestation programmes. In this paper, the in-vitro culture response of various ex-
plants of Swietenia macrophylla King (Broadleaf Mahogany) is reported. The
usefulness of S. macrophylla is very clearly explained in the tree flora of the S.E.
Asian region (Corner, 1952).
Materials and Methods
Seedlings of S. macrophylla were established in sand. Both nodal and internodal
segments of about 0.5 cm length were used as explants. Nodal segments from young
basal shoots of some 10-year old trees were also used in the experiments. These
explants were lightly washed in running water and later surface sterilised for about
10 minutes in 10% (w/v) freshly prepared sodium hypochlorite solution. Tween 20
was added as wetting agent. To reduce the exudation of phenolic compounds into
the media, the nodal segments from the trees were soaked in sterile water for about
2 hours, after surface sterilisation. Seedling nodal segments did not require this treat-
ment. Leaf tissue from shoots regenerated under in-vitro conditions were also used
to test their growth response.
Murashige & Skoog (1962) medium was used with 2% sucrose and 0.7% Difco
Bacto Agar. The macronutrients were reduced to half strength to lower the salt
concentration. However, the concentration of ammonium nitrate was increased to
2 g/l to increase the level of reduced nitrogen. The media were supplemented with
different concentrations and combinations of benzyladenine (BA), Indole-acetic acid
(IAA), Indole-butyric acid (IBA), and Kinetin (K). All cultures were maintained at
11
12 Gard. Bull. Sing. 41(1) (1988)
22°C to 25°C with a photoperiod length of 16 hours of Philips white flourescent
light at 35-45 wmole. em~’s~', followed by 8 hours darkness. Each treatment was
replicated 10 times and each experiment was repeated twice. For histological studies,
selected tissues of varying ages developed in-vitro were fixed in formalin acetic alcohol
(1:1:18). Standard practices were followed for dehydration, microtoming and staining
with hematoxylin and erythrosin (Sass, 1968).
Results
Response of explants on IAA + K media on a 5 factorial combination: Both
seedling explants as well as those excised from the mature (10-year old) trees were
inoculated onto IAA and K media (0, 1, 2, 5 and 10 ppm each), in a 3? factorial
combination. The nodal segments of young shoots excised from 10-year old trees
remained green without much response. Although the axillary buds in some replicates
-(IAA [0 to 2 ppm] and high K [5 to 10 ppm]) enlarged to some extent, they remained
dormant and no shoots developed. About 60% of the replicates turned brown about
12 days after inoculation and there was no further growth.
Growth was also slow in the nodal and internodal segments from the seedling axis.
All segments remained fresh. The explants on media with high IAA (5, 10 ppm) and
K (0 to 10 ppm) started growing 25 to 30 days after inoculation. In about 70% of
the cultures, the middle region of the segments enlarged and small ‘swellings’
developed when they were subcultured onto fresh medium 40 days after the first
inoculation. In cultures of about 50 to 60 days old, many small lobes of compact
callus developed which enlarged further in 60 to 70 days (Fig. 1). In all the cultures,
the axillary buds remained dormant, and did not emerge as shoots.
Response of nodal segments on BA media: In view of the limited response seen
above, an attempt was made to induce multiple shoots by culturing nodal segments
both from seedlings and old trees, in BA (0 to 10 ppm) media. The nodal segments
from the trees failed to respond. About 50% of the replicates turned brown within
10 to 12 days after inoculation and subsequently died.
With the nodal segments from seedlings, growth improved in all the media used.
In BA media (0.1 and 1 ppm), the axillary buds sprouted into shoots about 20 days
after inoculation. Shoot growth was slow and within 14 days from sprouting, the
tiny leaves that developed defoliated. No subsequent development was observed,
irrespective of the concentration used.
Figure 1 to 8. (opposite page)
Fig. 1. Compact callus developing from a nodal segment cultured on IAA (5.0 ppm) + K (2.5 ppm)
medium (60 days). Many lobes were obtained but growth is limited.
Fig. 2. Small shoots with whitish leaves developing from the callus cultured on BA (2 ppm) medium
(70 days).
Fig. 3, Several shoots obtained from the callus subcultured continuously on BA (2 ppm) medium.
4,5. These were the 4th subculture and they were about 120 days after inoculation.
Fig. 6. A rooted plantlet of S. macrophylla, with a single root.
Fig. 7. A periderm was formed at the cut surface of the nodal segment that was immersed in BA
(2 ppm) medium (10-12 days). Note the cambial initiation.
Fig. 8. About 6 to 8 layers of cambial tissue were formed (15 to 20 days). The cells on the outer region
were rounded and large.
5
°
13
Tissue Culture of Swietenia macrophylla
1 to 8
Figure
A
14 Gard. Bull. Sing. 41(1) (1988)
The best response was obtained in BA (2 and 5 ppm) media. The axillary buds
sprouted 10 days after inoculation, with each bud giving rise to a small reddish brown
shoot. The growth was vigorous and shoots measured 1.5 cm in length in about 25
to 30 days. Thereafter, the growth rate slowed down, and the lower leaves defoliated.
At this stage, the shoot segments were subcultured onto fresh media of similar com-
position, otherwise, the new axillary shoots would remain dormant and leafless. Even
after subculturing, only slight elongation of the shoots was observed and no multiple
shoots developed.
Along with the axillary shoots, callus developed at the basal region of the segments
in about 2 weeks (Fig. 2). The growth progressed further and about one month after
inoculation, the surface layers ruptured lightly at certain loci, to release small specks
of whitish and friable callus. These were subcultured once in 3 weeks to encourage
further tissue growth.
About 9 weeks after the first inoculation, small whitish buds developed on the
surface of the brown callus. Some of these developed into shoots with whitish or
pale coloured leaves (Figs. 2, 3), and in 10 days after emergence, the leaves turned
greenish. These shoots grew to a height of 1 to 3 cm within 25 days after emergence.
A cluster of 6-7 shoots was formed around a single clump of friable callus (Figs.
4, 5), and these shoots were excised for rooting. After excision of the mature shoots,
new shoots were induced when the brownish and friable callus clump was subcultured
onto a fresh medium.
Anatomical studies showed that about 10 to 12 days after inoculation, a distinct
periderm was formed at the cut surface of the nodal segment and a regular cambial
zone was initiated below the damaged peripheral layers (Fig. 7). There was no visible
change observed in the original cells in terms of losing their contents before the
regeneration of the new cambium. The fully formed cambial zone was 5 to 6 layers
deep and prominent (Fig. 8). The cambial formation was distinct but the distribution
was discontinuous (Fig. 9). The new cells formed towards the exterior from the
cambial activity were big, loosely arranged and of various sizes and shapes. Most
of the peripheral cells were either rounded or elongated. In 2 to 3 weeks old callus,
Figure 9 to 16. (opposite page)
Fig. 9. There were variations in cambial distribution and formation of loosely arranged tissue. The
peripheral cells were of various shapes and sizes (25 days).
Fig. 10. A mass of compact callus tissue which contained meristematic layers divided in many planes,
contributing to the growth of the callus mass. The peripheral cells were loosely arranged.
Fig. 11. Many growth nodules were present in some callus clumps. These consisted of meristematic
cells which divided actively, contributing to the growth of the callus.
Fig. 12. | Mature callus (60 days) with loosely arranged tissue, with a shoot primordium.
Fig. 13. The shoot primordium from Fig. 12, enlarged to show the shoot apex. The tunica-corpus zones
were distinct.
Fig. 14. An axillary bud of a regenerated shoot, induced to grow in a BA (2 ppm) medium.
Fig. 15. | New adventitious shoot growing directly from the secondary stem axis, in BA (2 ppm) medium
(95-100 days).
Fig. 16. Leaf cultured on BA (2 ppm) medium (85 days). Several outgrowths from the lower epidermal
layers were observed. Some of the outgrowths consisted of 8 to 10 cells (glandular) and could
be detached from the epidermal layers.
Tissue Culture of Swietenia macrophylla 15
Figure 9 to 16
16 Gard. Bull. Sing. 41(1) (1988)
the inner tissue was also compactly arranged although the peripheral free cells were
loosely arranged (Figs. 9, 10). Within the new tissue, there were many meristematic
regions and through their activity, additional tissue was formed, thereby contributing
to the growth of the callus (Figs. 10, 11).
In callus 5 to 6 weeks old, distinct ‘growth nodules’ were present. Cells within
the ‘growth nodules’ were compact and radially arranged in concentric rings (Fig. 11).
These cells as well as those surrounding them were highly meristematic and through
their active division, the volume of the callus increased. The cells towards the
peripheral region of the ‘growth nodules’ were more rounded and they were loosely
arranged, some with tannin contents (Fig. 11). The old tracheal cells remained in
the centre with the new cell layers around them (Fig. 11). In the newly formed tissue
2 islands of secondary phloem were regenerated.
Shoot primordia developed from the friable callus in about 60 days after inocula-
tion (Fig. 12). In the axis the cells of different sizes and shapes were loosely arranged
with many air spaces bounded by a distinct epidermis. The peripheral layers remained
fairly intact despite loose tissue inside. At certain loci, a single or a group of
meristematic cells organised into shoot primordia. Further growth led to the develop-
ment of a shoot apex with a distinct tunica corpus and the leaf primordia (Figs. 12,
13). With subsequent subculturing, additional shoots developed with new axillary
buds (Fig. 14). They developed into secondary shoot after the third subculture (about
80 to 95 days from first inoculation). These also developed into normal shoots.
Another interesting feature was the direct development of free buds on the internodes.
They started as small swollen structures attached to the exis at an angle. The trans-
verse section of the axis showed their relationship very clearly and most of them
developed from the inner cortical tissue. Leaf primordia were distinct and the ones
formed earlier were scale-like with basal meristematic tissue. Obviously they can be
used as explants to regenerate further tissue growth (Fig. 15).
Response of leaf tissue on BA media: Young leaves excised from regenerated shoots
were inoculated onto media supplemented with BA (0 to 10 ppm). Except for media
supplemented with BA (2, 5 ppm) no response was observed in the others. The leaf
tissue turned brown on BA (10 ppm) medium in about 4 days after inoculation. Hyper-
trophic growth was seen in explants at BA medium (2 ppm), resulting in the leaf blade
curling up into many folds. On the surface many small outgrowths were also observed.
Anatomical studies showed two growth patterns, (a) the leaf blade was folded
upward because of excessive growth in the region of the lower epidermis and, (b) the
epidermal and subepidermal layers were wavy, forming many small outgrowths
(Fig. 16). At certain points mesophyll cells also divided, contributing to the forma-
tion of small outgrowths. Each one of these had a group of actively dividing cells.
Plantlet formation: The excised shoots were planted onto IBA (2.5 and 10 ppm)
media to induce rooting and the initial response was slow. At the lower concentration
(2 ppm), no root developed, whereas at higher concentrations (5 and 10 ppm), only
some of the shoots rooted in about 40 days after inoculation. In each case, only 1
root was produced, growing horizontally to the shoot axis, resembling the primary
root of the seedlings (Fig. 6).
Transfer of plantlets into Jiffy-7 pellets: The plantlets with single shoots were
transferred to Jiffy-7 pellets which were stored within an enclosed translucent struc-
ture. They were each dipped in benlate solution prior to transfer, to avoid fungal
infection. The survival rate was about 20%. The leaves were yellowish despite being
fed with phostrogen, a soluble fertiliser. The saplings that developed were relatively
weak. However, these could be revived with appropriate treatments and grown into
healthy plantlets.
Tissue Culture of Swietenia macrophylla 17
Discussion
The possibility of inducing adventitious shoots from callus and nodal segments
is described. Thus there is a good potential for adopting in-vitro methods to produce
propagules in large numbers. However, the average number of shoots that was
produced per replicate in the present study was only about 6. Therefore further studies
need to be conducted to establish the pattern for production of large number of
propagules required for different programmes. Besides using nodal or internodal
segments, leaf tissues should be used extensively to induce shoot growth. Large
numbers of shoots were induced from leaf tissue of Fagraea fragrans Roxb. (Lee &
Rao, 1986). In this study, leaf tissue of S. macrophylla also responded well in BA
media, producing several outgrowths. If each of the outgrowths could be induced
to differentiate into shoots, many shoots could be obtained from a single leaf section.
Further work is in progress.
For in-vitro techniques to be effectively adopted, the plantlets produced must be
healthy so as to ensure a high survival rate of quality plants when transferred to soil.
This area needs to be refined further since a survival rate of only about 20% of the
plantlets was achieved in the present studies. One of the causes could be due to the
formation of only a single root which resembled a tap root. More roots might ensure
a higher survival rate.
The inability of nodal segments trom mature trees to respond is another area of
concern. The problem of juvenility factors should be further explored. Various means
to induce juvenile shoots to grow from mature plants, either through pruning or
grafting, should be attempted in case of elite trees. The newly developed parts should
be used as explants.
The present study has re-emphasised that BA is consistently effective in inducing
organogenesis in callus or multiple shoot growth in nodal explants of woody plants
(Zaerr & Mapes, 1982). Media supplemented with auxin and kinetin combinations
were only able to induce callus growth but the presence of BA promoted shoot growth.
Conclusion
With further understanding of the growth responses of various explants and the
factors affecting them, there is a good potential for adopting the tissue culture techni-
que for producing propagules of S. macrophylla in large numbers. Such studies can
be extended to include other useful economically important trees.
Acknowledgement
The authors wish to thank Mr Ong Tang Kwee for his help in photography.
References
Corner, E.H. (1952). Wayside Trees of Malaya. Government Printing Office,
Singapore.
Lee, S.K. and Rao, A.N. (1981). /n-vitro plantlet development in tropical trees —
Callophyllum inophyllum and Eugenia grandis, pp. 185-190. In COSTED Symp.
on Tissue Culture of Economically Important Plants. Ed. A.N. Rao, Singapore.
Lee, S.K. and Rao, A.N. (1986) /n-vitro regeneration of plantlets in Fagraea fragrans
Roxb. — a tropical tree. Plant Cell, Tissue and Organ Culture 7: 43-51.
18 Gard. Bull. Sing. 41(1) (1988)
Rao, A.N. and Lee, S.K. (1986). An overview of the in-vitro propagation of woody
plants and plantation crop; 123-138, in Plant Tissue Culture and its Agricultural
Applications. Ed. Withers, L.A. and Alderson, P.G., Butterworth, London.
Lee, S.K. and Rao, A.N. (1987). Propagation of some Eugenia species through Tissue
Culture. (IDRC and FRIM publication, in press).
Rao, A.N. (1988). /n-vitro culture studies on economically important tropical trees.
(Biotrop publication, in press).
Sass, J.E., (1986). Botanical Microtechnique. The Iowa State University Press, Ames,
Iowa.
Zaerr, J.B. and Mapes, M.O. (1982). Action of growth regulators, pp. 231-255. In
Tissue Culture in Forestry. Ed. J.M. Bonga and D.J. Durzan. Martinus
Nijhoff/Dr W. Junk Publishers, The Hague.
Compound Fertilizer Requirements for the
Establishment and Early Growth of Popular Ornamental
Shrubs between Road-side Trees
THAI WU FOONG and CHENG Nol YANG
Botanic Gardens, Parks and Recreation Department, Singapore.
Abstract
The fertilizer needs of some popular shade-loving shrubs were evaluated by a 1 year field trial. Plant
growth was the same with or without inorganic fertilizer supplements irrespective of shade conditions and
trial plants employed. Nutrients available from the planting mix comprising topsoil: treated sludge
(3:1 v/v) appeared to be sufficient for the early growth of shade shrubs.
Introduction
Evaluation of fertilizer requirements of ornamental and landscape plants have been
conducted extensively in the United States (Harris et al., 1977; Neely et al., 1970;
Smith & Treaster, 1981, and van de Werken, 1981). Traditionally, fertilizer recom-
mendations have been based on trunk caliper and in some cases on the soil surface
area (Smith & Treaster, 1981). In the Parks and Recreation Department, Singapore,
manuring practices are frequently, if not always, inferred and adopted from findings
established for economic plants in the region. In the case of ornamental shrubs, they
are often manured similarly irrespective of the edaphic factors e.g. light intensity of
the habitat.
With the advent of the Garden City Campaign in Singapore, many road-side trees
have been planted. The tree crowns have expanded over the years leaving much of
the areas between under shade. Various suitable shade-loving shrubs have been
established between trees to augment the adornment. However, empirical data
pertaining to their fertilizer needs are lacking. Plants adapted to shade have metabolic
rates and growth morphology which differ from those grown in full sun (Fails
et al., 1982a, b & c; McClendon & McMillen, 1979 & 1982) and hence their fertilizer
requisites are likely to be different. An interaction between shade intensity and fer-
tilizer requirement has been observed for the growth of Taxus x media ‘Hicksii’ (Khata-
mian & Lumis, 1982). In order to eliminate guesswork from fertilizing shade shrubs,
a field trial was initiated to provide the necessary information.
Materials and Methods
The experiment sites were on the East Coast reclaimed land under natural shade
of Acacia auriculiformis A. Cunn. ex Benth. and Samanea saman (Jacq.) Merr. Three
shade regimes were classified using the Li-Cor LI-185B photometer. The three shade
regimes and the test shrubs selected for the different light conditions appear in Table
1. The test plants have been commonly planted under these specific shade regimes.
if
20 Gard. Bull. Sing. 41(1) (1988)
Table 1
Shade regimes and attendant test plants
Shade regimes Experimental shrubs
1. Light shade a. Ptychosperma macarthurii
Light intensity (LI) (Wendl.) Nichols
= 15,000 - 20,000 lux b. Ixora javanica (Bl.) DC.
2. Medium shade a. Philodendron selloum C. Koch.
10,000 < LI < 15,000 lux b. Polyscias filicifolia L.H. Bailey
3. Dense shade a. Aglaonema pseudobracteatum Hort.
5,000 < LI < 10,000 lux b. Dracaena surculosa punctulata Hort.
Two compound fertilizers, Nitrophoska 15:15:15 and 12:12:17:2 + TE, were tested
against shrubs assigned to each shade regime at 3 rates viz: rate b= current practice
of 100g per shrub at half yearly intervals, broadcasted; rate a = half the recommended
dosage, and rate c = twice the recommended dosage. This is summarized for each
shade regime as follows:-
Compound fertilizer Rate
a. (aided
Nitrophoska SO ee
Se
13: 15215 Rbiisdemears 2
Cty 520
a |.) 0 ee
Shade regime ———>. Nitrophoska 2 oles b
——— - >
12:42:17:2 8: TE, inac) a
C A aaa
Control : without fertilizer
treatment
The various treatments were as follows:
= Control — without fertilizer treatment.
la = Nitrophoska 15:15:15 applied at rate a (50g per shrub at half yearly
intervals).
lb =~ Ibid but at rate b (100g per shrub at half yearly intervals).
lc =~ Ibid but at rate c (200g per shrub at half yearly intervals).
2a = Nitrophoska 12:12:17:2 + TE applied at rate a (50g per shrub at half
yearly intervals).
2b =~ Ibid but at rate b (100g per shrub at half yearly intervals).
2c =~ Ibid but at rate c (200g per shrub at half yearly intervals).
Each treatment was replicated 5 times.
Fertilizer Requirements for Shrubs Between Road-side Trees 21
Planting holes of dimension 0.5m xX 0.5m x 0.5m were made and backfilled
with a sandy clay loam topsoil premixed with treated sludge in the ratio 3:1 v/v
(topsoil : sludge). Uniform plants of each species were laid out in a randomized block
design under the appropriate shade regime, 1.5m apart from one another. Plants were
left to establish for two weeks before fertilizer treatment was initiated. Similar to
routine field fertilizer application, fertilizer was broadcasted around the plants at
a safe distance from the trunk to avoid burn injury.
The trial was conducted for a year. A regular pest control programme was main-
tained throughout the trial period. Snails were the most damaging pest but these were
kept at bay with ‘Snailex’. Whenever necessary, trees were pruned to maintain the
shade conditions required.
After 1 year, trial plants were harvested, washed with a non-ionic detergent and
finally rinsed with distilled water. Dry matter accumulations were determined and
recently matured leaves separated for the analysis of the N, P and K contents.
Composite soil samples comprising three 0-6’’ soil cores were collected for the analysis
of total N, Bray P and ammonium acetate exchangeable K.
Total N was determined by the micro-Kjeldahl method, phosphorus by the
molybdenum blue method and potassium by flame photometry (Anonymous, 1980;
Chapman & Pratt, 1961; Hesse, 1971).
Results and Discussions
Results were statistically analysed by the Duncan Multiple Range Test and tabulated
(Tables 2-7).
Irrespective of the shade regimes and the attendant plants investigated, there was
no apparent relationship between dry matter yield and fertilization. With Aglaonema
pseudobracteatum (Table 3), Polyscias filicifolia (Table 4) and Ptychosperma macar-
thurti (Table 6), treatment 2c (12:12:17:2 + TE at 200g per shrub at half yearly
intervals) appear to have retarded early growth.
The N and K contents in the soil did not increase consistently with higher fertilizer
rates probably partially due to leaching and run-off losses. However, in some cases,
the soil P content was found to increase significantly with increasing fertilizer rates
(Tables 3 & 6). P accumulation in the soil was probably due to its low mobility in
the soil and low consumption by the plants.
Foliar N, P and K contents did not reflect the levels of these elements in the soil
i.e. higher levels of such elements in the soil did not necessarily lead to their greater
accumulation in the leaves.
Regardless of shade intensities, trial plants, fertilizer types and rates of applica-
tion, the untreated controls appeared to perform similarly as the treated counter-
parts both visually and based on dry matter accumulation (Tables 2-7). The findings
of the present investigation indicate that the fertilizer requirements for the early
growth of ornamental shade shrubs were low. As a corollary, Othieno (1983) reported
that the N, P and K contents of mature tea leaves were reduced under shade. The
nutrient needs of shade shrubs appeared to be adequately met by the nutrient elements
furnished by the sludge incorporated initially into the topsoil.
Conclusion
Shade-loving shrubs could maintain healthy growth on topsoil supplemented with
sludge. Additional inorganic fertilizer did not further enhance growth in the first year.
At higher rates, inorganic fertilizer could become detrimental to plant growth.
Gard. Bull. Sing. 41(1) (1988)
22
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Fertilizer Requirements for Shrubs Between Road-side Trees
Gard. Bull. Sing. 41(1) (1988)
26
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28 Gard. Bull. Sing. 41(1) (1988)
This study tends to suggest that if sludge is used in the planting mix for shade
shrubs, the latter can thrive well for the first year without any supplement of inorganic
fertilizer. However, their long-term fertilizer requirements need to be elucidated by
further field experimentation.
Literature Cited
Anonymous. (1980). Handbook on reference methods for soil testing. The Council
on Soil Testing and Plant Analysis, University of Georgia, USA.
Chapman, H.D. and Pratt, P.F. (1961). Methods of analysis for soils, plants and
waters. Division of Agricultural Sciences, University of California, USA.
Fails, B.S., Lewis, A.J. and Barben, J.A. (1982a). Net photosynthesis and transpira-
tion of sun- and shade-grown Ficus benjamina leaves. J. Amer. Soc. Hort. Sci.,
107, 758-761.
Ibid. (1982b). Anatomy and morphology of sun- and shade-grown Ficus benjamina.
J. Amer. Soc. Hort. Sci., 107, 754-757.
Ibid. (1982c). Light acclimatization potential of Ficus benjamina. J. Amer. Soc. Hort.
Sci., 107, 762-766.
Hesse, P.R. (1971). A textbook of soil chemical analysis. William Clowes & Sons
Limited, London.
Khatamian, H. and Lumis, G.P. (1982). Influence of shade, media and fertility on
growth of Jaxus. J. Arbor., 8, 247-249.
McClendon, J.H. and McMillen, G.G. (1982). The control of leaf morphology and
the tolerance of shade by woody plants. Bot. Gaz., 143, 79-83.
Othieno, C.O. (1983). Studies on the use of shade in tea plantations in Kenya. I.
Effects of nutrient uptake and yield of tea — Preliminary results. 7ea, 4, 13-20.
Smith, E.M. and Treaster, S.A. (1981). Fertilizing trees in the landscape: A 9-year
evaluation. Ohio Agricultural Research and Development Center, Research
Circular 263, 11-13.
van de Werken, H. (1981). Fertilizing and other factors enhancing the growth rate
of young shade trees. J. Arbor. 7, 33-37.
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THE GARDENS’ BULLETIN
j SINGAPORE
VOL. 41 (Part 2) 1 December 1988
CONTENTS
PAGES
VERMEULEN, J.J. and LAMB, A.:
Six New Species of Bulbophyllum Sect. Monilibulbus (Orchidaceae) .......... 29-41
NG, F.S.P.:
Three New Taxa in Elaeocarpus in the Malay Peninsula ......................006. 43-44
| BIDIN, Aziz, JAMAN, Razali and SALLEH, Mat Kamaruddin:
A New Species of Adiantum from Trus Madi Range, Sabah ..................... 45-48
_ FERNANDO, Edwino S.: 7 :
§ Four New Taxa of Philippine Rattans (Palmae: Calamoideae) .................. 49-58
_ SWAN, Frederick R. Jr.: :
Tree Distribution Patterns in the f
) Buxm limah Nature Reserve, Singapore «2.2.2.5... ccsccceeedcsscaueavevecaseccrececces 59-81 i
_ WONG, K.M., WONG, Y.S. and SAW, L.G::
Notes on the Early Exploration and Botanical Collecting
in the Endau-Rompin Area of Peninsula Malaysia ...................cceceeeeeeeees 83-91
;
_ BIDIN, Aziz:
A Further Chromosome Count for Osmunda (Osmundales)
RI AEWA 2g, rs She 5 kU Cs aoe hdei'as dad dus socsdaascainnercesscecces 93-94
_ Book Review
_ CORNER, E.J.H.:
MIE 2G. soos ocivcdbuavavoodaedae ceeds badcbcsedcecccedecsecs 95
Published by the Botanic Gardens
Parks and Recreation Department
Ministry of National Development )
Cluny Road, Singapore 1025. \
ee Nm |
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tr
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GARDENS’ BULLETIN
EDITORIAL COMMITTEE
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eC AE) RO a nds RS ts SST SPA
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EXCHANY
THE GARDENS’ BULLETIN
SINGAPORE
VOL. 41 (Part 2) 1 December 1988
CONTENTS
PAGES
VERMEULEN, J.J. and LAMB, A.:
Six New Species of Bulbophyllum Sect. Monilibulbus (Orchidaceae) .......... 29-41
NG; F.S:P.:
Three New Taxa in Elaeocarpus in the Malay Peninsula ........................4. 43-44
BIDIN, Aziz, JAMAN, Razali and SALLEH, Mat Kamaruddin:
A New Species of Adiantum from Trus Madi Range, Sabah ..................... 45-48
FERNANDO, Edwino S.:
Four New Taxa of Philippine Rattans (Palmae: Calamoideae) .................. 49-58
SWAN, Frederick R. Jr.:
Tree Distribution Patterns in the
Eeraieit Breit NETS RESET VC) “SING ADOTE eons. a ooo donee eiieie scien Hes leap desen donno 59-81
WONG, K.M., WONG, Y.S. and SAW, L.G.:
Notes on the Early Exploration and Botanical Collecting
in the Endau-Rompin Area of Peninsula Malaysia ...................cceeeeeeeeeees 83-91
BIDIN, Aziz:
A Further Chromosome Count for Osmunda (Osmundales)
I aR RRC De ok ok oe ST soa wikis ecipabceuathesdespseeaine 93-94
Book Review
CORNER, E.J.H.::
SIR SD PERCE, MRT ho 6 cn dd cel, Wry URS eas ckawaa bude hnRdy cna seoeedeces 95
Published by the Botanic Gardens
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Six New Species of Bulbophyllum Sect.
Monilibulbus (Orchidaceae)
J.J. VERMEULEN! and A. LAMB?
'Rijksherbarium, P.O. Box 9514, 2300 RA Leiden,
The Netherlands.
Agricultural Research Station, P.O. Box 197,
Tenom, 89908 Sabah, Malaysia. —
Drawings by J.J. Vermeulen
EFFECTIVE PUBLICATION DATE: 10 MAR 1989
Abstract
Six new species of Bulbophyllum sect. Monilibulbus (Orchidaceae) from Borneo are described: B. kestron,
B. leproglossum, B. nubinatum, B. pelicanopsis, B. scabrum and B. thymophorum. Full descriptions and
detailed line drawings are presented of each species. Possible relationships of sect. Monilibulbus within
the genus Bulbophyllum are pointed out.
Introduction
The approximately 50 species of Bulbophyllum sect. Monilibulbus J.J. Smith range
from China (Yunnan), Indochina, Malaysia, Philippines to W. Indonesia (eastwards
up to Celebes and the Lesser Sunda Islands). As with most other sections within
Bulbophyllum, sect. Monilibulbus has never been subject to revision. Only enumera-
tions for comparatively small areas within its range have been published: Thailand
(Seidenfaden, 1979), West Malaysia (Holttum, 1957) and Java (Smith, 1905). Many
more species (often not even recognized as pertaining to sect. Monilibulbus) have
been described in numerous papers by Smith, Schlechter and Ames, as parts of endless
enumerations of new orchid species.
Within the large genus Bulbophyllum the species of sect. Monilibulbus can be
recognized by the following set of characters:
Rhizome creeping. Pseudobulbs distinct, approx. close together, (occasionally widely spaced in B. in-
aequale (Bl.) Lindl.), obliquely reclining and covering or even partly enveloping the subsequent section
of rhizome for most of their length, only the very top more or less erect (pseudobulbs distinctly dorsoven-
trally flattened but not particularly oblique in B. moniliforme Par. & Rchb. f.), with one leaf. Inflorescence
with one flower. Pedicel with an extra node close to its base.
Sect. Monilibulbus is a West Malesian (Van Steenis, 1948: p. XI) element. The
combination of characters mentioned distinguishes the section. Elsewhere within
Bulbophyllum all these characters occur as well, but always in different combina-
tions. They can be found in particular in species belonging to sections which have
a mainly East Malesian (New Guinea and surrounding archipelagos) distribution and
which have one-flowered inflorescences. The sections Fruticicola Schltr, Epibulbon
Schltr and Leptopus Schitr (see Schlechter, 1911-1914) can be mentioned as examples.
The flowers of sect. Monilibulbus, although often of a peculiar structure, do not
have a single character in common. Here, too, morphological similarities with E.
Malesian sections exist, in particular with the sections Leptopus Schltr and Brachypus
Schltr (see Schlechter, 1911-1914).
29
30 Gard. Bull. Sing. 41(2) (1988)
Among the sections with a one-flowered inflorescence, sect. Monilibulbus has a
distinctly aberrant range. Most sections with a one-flowered inflorescence are mainly
East Malesian, with only few representatives in West Malesia. Examples are sect.
Fruticicola Schltr, with many species in New Guinea and very few in West Malesia
(e.g. B. perductum J.J. Smith on Java and an undescribed species on Borneo), and
sect. Polyblepharon Schltr with numerous species in New Guinea and only few species
in W. Malesia (e.g. the widespread B. tortuosum (Bl.) (Lindl.).
Few sections with one-flowered inflorescences have an approximately equal number
of species occurring in West and East Malesia, e.g. sect. Sestochilus (Breda) Benth.
& Hook. f. The numbers of species belonging to this section described for Thailand
(Seidenfaden, 1979) or West Malaysia (Holttum, 1957) or New Guinea (Schlechter,
1911-1914) are of comparable magnitude.
Sect. Monilibulbus is the only section in which a one-flowered inflorescence is com-
bined with an exclusively West Malesian distribution.
Perhaps not supported by distribution patterns, but consistent with shared
- vegetative and floral characters, a close relationship of sect. Monilibulbus to East
Malesian sections is suggested, particularly to sect. Brachypus Schltr, Epibulbon Schltr,
Fruticicola Schltr and Leptopus Schltr.
Basic to this statement are two assumptions.
Firstly, sect. Monilibulbus should be a natural (monophyletic) group, i.e. a group
of species derived from a single ancestor species. Crucial for recognizing a
monophyletic group is that the species of the group share a number of characters
which can be considered derived within the group. Monilibulbus has a set of characters
shared by (almost) all its species. Unfortunately, without further phylogenetic analysis
one can only guess whether or not these are derived.
Secondly, within Bulbophyllum the character state ‘many-flowered inflorescence’
should be primitive, and the state ‘one-flowered inflorescence’ derived. This is very
likely, considering the fact that in most genera which may serve as the hypothetical
immediate ancestor of Bulbophyllum (other genera of Denbrobieae sensu Burns-
Balogh & Funk, 1986) most species have many-flowered inflorescences.
Some species of sect. Monilibulbus are very variable, particularly B. ovalifolium —
(BI.) Lindl. The new species B. kestron, B. leproglossum and B. scabrum all occur —
within the geographical range of B. ovalifolium and show a distinct similarity to races —
of that species. Before describing them as new species the variability of B. ovalifolium
has been surveyed extensively. The characters of the new species distinguishing them —
from B. ovalifolium are mentioned under the description of each of them. }
The other three species B. nubinatum, B. pelicanopsis and B. thymophorum each —
have one or more outstanding features, which immediately distinguish them from
other species of sect. Monilibulbus.
Colour slides of all six new species have been published in Vermeulen & Lamb (1988).
Description of the New Species
Bulbophyllum kestron J.J. Vermeulen & A. Lamb, sp. nov. Fig. 1.
Bulbophyllo ovalifolio affinis, labelli margine denticulato-lacerato differt. Type: Borneo; Lamb 566/86
(K!).
Rhizome creeping, 0.6 mm diam. Pseudobulbs 0.2-0.5 cm apart, ovoid, somewhat
flattened, 0.2-0.5 x 0.2-0.4 cm. Petiole 0.8-2 mm long. Leaves rather thin, elliptic
to (ob-)ovate, 0.5-1.7 x 0.2-0.5 cm, index 2.5-4. Inflorescence 2.5-4 cm long,
1-flowered. Peduncle 1.8-2.5 cm. Floral bracts tubular, c. 1.5 mm long. Pedicel and
Six New Species of Bulbophyllum 31
ovary 5-14 mm long. Median sepal thin, elliptic to obovate, 2.5-6 x 1.5-2.5 mm,
index 1.6-2.5, tip rounded, margins finely papillose, surface glabrous. Lateral sepals
free, ovate to elliptic, 3.8-6 x 2-3.5 mm, index 1.5-2.5, otherwise as the median.
Petals thin, obovate, 1.2-1.9 x 0.7-1.2 mm, index 1.5-2, tip rounded, margins erose
towards the tip, surface glabrous. Lip recurved, rather thick, c. elliptic, 1-2.8 x
0.8-1.5 mm, adaxially with 2 keels in the basal part, tip rounded, margins dentate-
lacerate c. half way, surface with large, often flattened, rounded to truncate appen-
dages. Column 0.4-1.2 mm long. Stelidia triangular, 0.15-0.7 mm long, with a distinct,
obtuse tooth along the lower margin. Stigma with a rather inconspicuous basal callus.
Pollinia 4, of unequal size. Stipes absent.
Colours: Sepals bright orange to salmon red, or green, suffused with dark red. Petals
pale yellowish to pale orange red, occasionally with somewhat reddish purple top
part and midvein. Lip (dull) dark red or red purple, occasionally yellow near base.
Column pale yellow with some purple. .
Habitat and Ecology: One observation: high and wet montane forest, on the bole
of a large tree. Growing on bark covered with algae or fine moss. Alt. 1500-2000
m. Flowers not scented. Flowering May-July and October.
Distribution: Sabah. West Coast Z./Interior Z.: G. Kinabalu; Crocker Range.
General Distribution: Borneo.
Notes: B. kestron is morphologically close to B. ovalifolium (Bl.) Lindl. but can be
distinguished when looking at the margins of the lip: in B. kestron it is denticulate-
lacerate about half way the lip where the margins curve downwards, whereas in B.
ovalifolium it is always entire or at most somewhat irregular.
Some specimens of B. kestron have a relatively larger lip (compared to the lateral
sepals) than the Bornean specimens of B. ovalifolium.
The various ornamentations on the lip (ridges and verrucae) may vary conspicuously
in B. kestron. When more material becomes available probably it will show a wide
range of variation on this point, similar to that in B. ovalifolium.
The name is derived from the word ‘kestros’ which means: rough of tongue.
Bulbophyllum leproglossum J.J. Vermeulen & A. Lamb, sp. nov. Fig. 2.
Bulbophyllo ovalifolio affinis, labelli latere adaxiali duobus locis rugosis differt. Type: Borneo; Vermeulen
584 (L!).
Rhizome creeping, 0.8 mm diam. Pseudobulbs 0.3-0.7 cm apart, ovoid, flattened,
0.3-0.7 x 0.2-0.4 cm. Petiole 0.5-1 mm long. Leaves rather thick, elliptic to obovate,
0.7-2.4 x 0.4-0.7 cm, index 1.6-3.5. Inflorescence c. 6.5 cm long, 1-flowered.
Peduncle 4.5 cm. Floral bracts tubular, c. 2 mm long. Pedicel and ovary 22 mm long.
Median sepal thin, ovate, c. 6.5 x 1.8 mm, index c. 3.5, tip acute, c. glabrous.
Lateral sepals free, c. 11 x 4 mm, index 3.7, margins somewhat erose, otherwise
as the median. Petals thin, elliptic, c. 2.4 x 1 mm, index c. 2.4, tip acute, glabrous.
Lip recurved, rather thin, ovate, c. 3.6 x 1.6 mm, tip rounded, margins somewhat
erose, surface glabrous except for two rugose patches adaxially towards the margins
in the lower half. Column c. 2 mm long. Stelidia subulate, c. 1 mm long, with rather
inconspicuous, obtuse teeth along the upper as well as the lower margin. Stigma with
a distinct, obtuse basal callus. Pollinia 2. Stipes absent.
Colours: Median sepal translucent white with red veins. Lateral sepals white with
red veins. Lip dark red purple.
32 Gard. Bull. Sing. 41(2) (1988)
Fig. 1.
sepal, petal, lateral sepal, lip; d — lip, adaxial side; e — lip, abaxial side; f — column and |
lip, lateral view; g — anther, adaxial side; h — anther, abaxial side; i — pollinia. Drawn from
type specimen.
Six New Species of Bulbophyllum 33
Fig. 2.
B. leproglossum. a — habit; b — flower; c — flower analysis. From left to right: median
sepal, petal, lateral sepal, lip; d — lip, adaxial side; e — lip, abaxial side; f — column and
lip, lateral view; g — anther, adaxial side; h — anther, abaxial side; i — pollinia. Drawn from
type specimen.
34 Gard. Bull. Sing. 41(2) (1988)
Habitat and Ecology: Found in high montane forest, on mossy branch of small tree.
Alt. 1300-1500 m. Flowers not scented. Flowering observed in October.
Distribution: Sabah. Interior Z.: Ulu Padas.
General Distribution: Borneo.
Notes: B. leproglossum is a species close to B. ovalifolium (Bl.) Lindl. It can be
distinguished by the general shape of the lip and in particular by the two patches
of rough texture in the lower half of the lip (take care with shriveled herbarium
specimens, in which these patches may not be very distinct). The colour, however
characteristic it seems, is not diagnostic: similarly coloured specimens of B. ovalifolium
have been found, be it only outside Borneo so far.
Its name has been derived from ‘lepros’: rough, glossa: tongue.
Bulbophyllum nubinatum J.J. Vermeulen, sp. nov. Fig. 3.
In sectione Monilibulbo floribus magnis, sepalis lateralibus 1-2.5 cm longis, labello gracilissimo distincta.
Type: Borneo; Chan 63/87 (Holo- L!, iso- K!, SNP!).
Rhizome creeping, 0.8-1 mm diam. Pseudobulbs 0.3-0.6 cm apart, ovoid to ellip-
soid, flattened, 0.2-0.6 x 0.15-0.2 cm. Petiole 0.5-1 mm long. Leaves rather thin,
ovate to elliptic, 0.6-2.2 x 0.2-0.6 cm, index 2-8. Inflorescence c. 7 cm long,
1-flowered. Peduncle c. 5 cm. Floral bracts tubular, 2.2-3 mm long. Pedicel and ovary
8-15 mm long. Median sepal thin, ovate, 9-21 x 1-3 mm, index 7-16, tip subacute,
glabrous. Lateral sepals free, 10-20.5 x 1.5-2.8 mm, index 4-13, otherwise as the
median. Petals thin, elliptic to obovate, 1.5-4 x 0.7-1.5 mm, index 2-2.5, tip ob-
tuse to acute, margins glabrous to coarsely erose, surface glabrous. Lip recurved,
rather thick, c. ovate with a slightly widened top part (c. elliptic when spread), 2.8-5.5
x 0.9-1.2 mm, with a callus towards the base which is thickest along the margins,
tip obtuse, margins somewhat erose towards the tip and the base, surface glabrous.
Column 0.7-1 mm long. Stelidia inconspicuous, deltoid, obtuse, without teeth along
the upper or lower margins. Stigma with a small toothlike callus at the base. Pollinia -
2. Stipes absent.
Colours: Flowers entirely (orange) yellow.
Habitat and Ecology: Upper montane Dacrydium-Leptospermum forest; upper mon-
tane forest on ultrabasic soil. Alt. 2000-3000 m. Flowers not scented. Flowering
observed in March, June and August.
Distribution: Sabah. West Coast. Z./Interior Z.: G. Kinabalu.
Notes: B. nubinatum is well characterized by the shape of the lip: long and narrow,
with recurved margins half way and a flat, wider top part.
The name ‘nubinatum’, born in the clouds, refers to the high altitudes at which
the species grows.
Bulbophyllum pelicanopsis J.J. Vermeulen & A. Lamb, sp. nov. Fig. 4.
In sectione Monilibulbo sepalis lateralibus ellipticis connatis et labello elliptico distincta. Zype: Borneo;
Vermeulen 582 (L!). Plate 4.
Rhizome creeping, c. 0.6 mm diam. Pseudobulbs 0.15-0.6 cm apart, ellipsoid, flat-
tened, 0.15-0.6 x 0.15-0.22 cm. Petiole 0.2-0.3 mm long. Leaves rather thin, ovate, —
0.3-0.4 x 0.25-0.3 cm, index 1-1.5. Inflorescence 1-1.2 cm long, 1-flowered. Pedun-—
cle 0.7 cm. Floral bracts tubular, 0.8-1 mm long. Pedicel and ovary 2-3 mm long. —
Median sepal thin with distinctly thickened top part, obovate-spathulate, 2.5-4.2 x 1
Six New Species of Bulbophyllum 35
Fig. 3. B. nubinatum. a — habit; b — flower; c — flower analysis. From left to right: median sepal,
petal, lateral sepal, lip; d — lip, adaxial side; e — lip, abaxial side; f — column and lip, lateral
view; g — anther, adaxial side; h — anther, abaxial side. Drawn from type specimen.
36 Gard. Bull. Sing. 41(2) (1988)
2mm
Fig. 4. B. pelicanopsis. a — habit; b — part of plant; c — flower analysis. From left to right: median
sepal, petal, lateral sepal, lip; d — lip, adaxial side; e — lip, abaxial side; f — column and
lip, lateral view; g — anther, adaxial side; h — anther, abaxial side; i — pollinia. Drawn from
type specimen.
Six New Species of Bulbophyllum 37
1-1.4 mm, index 2.5-3, tip rounded to subacute, glabrous. Lateral sepals adnate,
thin, elliptic, 4-7 x 2-3 mm, index 2-2.5, tip cuspidate, glabrous. Petals thin, ovate,
1-2 x c. 0.3 mm, index 3.3-7, tip acute, glabrous. Lip not recurved, thin, elliptic,
2.2-3.2 x 1.5-2 mm, tip rounded, almost entirely finely papillose. Column 1-1.5
mm long. Stelidia inconspicuous, deltoid, obtuse, without teeth along the upper or
lower margins. Stigma without basal callus. Pollinia 2. Stipes absent.
Colours: Median sepal pale yellow, brownish orange at the tip. Lateral sepals, petals
and lip white.
Habitat and Ecology: Observed in high montane Agathis-Lithocarpus forest on a
ridge, on the bole of a large tree, near the forest floor. Growing among fine moss of
exactly the same colour. Alt. 1200-1500 m. Flowers not scented. Flowering observed
in October.
Distribution: Sabah. West Coast Z./Interior Z.: G. Kinabalu; Crocker Range; Ulu
Padas.
Notes: Within sect. Monilibulbus, B. pelicanopsis shares the connate lateral sepals
with B. connatum Carr. It can be distinguished by the acute, not caudate lateral
sepals. Unique in B. pelicanopsis is the spathulate median sepal.
The name ‘pelicanopsis’, ‘like a pelican’ is given because the flowers look like the
head of a pelican, with a narrow upper beak and a much wider lower one.
Bulbophyllum scabrum J.J. Vermeulen & A. Lamb, sp. nov. Fig. 5.
Bulbophyllo phaeoneuron similis, sepalis latere abaxiali et marginibus papillosis insigne. Zype: Borneo;
Vermeulen 483 (L!).
Rhizome creeping, c. 1 mm diam. Pseudobulbs 0.25-0.5 cm apart, ellipsoid to
orbicular, somewhat flattened, 0.25-0.5 x 0.25-0.5 cm. Petiole 0.2-0.5 mm long.
Leaves thick, ovate to elliptic, 0.5-1.8 x 0.4-0.5 cm, index 1.2-3.6. Inflorescence
1 cm long, 1-flowered. Peduncle 0.3 cm. Floral bracts tubular, c. 2 mm long.
Pedicel and ovary c. 4.5 mm long. Median sepal rather thin, ovate to elliptic,
c. 4 x 3.2 mm, index c. 1.2, tip cuspidate, margins papillose, abaxial surface
irregularly papillose. Lateral sepals free, rather thick, ovate, 4 x 3.4 mm, index
c. 1.2, margins somewhat erose, papillose, otherwise as the median. Petals thin,
ovate, c. 1 X 1 mm, indexc. 1, tip subacute, glabrous. Lip with a recurved top part,
very thick, obovate, c. 2.3 x 1.6 mm, adaxially with 2 short, rounded keels near
the base, tip rounded, glabrous. Column 0.8 mm long. Stelidia triangular, 0.2 mm
long, without teeth along the margins. Stigma with a large basal callus. Pollinia 4,
of unequal size. Stipes absent.
Colours: Median sepal and petals translucent with orange veins. Lateral sepals bright
orange red. Lip dark red. Column greenish.
Habitat and Ecology: One observation: Montane Fagaceae-Dacrydium-Leptospermum
forest, growing in dense mats on a large branch. Alt. 1500 m. Flowers not scented.
Flowering observed in October.
Distribution: Sabah. West Coast Z./Interior Z.: G. Kinabalu.
Notes: B. scabrum is characterized by the very short inflorescence, just as B
phaeoneuron Schltr from Sumatra and Borneo. It differs from this species in the partly
papillose sepals and in the shape of the lip which is gradually recurved towards the
tip and which has distinctly sinuose margins. Some specimens of B. ovalifolium (B1.)
38 Gard. Bull. Sing. 41(2) (1988)
1 mm
Fig. 5. B. scabrum. a — habit; b — part of plant; c — flower analysis. From left to right: median
sepal, petal, lateral sepal, lip; d — lip, adaxial side; e — lip, abaxial side; f — column and ©
lip, lateral view; g — anther, adaxial side; h — anther, abaxial side; i — pollinia. Drawn from
type specimen.
39
Six New Species of Bulbophyllum
5mm
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vVYrveEeie
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B. thymophorum. a — habit; b — part of plant; c — flower analysis. From left to right:
median sepal, petal, lateral sepal, lip; d — lip, adaxial side; e — lip, abaxial side; f — column
and lip, lateral view; g — anther, adaxial side; h — anther, abaxial side; i — pollinia. Drawn
Fig. 6.
from type specimen.
40 Gard. Bull. Sing. 41(2) (1988)
Lindl., a species which has been found on Borneo as well, have lips with similarly
sinuose margins but a much longer inflorescence.
The name ‘scabrum’, ‘rough’ is given because of the papillose margins and abax-
ial surface of the sepals.
Bulbophyllum thymophorum J.J. Vermeulen & A. Lamb, sp. nov. Fig. 6.
In sectione Monilibulbo labelli vitta centrali paulo elata distincta. Type: Borneo; Lamb 564/86 (K!).
Rhizome creeping, c. 0.8 mm diam. Pseudobulbs 0.2-0.4 cm apart, ovoid,
somewhat flattened, 0.2-0.4 x 0.25-0.35 cm. Petiole 0.6-1 mm long. Leaves rather
thin, ovate to elliptic, 0.9-1.5 x 0.2-0.35 cm, index 3-4. Inflorescence 3-3.5 cm long,
1-flowered. Peduncle 2.1-2.8 cm. Floral bracts tubular, c. 2 mm long. Pedicel and
ovary 9-12 mm long. Median sepal thin, ovate, 5-5.8 x 2-3.4 mm, index 1.7-2.5,
tip acuminate, margins finely erose, papillose, surface glabrous, abaxially somewhat
papillose. Lateral sepals free, 11-13 x 2-3.8 mm, index 4-5.5, tip obtuse, otherwise
as the median. Petals thin, elliptic, 2.2-3.1 x 0.2-0.3 mm, index 10-11, tip acute,
glabrous. Lip somewhat recurved, rather thick, obovate, 2.8-3.8 x 0.8-1.5 mm, tip
rounded, margins somewhat erose, adaxially with a slightly thickened median ridge
towards the tip, surface coarsely verrucate along the median line, finely verrucate-
papillose towards the margins. Column 2-2.2 mm long. Stelidia inconspicuous,
rounded, margins deeply erose-denticulate, lower margin with a deltoid, acute tooth.
Stigma without basal callus. Pollinia 2. Stipes absent.
Colours: Median sepal translucent white to orange, with orange veins. Lateral sepals
almost white, veins brown purple. Petals white. Lip purple to very dark red. Column
white.
Habitat and Ecology: High, wet or dry montane forest, on trunks and large branches
of canopy trees. Alt. 1700-1900 m. Flowers with a faint, unpleasant smell. Flower-
ing observed in June-July.
Distribution: Sabah. West Coast Z./Interior Z.: Crocker Range.
Notes: B. thymophorum can be recognized easily because of the slightly elevated,
verrucose-papillose longitudinal strip over the median part of the lip, which is well
separated from the much less textured lateral sides. The name refers to ‘thymos’
meaning wart.
Acknowledgements
Thanks are due to Mr P.C. Van Welzen for critically reading the manuscript.
References
Burns-Balogh, P. & Funk, V.A. (1986). A Phylogenetic Analysis of the Orchidaceae.
Smithsonian Contributions to Botany 61, 1-71.
Holttum, R.E. (1957). Orchids of Malaya. Flora of Malaya I. 2nd ed., 1-759.
Schlechter, R. (1911-1914). Die Orchidaceen von Deutsch Neu-Guinea. Fedde, Rep.,
Beih. I. 1-1041.
Seidenfaden, G. (1979). Orchid Genera in Thailand VIII: Bulbophyllum. Dansk Bot.
Ark. 33: 7-228.
Six New Species of Bulbophyllum 4]
Smith, J.J. (1905). Die Orchideen von Java. Flora Buitenzorg 6. 1-672.
Steenis, Van, C.G.G.J. (1948). Introduction to Flora Malesiana 1, 4, p. II-XII.
Vermeulen, J.J. & Lamb, A. (1988). Bulbophyllum — some interesting novelties from
the Bornean jungle. Mal. Orch. Rev. 22. 44-47.
herr bas und on Be
ah ‘Ret FA, ere ti rx pat epee. a ‘;
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wees.
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Three New Taxa in Elaeocarpus in the Malay Peninsula
F.S.P. NG
Forest Research Institute Malaysia
Kepong, 52109 Kuala Lumpur, Malaysia
EFFECTIVE PUBLICATION DATE: 10 MAR 1989
Abstract
Upon completion of a revision of the Elaeocarpaceae for the Tree Flora of Malaya Vol 4, which will
be published in early 1989, two new species and a new variety were uncovered. These are Elaeocarpus
sallehiana, E. symingtonii and E. nitidus var. velutinus, described below.
The total number of Elaeocarpus spp. recognised in the Peninsula now stands at
27 compared to the 26 in Ridley’s Flora of the Malay Peninsula 1(1922) 308-321 and
31 in Corner’s revision in the Gardens’ Bulletin Straits Settlements 10(1939) 308-329.
Elaeocarpus sallehiana Ng sp. nov.
Arbor mediocris usque 30 alta, ambitu 1.2 m. Truncus in sectione interdum irregularis, interdum
anteridibus angustis rectis usque | m altis. Cortex brunneus, laevis; stratura interiore rubro-brunnea. Lignum
vivens album usque cremeum. Partes ramulorum foliaceorum 0.15-0.3 cm diametro; ramuli cum petiolis,
faciebus foliorum inferioribus et inflorescentiis dense velutini; stipuli minutis, triangulares, caduci. Folia
plus spiraliter quam alternatim disposita; laminae ovatae usque ellipticae, coriaceae, 4.8 x 2.3 — 12.5
x 5.5 cm, apice acuminato, basi cuneata, marginibus obscure dentatis, nervis secondariis 4-7 jugis,
nervis tertiariis transversis; petioli 2-4 cm, leniter geniculati. Racemi 3-8 cm longi, plerumque in axillis
foliorum etiam praesentium orti. Flores bracteis + persistentibus villosis 0.3-1 cm longis subtenti, 5-meri;
petala 0.3 cm longa; stamina 15; ovarium sericeum; pedicelli 0.2-0.3 cm longi. Fructus ellipsoidei usque
obovoidei, in sicco durescentes, tenuiter pilosi, usque 2.2 x 1.9 cm.
Medium trees to 30 m tall. Similar to some variants of FE. stipularis (which it resembles
in the hairiness of the twigs, the deeply fimbriate petals and S-locular ovary) but
distinguishable in the absence of leafy stipules, presence of semipersistent bracts
subtending the flowers, the fewer stamens (15, not 30-35), and the hairy fruits.
Distribution: Trengganu (KEP 79597, FRI 2614, 10782, 12750, 12788), Pahang (FRI
15368). In hill and mountain forests at 210-1070 m.
Holotype: FRI 12788 in Hb. KEP! Isotypes: K, L, SING, ARN.
The species is named after Dr. Salleh Mohd Nor, Director General of the Forest
Research Institute Malaysia (Kepong).
Elaeocarpus symingtonii Ng sp. nov.
Arbor parva usque 7 m alta. Partes ramulorum foliaceorum 0.4-0.8 cm diametro, apicibus interdum
resinosis. Laminae foliorum ellipticae usque oblongo-ellipticae, tenuiter coriaceae, 10 x 4 — 21 x 10cm,
glabrae, apice acuto usque acuminato, basi rotundata usque obtuse cuneata, dentibus marginis 1.5-4 per
cm, nervis secondariis 8-12 jugis, nervis tertiariis reticulatis usque approximate transversis; petioli 6-14 cm
longi, valde geniculati. Racemi 7-15 cm longi, in axillis foliorum etiam praesentium orti. Flores 4-meri;
petala c. 0.5 cm longa; stamina c. 30; ovarium sericeum; pedicelli 0.6-0.9 cm longi. Fructus ignoti.
Small trees to 7 m tall.
43
44 Gard. Bull. Sing. 41(2) (1988)
Distribution: Perak (FRI 6143), Trengganu (FRI 1209]), Pahang (KEP 31009), in
summit forests at 1400 m and above.
Holotype: FRI 6143 in Hb KEP! Isotypes: K, L, SING, ARN.
This species is named after C.F. Symington, Forest Botanist at the Forest Research
Institute (Kepong) before the Second World War.
E. nitidus Jack var. velutinus Ng var. nov.
Arbor mediocris, usque 21 m alta, ambitu 1.2 m, cum anteridibus rectis vel gralliformibus. A var.
nitido foliis infra dense et minute velutinis, petiolis 1.5—4.5 cm longis, fructibus paullo longioribus quam
latioribus.
Medium tree to 21 m tall, differing from the typical variety in the leaves densely
finely velvety below (instead of glabrous) and the fruits a little longer than wide
(instead of globose).
Distribution: Kelantan (FRI 12464), Pahang (FRI 16594), Johore (FRI 12382), in hill
and mountain forests at 820-1528 m.
Holotype: FRI 12382 in Hb. KEP! Isotypes: K, L, SING.
Acknowledgements
I am grateful to Mr. M.J.E. Coode of the Royal Botanic Gardens, Kew, for the
translation of my descriptions into botanical Latin.
A New Species of Adiantum from Trus Madi Range, Sabah
AZIZ BIDIN!, RAZALI JAMAN? and KAMARUDDIN MAT SALLEH?
1 & 2Botany Department, Faculty of Life Sciences
Universiti Kebangsaan Malaysia, 43600 Bangi
Selangor, Malaysia
3Biology Department, Faculty of Science and Natural Resources,
Sabah Campus, Kota Kinabalu, Sabah, Malaysia
EFFECTIVE PUBLICATION DATE: 10 MAR 1989
Abstract
Adiantum lamrianum Aziz Bidin and Razali Jaman is described as a new species. It is found in un-
disturbed forest of Trus Madi Range, Sabah.
Introduction
The flora of Sabah has been of great interest among botanists since Hugh Low
first reached the summit of Mount Kinabalu on 11 March 1851. Since then many
more expeditions have been carried out mainly to collect plants along the trail to
Kinabalu Peak. Among the notable accounts and collections were those of O. Stapf
in 1894 (Cockburn, 1978); L. Gibbs and D.R. Maxwell in 1910, J. Clemens and R.E.
Holttum in 1931 (Jenkins, 1978) and more recently J.H. Beaman in 1983-1984 (Price,
1987), who collected at various localities along the Crocker Range which extends from
Northeastern Sarawak to Northern Sabah including Mt. Kinabalu. Meanwhile, the
southern portion of Borneo (Kalimantan Indonesia) has been extensively surveyed
by a group of Japanese workers in collaboration with their Indonesian counterparts
at LIPI, Bogor. Their total collection amounted to more than 15,000 numbers of
vascular plants and a vast number of bryophytes and lichens (Iwatsuki ef a/., 1980;
Iwatsuki & Kato, 1980a, & b, 1981 and 1983a & b). Recently in the course of prepar-
ing a general account of the ferns of the Trus Madi and Crocker Ranges, Sabah,
the authors came across a number of specimens that could not be matched with other
Bornean or Malesian materials. One of the species, belonging to the genus Adian-
tum, is described in the present paper. This particular species is from a medium eleva-
tion hill dipterocarp forest on the eastern slope of Trus Madi Range, where it was
collected from an extensive population on the rocky bank of a small river.
Description of the New Species
Adiantum lamrianum Aziz Bidin & Razali Jaman, sp. nov. Fig. 1.
Rhizoma breve, erectum, basibus stipitum aggregatis, ad apicem squamatum; squamae triangulares
vel lanceolatae, ad 1 mm longae, c. 0.1 mm latae, atrobrunneae; stipes usque ad 4 cm longus, ater vel
atrobrunneus, sulcatus, nitidus, glaber praeter basem sparsim squamatam; filum xylematis parum sur-
sum curvum ubique; lamina oblonga vel lineariovata, pinnata, pinnae ad c. septem pares et pinna ter-
minalis, petiolatae, alternatae, in amplitudine similes sed infimae curtiores et flabellatae, dispositae arcte
sednon imbricatae, costa carentes, ad marginem basiscopicam rectaevel parum deorsum curvae, ad marginem
acroscopicam ad distalem incisae sed non profunde, tamen lobatae, in textura herbaceae vel tenuiter her-
baceae, parce hirsutae, pilis uniseriatis atrobrunneis 0.3-1.0 mm longis, praeditae, venae dersae, ad paginam
45
Gard. Bull. Sing. 41(2) (1988)
Oo 5cm
Osh *0% tas
Be@s\°4,50>
CRNA
SY
Fig. 1: © Adiantum lamrianum from Trus Madi, Sabah (KMS 2005, UKMB)
1A. Complete adult frond. IF. Scale of stipe base.
1B. Details of pinna shape. 1G. Scale of rhizome.
1C. Matured sporangium. 1H-1K. Stelar system of stipe.
1D. Spore. IL. Stomatal arrangement of pinna.
1E. Uniseriate hair of pinna. IM. Detailed structure of indusium.
A New Species of Adiantum 47
superam et paginam infernam distinctae; sori usque ad sex in quoque pinna, unus in quoque sinu; indusia
suborbiculares ad reniformes, usque ad 1 mm longa, 0.05 mm lata, hirsuta, pilis uniseriatis atrobrunneis
c. 0.3 mm longis praedita, cellulae indusii irregularer forma, parietibus cellularum undulatis.
Rhizome short, erect, petiole-bases crowded, scaly at apex; scales triangulate to
lanceolate, to 1 mm long, about 0.1 mm broad, dark-brown; stipe up to 4 cm long,
blackish to dark-brown, grooved, polished, glabrous except for the sparsely scaly
base, xylem strand slightly curved upward throughout; lamina oblong to linear-ovate,
pinnate, to about 7 pairs with an ultimate pinna, petiolate, alternate, all about the
same size except for the lowest shorter and flabellate, closely spaced but not im-
bricate, without costa, basiscopic margins straight or slightly curved downward,
acroscopic and distal margins incised but not very deep, yet forming lobes, her-
baceous or thinner, sparsely hairy with uniseriate dark-brown hairs about 0.3-1.0 mm
long, veins dense, distinct on upper and lower surface; sori to six for each pinna,
one for each sinus; indusia suborbicular to reniform, up to 1 mm long, 0.05 mm
broad, hairy with uniseriate dark-brown hairs, hairs about 0.3 mm long, ground cells
of irregular shape with undulating cell walls (Fig. 1).
Sabah. Trus Madi Range eastern slope, Kaintanu Besar River, on steep rocky slope
of riverine forest of hill dipterocarp, dominated by Shorea laevis and Shorea mon-
ticola, 12 Nov. 1987, K. Mat Salleh & Zainiruddin H. Harith, KMS 2005 (Holotype
UKMB, isotypes UKMS, SING.).
This species is named in honour of Mr. Lamri bin Ali, Director of Park, Sabah
in recognition of his continuous support and cooperation in helping to organize a
number of field surveys in Sabah especially in the Trus Madi and Crocker Ranges.
Observations
This species has so far not been found elsewhere on both Trus Madi and Crocker
Ranges. Based on his studies on the indusial character of more than 70 species of
Adiantum worldwide, the senior author has utilised hairy versus glabrate indusium
as the first segregating factor for the genus (Bidin, 1980).
Of the eight species of Adiantum with hairy indusia, only three species from the
Malayan-Bornean region belong to the group, namely A. diaphanum, A. hispidulum
and A. caudatum. The new species shows a similar habit where the outer surface
of the indusium is hairy with uniseriate or single-celled hairs (Fig. 1M), similar to
those found on both surfaces of the pinna. The indusium is composed of uniform
ground cells of irregular shape with undulating cell walls (Fig. 1M), resembling the
pattern found in A. hispidulum (Bidin, 1980).
The stelar system in the stipe of Adiantum consists of one or two traces which
are usually arranged in an adaxially curved arc and shows a wide range of variations.
Based on observation of the xylem configurations of the stipe in 46 species of Adian-
tum from different geographical areas, Bidin (1985) subdivided the genus into 8
groups. Sections made at three different places of the stipe (base, middle and upper)
revealed that the new species belongs to the ‘‘slightly curved-upward’’ group to which
A. diaphanum also belongs (Fig. 1H-1K).
Acknowledgements
We would like to thank En. Lamri bin Ali, the Director of Sabah Park for much
help during our several visits to Sabah. We are grateful also to Dr. Ghazali bin Ismail
and En. Rahim bin Sidek of the Universiti Kebangsaan Malaysia Sabah Campus and
48 Gard. Bull. Sing. 41(2) (1988)
Sabah Park Headquarters at Kota Kinabalu respectively for their continuous sup-
port and interest in the field. To Dr. B. Parris of the Herbarium, Royal Botanic
Gardens, Kew we owe a special debt of gratitude for her help with the Latin descrip-
tion, and for comments on the manuscript.
References
Bidin, A. (1980). Studies in the Fern Genus Adiantum L. Ph.D. Thesis, University
of Newcastle upon Tyne, United Kingdom (unpublished).
Bidin, A. (1985). Comparative Anatomy of the Stipe of the Fern Genus Adiantum
L. (Adiantaceae). Gard. Bull. 38(2): 227-233.
Cockburn, P.F. (1978). The Flora. Sabah Society Monograph 1978. The Sabah
Society, Kota Kinabalu, Sabah, Malaysia.
Jenkins, D.V. (1978). The First 100 Years. Sabah Society Monograph 1978. The Sabah
Society, Kota Kinabalu, Sabah, Malaysia.
Price, M.G. (1987). Sabah Ferns Collected by John Beaman. Contr. Univ. Mich. Herb.
16: 189-200.
Iwatsuki, K.; J.P., Mogea; G. Murata and K. Kartawinata, (1980). A Botanical Survey
in Kalimantan during 1978-1979. Acta Phytotax. Geobot. 31(1-3): 1-23.
Iwatsuki, K. & M. Kato. (1980a). Enumeration of Kalimantan Pteridophytes Col-
lected during 1978-1979 (1). Acta Phytotax. Geobot. 31(1-3): 24-43.
_____. (1980b). Enumeration of Kalimantan Pteridophytes Collected during
1978-1979 (2). Acta Phytotax. Geobot. 31(4-6): 164-181.
_____. (1981). Enumeration of Kalimantan Pteridophytes Collected during 1978-1979
(3). Acta Phytotax. Geobot. 32(1-4): 121-132.
___. (1983a). Additions to the Enumeration of East Kalimantan Pteridophytes 1.
Acta Phytotax. Geobot. 34(1-3): 55-65.
_____. (1983b). Additions to the Enumeration of East Kalimantan Pteridophytes
2. Acta Phytotax. Geobot. 34(4-6): 130-141.
Four New Taxa of Philippine Rattans (Palmae: Calamoideae)
EDWINO S. FERNANDO
Department of Forest Biological Sciences, College of Forestry,
and Museum of Natural History, University of the Philippines
at Los Bafios, College, 4031 Laguna, Philippines
EFFECTIVE PUBLICATION DATE: 10 MAR 1989
Abstract
Calamus aidae E. Fern., C. balerensis E. Fern., C. ornatus Blume var. pulverulentus E. Fern. and
Daemonorops polita E. Fern. are described as new taxa of rattans from the Philippines.
Recent intensive collection of herbarium material of rattans in the Philippines has
resulted in the discovery of undescribed taxa. There is need to provide names for
these rattans as most of them are already being commercially exploited and their
habitats are threatened. This paper is published to validate names for four new taxa.
Calamus aidae E. Fern., sp. nov. Fig. 1
Species distinctissima, inter species Philippinenses flagello cirroque carentibus, foliolis infra dense albide-
farinosis setosisque, ocrea papyracea mox fatiscenti distinguibilis. Zypus: Samar, Basey, Guirang, Rawis,
Baja-Lapis 123 (holotypus K; isotypus LBC).
Robust, solitary, pleonanthic, dioecious rattan. Stems climbing to 15 m; stem
without sheaths 2.5-4.0 cm dia., with sheaths to 6 cm dia.; internodes to 18 cm long.
Leafsheaths densely covered with creamish-green, mealy indumentum and armed
with brown, slender, narrowly laminar and acicular spines to 6.5 cm long, arranged
closely in partial whorls, those around leafsheath mouth longer, erect; the spines very
brittle and readily breaking off; knee present although hardly developed, armed as
the sheath but less densely so; ocrea to 40 cm long, 3 cm wide near the base, papery,
creamish or dirty white in colour, the proximal portion sparsely covered with brownish
indumentum and armed along the edges with acicular spines to 6 cm long, ocrea pro-
minent in newly expanded leaves, but quickly tattering and disintegrating. Leaf sub-
cirrate, to 3 m long, including petiole; cirrus none; petiole to 30 cm long, semi-circular
in transverse section, flattened to slightly concave on adaxial side, convex on abaxial
side, to 3.5 cm wide, 1.5 cm thick near base, armed with scattered, slender, laminar
spines to 5 cm long on adaxial surface and along edges, the spines decreasing in size
distally, abaxial surface generally smooth, except near the edges; petiole and rachis
covered with brownish, mealy indumentum; rachis at mid-portion nearly triangular
in section, bifacial above and armed along top edge with short rigid spines to 4 mm
long, arranged 15-25 mm apart, flattened or convex below and armed with rigid and
robust 3-hooked grapnel spines to 1.5 cm long, arranged 6-8 cm apart, becoming
2-hooked then single-hooked grapnel spines towards tip. Leaflets to 130 on each side
of the rachis, coriaceous, stiff, regularly arranged to 3 cm apart, linear-lanceolate;
adaxial surface drying pale or light greenish-yellow, glabrous, except for very short
bristles to 2 mm long and spaced to 7 mm apart along margins, transverse veinlets
prominent; abaxial surface covered with chalky-white indumentum and dense bristles
along all costae, those along the mid-costa to 4 mm long, all others generally shorter;
49
50 Gard. Bull. Sing. 41(2) (1988)
OC atih
oe.
a.
WEEE PLUGS) mm
S
atte
ILE Shere
ors e ol
ners
>
14
»' ree
Fig. 1. | Calamus aidae E. Fern. — A. leafsheath, x 2/5; B. petiole, x 2/5; C. mid-portion of leaf,
x 2/5; D. leaf apex, x 2/5; E. portion of pistillate inflorescence, x 2/5; F. portion of rachilla
with young fruits, x2 1/2. A, E, F from Baja-Lapis 123; B, C, D from Fernando 414.
Four New Taxa of Philippine Rattans 51
basal leaflets to 25 x 1.0 cm; mid-lamina leaflets to 49 x 2.2 cm, apical leaflets
to 5.5 x 0.3 cm, smaller, rudimentary leaflets often present. Staminate inflorescence
not known. Pistillate inflorescence generally ascending, to 2 m long, with up to 5
partial inflorescences spaced to 50 cm apart, decreasing in size distally; prophyll
tubular, to 20 x 1.8 cm, elliptic in section, 2-keeled, armed with scattered laminar
bulbous-based spines to 1.5 cm long, mouth of prophyll surrounded with bristles to
5 cm long; other bracts similar but decreasing in size distally and becoming less densely
armed to glabrous; peduncle c. 12 x 1 cm to the prophyll scar; partial inflorescence
to 35 cm long, bearing to 20 tubular bracts, each to 13 x 8 mm, the upper half often
tattering, unarmed and covered with creamish-green indumentum, the proximal up
to 7th bract bearing second-order branches, the succeeding and ultimate bracts bear-
ing rachillae; second-order branches to 19 cm long, with up to 11 rachillae, each to
40-90 x 3 mm, generally erect, borne above subtending bract; rachilla bearing
distichously arranged bracts, each subtending a flower pair, alveolus of sterile
staminate flower c. 1 mm dia., that of pistillate flower c. 1.5 mm dia. Sterile staminate
and pistillate flowers not known. Fruit (immature) globose, c. 7 X 6 mm, beaked;
pericarp with scales arranged to 13 vertical rows, pale yellowish-green and with pro-
minent mid-scale groove. Seed not known. Seedling leaf (eophyll) pinnate, with 5-7
pairs of leaflets, each to 35 x 2 mm, with chalky white indumentum and short bristles
along margins and midcosta on undersurface.
Distribution and Habitat: Luzon (Sorsogon Prov.), Samar, Biliran, Dinagat, and Min-
danao (Surigao Prov. and Agusan del Sur Prov.); in dipterocarp forest at c. 50-500
m alt. Endemic.
Vernacular names: Ulisi (Biliran), Ulasi (Samar), Inhian (Agusan del Sur).
Specimens examined: Luzon: Sorsogon Prov., Irosin, Mt Bulusan, E/mer 1687] (BM,
K); Samar: Basey, Guirang, Rawis, Baja-Lapis 123 (holotype K; isotype LBC); Biliran:
Naval, Mohon, Fernando 679 (LBC); Dinagat: locality not known, Ramos & Pascasio
B.S. 35250 (in part, as to portion of inflorescence only) (K); Mindanao: Surigao Prov.,
locality not known, Ponce FB. 25070 (BM, kK); Surigao del Sur Prov., Bislig, Fer-
nando 727 (LBC), Agusan del Sur Prov., Trento, Fernando 414 (K, LBC).
Calamus aidae is an unusual and very distinctive Philippine rattan in the curious
absence of either a cirrus or a flagellum, in the dense short bristles and chalky-white
indumentum on the undersurface of leaflets, and in the long, papery ocrea which
quickly disintegrates. Earlier collections of this species have been referred to either
C. discolor Mart. or C. bicolor Becc. owing to its similarly discolorous leaflets, C.
discolor, however, has distinctly ecirrate leaves and the leafsheath bears a flagellum;
C. bicolor, on the other hand, has leaves with a prominent cirrus. Features of the
inflorescence suggest that C. aidae may be related to C. inops Becc. ex Heyne of
Sulawesi (Dransfield, pers. comm.).
This species is named for Mrs Aida Baja Lapis who collected the type specimen.
Calamus balerensis E. Fern., sp. nov. Fig. 2
C. usitato Blco. affinis sed foliis subsessilibus multo brevioribus, foliolis non nisi marginibus setosis,
pagina adaxiali in sicco nitida, semine brunneo laeve differt. Zypus: Luzon, Aurora Prov., Baler, Fernando
478 (holotypus LBC; isotypus K).
Very slender, clustering, pleonanthic, dioecious rattan. Stems to 3 m long, without
sheaths 3-4 mm dia., with sheaths to 6 mm dia., internodes to 8 cm long. Leafsheaths
52 Gard. Bull. Sing. 41(2) (1988)
ris, 2. Calamus balerensis E. Fern. — A. sheathed stem with one leaf and old infructescence, x 1/2;
B. detail of rachilla, x6; C. fruit, x1 1/4; D. seed, x1 1/4. All from Fernando 478.
bright green, armed with scattered, light-brown, slender, acicular spines to 7 mm,
yellowish and broad at their base, those around leafsheath mouth longer to 18 mm,
erect; knee conspicuous, armed as the sheath; flagellum to 50 cm long, armed with
short rigid spines; ocrea inconspicuous. Leaf ecirrate, c. 14-18 cm long; petiole very
short, to 5 mm, sometimes nil; rachis angular in section, bifacial above, flattened
below and armed with solitary black-tipped, reflexed, rigid spines to 3 mm long.
Leaflets up to 8 on each side of the rachis, pendulous, irregularly arranged 2-45 mm
apart, singly or in groups of up to 4 and held in same plane, linear-lanceolate, adax-
ial surface drying glossy greyish-green, the costae on both surfaces unarmed, except
for very short bristles along the margin, becoming more conspicuous near the leaflet
tip, the bristles to 1 mm or often less; transverse veinlets prominent; basal leaflets
to 16.8 x 0.7 cm, mid-lamina leaflets to 18.4 x 0.8 cm; apical leaflets to 1.2 x
Four New Taxa of Philippine Rattans St
0.7 cm, the last pair joined to 6 mm along rachis tip. Staminate inflorescence not
known. Pistillate inflorescence pendulous, to 60 cm long, with up to 3 partial in-
florescences and terminating in a well-defined flagellum, the partial inflorescences
spaced to 15 cm apart, decreasing in size distally; prophyll tubular, to 17 x 0.3 cm,
armed with scattered short, black, rigid spines to 2 mm; other bracts similar but
decreasing in size distally; peduncle c. 16 x 0.2 cm to the prophyll scar; partial in-
florescence pendulous, to 12 cm long, with up to 6 second-order branches of which
the proximate one often bearing up to 3 rachillae, succeeding and ultimate second-
order branches as rachillae; rachilla to 25-35 x 2 mm, very slender, flexuous, bear-
ing distichously arranged, striate bracts, each subtending a flower pair, alveolus of
sterile staminate flower c. 0.5 mm dia., that of pistillate flower c. 1 mm dia. Sterile
staminate and pistillate flowers not known. Fruit globose-oblong, to 1.5 x 1 cm when
fresh, with a rather obtuse or blunt beak; pericarp with scales arranged in 15 vertical
rows, dull light-green to creamish-yellow, with light brown margins and mid-scale
groove. Seed plano-convex, to 1 x 1.2 x 0.8 cm when fresh, smooth, brown and
glossy on surface; endosperm homogenous. Seedling leaf not known.
Distribution and Habitat: Luzon (Aurora Prov.); in forest with large boulders,
facing the sea, c. 50 m alt. Endemic.
Specimens Examined: Luzon: Aurora Prov., Baler, Digisit, Fernando 478 (holotype
LBC; isotype K), Semento, Hernaez 3874 (CAHP).
This species belongs to Section Coleospathus Furt. and is closely related to C.
usitatus Blco. differing in the much shorter leaves with a very short and often absent
petiole, in the leaflets armed with short bristles only along the margins and drying
glossy on the adaxial surface, and in the seed which is brown and generally smooth
on the surface. In contrast, C. usitatus generally has longer leaves with a distinct,
well-developed petiole; the leaflets are armed with bristles on both surfaces and along
margins, and drying dull on the adaxial surface; the seed is black and with rough,
irregular surface. Furthermore, C. usitatus often has leafsheaths and petioles covered
with dull greyish-brown indumentum, a feature not found in C. balerensis. Although
C. usitatus is such a variable species, C. balerensis has characters which amply separate
it as a distinct species.
The specific epithet refers to the type locality.
Calamus ornatus Blume var. pulverulentus E. Fern., var. nov. Fig. 3
A ceteris varietatibus vaginis foliorum semper inermibus et simul petiolis, rachidibus foliorum et brac-
teis inflorescentiae indumento cineraceo-brunneo dense tectis, et squamis fructu atratis differt. Zypus: Min-
danao, Zamboanga Peninsula, La Paz, Fernando 599 (holotypus LBC; isotypus K).
Robust, clustering, pleonanthic, dioecious rattan. Stems climbing to 20 m, stem
without sheaths to 2.5 cm dia., with sheaths to 5 cm dia.; internodes to 38 cm long.
Leafsheaths completely inerm, densely covered with greyish-brown, mealy or powdery
indumentum; knee very conspicuous, unarmed as the leafsheath; ocrea scarcely
developed; flagellum to 5 m long, armed with rigid grapnel spines. Leaf subcirrate,
rarely ecirrate, to 3 m long; petiole to 30 cm long, semi-circular in transverse section,
flattened to slightly convex on adaxial side, convex on abaxial side, to 2.5 cm wide,
1.0 cm thick near base, armed with solitary rigid spines to 6 mm, only along edges
and occasionally along mid-portion on abaxial surface; petiole and rachis covered
with greyish-brown, mealy indumentum, rather thick below and along the edges; rachis
at mid-portion triangular in section, bifacial and unarmed above, flattened or slightly
convex below and armed with black, rigid, grapnel spines arranged to 4-8 cm apart.
54
Fig. 3.
Gard. Bull. Sing. 41(2) (1988)
oe:
J ae
VISAS ine ‘
SSR Re
SI23 > :
wav
~
Se CN
Ss
a
fp 7
MW
a ry
Calamus ornatus Blume var. pulverulentus E. Fern. — A. leafsheath with base of flagellum,
x 2/5; B. petiole, x 2/5; C. mid-portion of leaf, x 2/5; D. leaf apex, x 2/5; E. partial pistil-
late inflorescence, x 2/5; F. sterile staminate flower, x 3 1/3; G. pistillate flower in bud, x 3;
H. vertical section of pistillate flower in bud, x 3; I. immature fruit, 3/5. All from Fernando 599.
Four New Taxa of Philippine Rattans 55
Leaflets to 25 on each side of the rachis, arcuate, regularly arranged to 9-14 cm apart,
broadly linear-elliptic to lanceolate, generally unarmed on both surfaces except near
leaflet tip where midcosta on adaxial side and margins are armed with short spiculae
to 1.5 mm, transverse veinlets prominent; basal leaflets to 57 x 6 cm; mid-lamina
leaflets to 70 x 7 cm; apical leaflets to 15 x°1.5 cm, the terminal pair often fused
to the tip of rachis. Staminate inflorescence not known. Pistillate inflorescence
flagelliform, pendulous, to 3 m long, with up to 3 partial inflorescences and ter-
minating in a well-defined flagellum, the partial inflorescences spaced to 55 cm apart,
slightly decreasing in size distally; peduncle to 8 x 3 cm to the prophyll scar, laterally
compressed and 2-keeled, unarmed, covered with greyish-brown, mealy indumen-
tum; prophyll closely tubular to 56 x 3 cm, covered with greyish-brown, mealy in-
dumentum and generally unarmed except along edges on proximal side where sparsely
armed with bulbous-based laminar spines to 1.5 cm long; other primary bracts similar
but decreasing in size distally and completely unarmed, all other bracts similarly
covered with mealy indumentum and margins fringed with caducous cream-coloured
hairs to 3 mm; partial inflorescences to 42 cm long, arcuate, bearing to 21 reflexed
rachillae, each rachilla subtended by a tubular bract to 3.5 x 1.5 cm, decreasing
in size distally; rachilla c. 9-20 x 1 cm, robust, decreasing in length distally, and
bearing to 20 bracts, each subtending a flower pair, alveolus of sterile staminate flower
c. 2 mm dia., that of pistillate flower c. 4 mm dia. Sterile staminate flower c. 6 x
3 mm; calyx 3-lobed, with basal tube to 4 mm and triangular lobes to 1.5 mm; cor-
olla with very short basal tube and 3 petals to 4 x 2 mm; stamens 6, with filaments
to 2 mm long and anthers 1.5 x 0.5 mm; pistillode trifid to 1 mm high. Pistillate
flower c. 7 X 5 mm; calyx tubular in basal 4 mm with three triangular lobes to 3
x 2 mm; corolla with short basal tube and three petals to5 x 2.5 mm; staminodal
ring to 2.5 mm high bearing 6 minute triangular teeth; ovary c. 4 x 1.5 mm. Fruit
(immature) obovoid-ellipsoid or spindle-shaped, c. 4.2 x 2 cm, tipped with a beak
to 4mm; pericarp with scales arranged in 15 vertical rows, dark brownish-black with
darker margins and prominent mid-scale groove. Seed from immature fruit rather
angular; sarcotesta sour; endosperm homogenous. Seedling leaf not known.
Distribution and Habitat: Palawan and Mindanao (Zamboanga Peninsula); in
dipterocarp forest at c. 100-800 m alt. Endemic.
Vernacular names: Borongan (Zamboanga), Mananga (Palawan).
Specimens Examined: Palawan: Puerto Princesa, Bagumbayan, Dransfield 5486 (K,
LBC), Irawan, Madulid 1007 (K, PNH); Aborlan, Talakigan River, Hernaez 3875
(CAHP, LBC); Mindanao: Zamboanga Peninsula, Malayal, Fernando 589 (K, LBC),
La Paz, Fernando 599 (holotype LBC; isotype K).
This new variety is distinguishable from all other varieties of C. ornatus Blume
in the leafsheaths which are consistently completely unarmed and densely covered
with greyish-brown, powdery indumentum, including petioles, leaf rachis, and in-
florescence bracts, and in the dark brownish-black fruit scales. The other endemic
variety of C. ornatus in the Philippines, C. ornatus Blume var. philippinensis Becc.,
is more widespread in the islands and differs from C. ornatus var. pulverulentus in
the leafsheaths being dark green and armed with laminar spines and in the fruit
scales which are yellowish with blackish margins.
The varietal epithet refers to the powdery indumentum on the leafsheaths.
56 Gard. Bull. Sing. 41(2) (1988)
Daemonorops polita E. Fern., sp. nov. Fig. 4
Structura inflorescentiae et bracteis secondariis tertiariisque saepe findentibus D. ruptili Becc. var. ruptili
affinis sed habitu solitario, vagina folii spinis complanatis latioribus basi tumidis in verticillis partialibus
dispositis, geniculo conspicuo, foliolis confertioribus, subtus 3-nervis setosis, fructu rotundiore differt;
D. ruptili Becc. var. acaulescenti Dransf. idemque affinis sed habitu et folio differt. Zypus: Mindanao,
Zamboanga Peninsula, La Paz, Fernando 575 (holotypus LBC; isotypi BH, K).
Robust, clustering, pleonanthic, dioecious rattan. Stems climbing to 15 m, stem
without sheaths to 2.5 cm dia., with sheaths to 4 cm dia., internodes to 22 cm long.
Leafsheaths covered with reddish-brown indumentum and armed with pale yellowish,
laminar spines to 4 cm long, to 1 cm broad at base, rigid, arranged in partial whorls,
generally horizontal or reflexed; knee conspicuous, only sparsely armed with shorter
laminar spines, or generally smooth; ocrea inconspicuous. Leaf cirrate to 3 m long
including cirrus to 1 m long; cirrus armed with grapnel spines; petiole yellowish in
colour, to 20 cm long, semi-circular in section, slightly concave on adaxial side
especially near base, convex on abaxial side, to 2.5 cm wide, 1 cm thick near base,
armed with laminar spines to 3 cm long, arranged in groups along the edges and
abaxial surface and with shorter spines to 1.5 cm long on adaxial surface, all spines
on petiole decreasing in size distally; abaxial surfaces of petiole and rachis yellowish,
covered with indumentum as the leafsheath; rachis at mid-portion nearly triangular
in section, bifacial above, smooth or only sparsely armed with short spines, flattened
or convex below and armed with rigid grapnel spines to 8 cm apart. Leaflets to 85
on each side of the rachis, coriaceous, stiff, regularly arranged, rather closely set
to 1.7-2.0 cm apart, linear-lanceolate, bright green, concolorous; adaxial surface
glabrous to sparsely bristly along mid- and side costae, especially toward leaflet tip,
the margins armed with short bristles to 1 mm, often in pairs, transverse veinlets
rather indistinct; abaxial surface armed with bristles to 2 mm long, very closely set
along mid-costa and sparsely set to 3-20 mm apart along two side costae; basal leaflets
to 15 x 0.8 cm; mid-lamina leaflets to 32 x 2.7 cm, the tips often with a brittle
mucro to 1.5 cm long; apical leaflets to 25 x 1.0 cm, smaller, rudimentary leaflets
occasionally present. Staminate inflorescence erect, to 70 cm long, with up to 14 par-
tial inflorescences spaced to 4-8 cm apart, decreasing in size distally; peduncle c.
10 x 1.3 cm to the prophyll scar, flattened and 2-keeled, covered with reddish-brown
indumentum and armed with rigid laminar spines to 1.5 cm long; prophyll c. 32 x
2 cm, + woody-textured, but brittle when dry, very densely covered with reddish-
brown indumentum, only sparsely armed with short spines to 8 mm and mainly along
edges, splitting down middle portion; other primary bracts decreasing in size distally,
+ armed as the prophyll but even more sparsely so, covered with indumentum as
the prophyll; prophyll and other primary bracts subtending a partial inflorescence,
all caducous at anthesis; basal partial inflorescence to 10 cm long with up to 12
crowded rachillae, each 2.5-3.0 cm long x 0.6 cm wide, subtended by a persistent
bract with a distinct triangular limb to 1.5 cm long, often tattering, each rachilla
bearing up to 15 distichously arranged bracts, each subtending a flower, alveolus of
flower to 3 mm dia., apical partial inflorescence simple, unbranched. Staminate flower
to 6 x 3 mm, cylindrical in bud; calyx greenish, 3-lobed, with basal tube to 3 mm,
and triangular lobes to 1.5 mm; corolla yellowish-brown, with short basal tube and
3 petals to 5 x 2.5-3.0 mm; stamens 6 with free filaments, white, to 6 mm long at
anthesis, anthers yellow to 3 x 1 mm; pistillode to 2 mm long, trifid. Pistillate in-
florescence as the staminate but more robust, peduncle slightly longer, and prophyll
does not subtend a partial inflorescence; whole inflorescence arching when in fruit;
rachilla c. 4 x 0.8 cm, covered with reddish-brown indumentum, rachilla bracts with
a prominent triangular limb to 6 mm; alveolus of sterile staminate flower c. 2 mm
————
Four New Taxa of Philippine Rattans 57
Fig. 4.
Daemonorops polita E. Fern. — A. sheathed stem, x 2/5; B. petiole, x 2/5; C. mid-portion
of leaf, x 2/5; D. leaf apex with cirrus, x 2/5; E. portion of infructescence, x 2/5; F. sterile
staminate flower, x3; G. pistillate flower, x3; H. immature fruit, x1 1/4. All from
Fernando 575.
58 Gard. Bull. Sing. 41(2) (1988)
dia., that of pistillate flower c. 5 mm dia. Sterile staminate flower as the fertile but
with undeveloped anthers. Pistillate flower c. 8 x 4 mm; calyx tubular in basal
4 mm with three triangular lobes to 2 x 2.5 mm; corolla with basal tube to 2 mm
and three petals to 4 x 3 mm; staminodal ring bearing 6 teeth to 2 mm long; ovary
c. 3 x 2.5 mm with three reflexed stigmas to 2 mm long. Fruit (immature) globose,
c. 1.3 x 1.4 cm, tipped with a beak to 5 mm; pericarp with 15 vertical rows of
glossy, yellowish scales with prominent reddish-brown margins and mid-scale groove.
Seed globose, c. 1 x 1 cm; endosperm ruminate; embryo basal. Seedling leaf (eophyll)
pinnate with 6 pairs of leaflets, each c. 40 xk 4 mm.
Distribution and Habitat: Mindanao (Zamboanga Peninsula); in dipterocarp forest
at c. 600-800 m alt. Endemic.
Vernacular name: Lapa-utong.
Specimens Examined: Mindanao: Zamboanga Peninsula, La Paz, Fernando 575
‘(holotype LBC; isotypes BH, K), Fernando 719 (BH, K, LBC), Kabasalan, Dipala
Mt, Ebalo 77] (BH).
This new species clearly belongs to Section Piptospatha and is most closely similar
to D. ruptilis Becc. var. ruptilis of Borneo in the inflorescence structure and in the
persistent, often splitting secondary and tertiary bracts. It is, however, distinguished
by its generally solitary habit, in the leafsheath armed with broader-based laminar
spines arranged in partial whorls, in the more conspicuous knee, in the more closely
set regular arrangement of the leaflets, in the leaflets bristly on three nerves on the
undersurface, and in the more rounded fruit. D. polita is also similar to D. ruptilis
Becc. var. acaulescens Dransf. in the inflorescence structure and in the shape and
glossiness of the fruit but the habit is quite different.
The specific epithet refers to the polished, glossy scales of the fruit.
Acknowledgements
I should like to thank Dr John Dransfield of the Herbarium, Royal Botanic
Gardens, Kew, England, for reading and commenting on the manuscript and for
assistance with the Latin diagnoses. R.T. Camposano and E.A. Lapitan prepared
the illustrations. Field work was supported, in part, by a University of the Philip-
pines at Los Banos Basic Research Program Grant No. 85-4.
Tree Distribution Patterns
in the Bukit Timah Nature Reserve, Singapore.
FREDERICK R. SWAN, JR.*
Department of Biology, West Liberty State College,
West Liberty, West Virginia 26074, USA
Abstract
All living stems > = 2 cm dbh were marked, identified and mapped at a scale of 1 cm to 1 m in two
0.24-ha plots in the Bukit Timah Nature Reserve, Republic of Singapore. The Fern Valley plot was V-
shaped in cross-section and contained a small area of exposed bedrock and several boulders along an
ephemeral stream channel; the Jungle Fall Valley plot had no stream channel and neither exposed bedrock
nor boulders. In both plots combined (0.48 ha), there were over 290 species representing 53 families.
The two plots shared 95 species, while 76 were unique to the Fern Valley plot and 119 to the Jungle Fall
Valley plot. Fern Valley had 20% fewer species, 44% fewer stems, 23% less total basal area and 40%
fewer woody climbers >= 1.4 m tall than Jungle Fall Valley. Shallower depth to granitic bedrock in
Fern Valley is hypothesized to be a contributing factor for this difference. In both plots, the Dipterocar-
paceae had the greatest basal area and the Euphorbiaceae the greatest density and number of species.
The distributions of Shorea curtisii and Pimelodendron griffithianum along slopes in these small plots
conformed to their observed ecological preferences on a larger scale in the Malay Peninsula. The presence
of a few old trees of pioneer species with little regeneration indicated an on-going process of recovery
from disturbance during and prior to World War II.
Introduction
The purposes of this study were to compare the vegetation of two plots in the Bukit
Timah Forest Reserve, Singapore, and to analyze the distribution patterns of woody
species along elevational gradients. Because the two plots were only 250 m apart and
presumably shared a similar vegetational history, I set, out to discover how similar
they would be in species composition, stem density, total basal area and size distribu-
tions of the stems of those species represented by more than five stems or contributing
more than 0.5% of each plot’s basal area. Answers to these questions should pro-
vide a better understanding of the natural variability of the vegetation within the
reserve and a basis for prediction of future changes in species composition.
The Bukit Timah Nature Reserve was established in 1883 and covers an area of
71 ha but lacked governmental protection between 1930 and 1937 and during World
War II (Corlett 1988). The highest point on Singapore Island is located within the
reserve and has an elevation of 162.5 m. Bedrock is granite probably of post-lower
Jurassic age (Wong 1969, Hill 1973, Nature Reserves Board 1975). Ives (1977)
described the soils of Bukit Timah as belonging to the Rengam series, which is well-
drained and characterised by a dark, greyish-brown topsoil 10-20 cm deep; there is
a yellowish brown subsoil, which grades to a yellowish-red, firm horizon below 1.5 m.
* Present address: Clayton Environmental Consultants, Raritan Center, 160 Fieldcrest Ave., Edison,
New Jersey 08837, USA.
59
60
Fig. 1:
Gard. Bull. Sing. 41(2) (1988)
0) 150 200M SINGAPORE
JUNGLE \3-~%
““"\FALL VALLEY
Map of the Bukit Timah Forest Reserve showing the locations of the two 0.24 ha plots.
os
Tree Distribution Patterns in Bukit Timah Nature Reserve 61
The flora of the reserve has been intensively studied and is the source of type
specimens of many species. Hill (1977) constructed a vegetation map of Singapore
and reported the presence of 99 tree species at the Bukit Timah Forest Reserve. Wong
(1987) sampled 687 trees > = 24 inches in girth in the reserve. He reported tree den-
sities of 57 to 137 stems per acre and postulated that past harvesting of smaller stems
by residents of nearby villages could account for areas of low tree density. His total
sample of 849 trees represented 212 species, 111 genera and 44 families. Whitmore
(1984) concluded that the vegetation of the Bukit Timah Forest Reserve was an iso-
lated relict of dipterocarp forest with fewer species that would normally be present
in typical lowland tropical moist forest on the nearby Malay Peninsula. He also
described the lowland dipterocarp forests on ridges of the Malay Peninsula as being
dominated by Shorea curtisii, which forms an edaphic climax there as it does at Bukit
Timah.
The following animals were observed during sampling: Long-tailed Macaque
(Macaca fasicularis), Flying Lemur (Cynocephalus variegatus), Red-bellied Squirrel
(Callosciurus notatus), and Great Racquet-Tailed Drongo (Dicrurus paradiseus).
Materials and Methods
Design and Layout
I selected one 0.24 ha plot in Fern Valley (Fig. 1) and one about 250 m away in
Jungle Fall Valley on the bases of minimal slope, lack of excessive disturbance from
tree falls, width of more than 60 m across each valley, and absence of roads and
foot paths. Each plot was 60 by 40 m and was oriented so that the long axis was
perpendicular to the path of water drainage. Fern Valley drains to the west and Jungle
Fall Valley to the north-northeast. The vegetation of each plot was sampled by use
of six contiguous quadrats (in two rows of three quadrats) 20 m square (400 m2).
In Fern Valley, two of these quadrats were on the north side of the valley and had
slopes of 25° towards the southwest (220°). The valley bottom was on the southern
edge of these quadrats. Four quadrats were on the south side of the valley and had
slopes of 18° or less towards the northwest (320°). In Jungle Fall Valley, all six quad-
rats had slopes of 12° to 28° to the north.
Stem Measurement, Labeling and Identification
In each plot, the diameters at 1.4 m height (dbh) of all living stems > = 2 cm
dbh were measured, and a numbered aluminium tag was attached to each. I estimat-
ed stem heights and mapped the positions of all living and dead stems > = 2 cm dbh
and fallen stems >= 20 cm in diameter at a scale of 1 cm equal to | m (Figs. 2
& 3). The following plant growth forms were defined in terms of a species’ potential
adult stem diameter as follows: a species described as a treelet or shrub had stems
<= 5 cm dbh; small trees, 6-15 cm; trees, 16-30 cm; and large trees, >30 cm.
Samples of leaves and fruits were collected for later identification at the Singapore
Botanic Gardens Herbarium. Scientific nomenclature of plant species follows Keng
(1973, 1974, 1976, 1978, 1980, 1982).
Plant specimens collected from the study plots were deposited at the Department
of Botany, National University of Singapore, and their identification was verified
by Dr R.T. Corlett, a faculty member in the department. A partial set of specimens
is stored in the herbarium of the Department of Biology, West Liberty State College,
West Liberty, West Virginia 26074, USA. Copies of my field notes and maps of the
two plots are on file at the Department of Botany, National University of Singapore.
Species names with authorities are listed by family in the Appendix.
62 Gard. Bull. Sing. 41(2) (1988)
Pattern Analysis
To determine whether or not species with four or more stems per plot differed
from each other in distribution patterns along valley slopes, I used the map of each
plot to measure the distances from each stem perpendicular to the valley bottom or
drainage path (D-S) and to the point of lowest elevation (DLP). The Jungle Fall Valley
plot did not have a clearly defined valley bottom while the Fern Valley plot did. I
estimated the valley bottom in Jungle Fall Valley to be along a line from the lowest
point perpendicular to the long axis of the plot. To study other aspects of distribu-
tion patterns, the distance of each stem was measured to the nearest conspecific
(NNSS), to the nearest neighbour (NN), and to the nearest fallen stem (DNFT) > =
20 cm in diameter.
To perform regression and correlation analyses, the Daisy statistics software for
the Apple Computer, Rainbow Computing Inc., 9718 Pagoda Blvd., Pasedena,
California, USA, was used.
Results and Discussions
Differences in the Vegetation of the Two Plots
The vegetation of the Fern Valley plot was simpler in composition and structure
than that of the Jungle Fall Valley plot. While the two plots shared 95 species, 76
were unique to Fern Valley and 119 to Jungle Fall Valley. The Fern Valley plot had
20% fewer species, 44% fewer stems > = 2 cm dbh, 23% less total basal area, and
40% fewer woody climbers > = 1.4 m tall (Table 1). A comparison of the species
area curves for the two plots (Fig. 4) shows the curve for Jungle Fall Valley (bi-
variate normal correlation coefficient, r = 0.9838, cumulative number of species
versus number of 10 by 10 m quadrats) to be consistently higher than that for
Fern Valley (r = 0.9768) with the gap between the two widening after ten 100-m2
quadrats (Connor and McCoy 1979). In both plots, the Dipterocarpaceae had the
greatest basal area and the Euphorbiaceae the greatest density and number of species
(see Appendix).
The differing characteristics of the vegetation in the two plots may be due to chance
or may indicate that there are environmental differences between them. Soil depth
is a possible cause of the observed differences. Physical evidence for less soil depth
in Fern Valley includes exposed bedrock near the upper end of the plot’s stream chan-
nel and large boulders one to two metres in largest dimension lying exposed toward
the lower end of the channel (Fig. 2). About 50 m west of the Fern Valley plot, I
observed several large cracks in the soil perhaps caused by soil slippage during ex-
ceptionally heavy rains. In contrast, the Jungle Fall Valley plot contained neither
rock exposures nor soil cracks. About 2 m from the southeast corner of the Jungle
Fall Valley plot there was a circular hole of unknown origin and age, 1.3 m in diameter
and 3-4 m deep with no sign of bedrock along its sides.
Shorea curtisii (Dipterocarpaceae) had a greater basal area than any other species
in each plot (Tables 2 and 3). Of the dicotyledonous tree species capable of attaining
great size, it also had the most individuals in the 2-10 cm dbh size class. In Fern
Valley its stems grew at the highest average elevation (#20, Fig. 5), and in Jungle
Fall Valley at the ninth highest elevation (#6, Fig. 6). I assume that the elevational
gradients depicted in Figs. 5 and 6 may reflect not only water relations (with the driest
end being at the upper right corner) but also differences in soil depth, texture, chemical
composition, and a tendency for soil slippage. Whitmore (1984) noted that Shorea
curtisii characteristically grows along ridge crests between 225 and 750 m on inland
Fern Valley — Plot 4
Revised 16 Nov 1982.
Ee N Fern Valley — Plot 5
t ; = Redrawn 20 Nov 1982.
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Map of the Fern Valley plot showing the locations of all living stems >= 2 cm dbh and
fallen stems > = 20cm in diameter. The plot is 40 by 60 m as measured on the south and east
sides respectively. The west side measures slightly more than 60 m.
a ed eS Ton, Sige a i
bad)
%
\ \*
we -—---— a re ----
=
‘a
> ------g--— -A \e------
Eyre Q
TUNES Hal Vanicy Flor 10
Bukit Timah Nature Reserve
F.R. Swan Jr.
Revised 26 May 1983.
mukic Pimanh Nature Reserve
Revised 7 May 1983.
Spe ONE 3k
Estimated Dr
aina
+451
7g wf
Pr is
we ‘e if od
"90 ,
yy 7 5 1G ‘ qe
#3, 139 “l 999 0 +634 tbo tz OH Pee,
ate ciel : & Fr. y,
ows Tae £ «ry ee sin 639 rv4 ag ”y
Sod * “ 436 4) /
or] So fh eg 639 see ut oe 0 7,
ri)
“28 +2396
Map of the Jungle Fall Valley plot showing the location of all living stems > = 2 cm dbh
Fig. 3:
and fallen stems >= 20 cm in diameter. The plot is 40 by 60 m.
7
Tree Distribution Patterns in Bukit Timah Nature Reserve
Table 1
A comparison of the major features of the vegetation and soils
in the Fern Valley and Jungle Fall Valley plots.
Fern Jungle
Valley Fall
Number of species > = 2 cm dbh 171 214
Number of families 39 49
Number of individuals > = 2 cm dbh 564 1000
Total basal area (m?/ha) 22.3 28.9
% stems >= 2 cm dbh with attached climbers 25.1 39.7
>= 1.4m tall
Number of climbers > = 2 cm dbh 55 47
Number of climbers <2 cm dbh & 334 938
>= 1.4m tall
Total climbers per stem >= 2 cm dbh 0.71 0.46
Number of woody climbers > = 2 cm dbh 27 45
Number of monocot climbers > = 2 cm dbh (Palmae) 28 2
Number of monocot climbers <2 cm dbh & 11 214
>=. 1.4 m tall
CUMULATIVE NUMBER OF SPECIES
ee
o
JUNGLE FALLo
VALLEY 2
o° 0°
0° ° FERN VALLEY
+2]
a a?
Oo 24 6 8 10 12 14 16 18 20 22 24
NUMBER OF !00m* QUADRATS
Species area curves for the Fern Valley (plot F) and Jungle Fall Valley (plot J) plots.
63
64 Gard. Bull. Sing. 41(2) (1988)
mountain ranges of the Malay Peninsula and nearly down to sea level on coastal hills.
Its canopy leaves are hard and waxy and have a high albedo, giving it some drought
resistance.
Of the 25 species of greatest basal area in the Fern Valley plot (Table 2), 15 had
one or more stems > = 20 cm dbh but zero or one individual in the 2-10 cm dbh
size class. Comparable values in the Jungle Fall Valley plot were nine of 24 species
(Table 3). A study of larger plot sizes is needed to determine whether reproduction
of these species is taking place anywhere in the forest reserve under current en-
vironmental conditions.
Gironniera parvifolia (Ulmaceae) was the most numerous woody species in Jungle
Fall Valley (43 stems, Table 5) and was the eighth most numerous species in Fern
Valley (9 stems, Table 4). The largest individuals were 13 cm dbh in Jungle Fall Valley
and 79 percent of the stems were in the 2-10 cm dbh size class. In Fern Valley, the
largest stem was 17 cm dbh, and 67 percent of the stems were in the 2-10 cm dbh
size class. It occupied a central position along the elevational gradient in Fern Valley
- (#8, Fig. 5) and a slightly higher position in Jungle Fall Valley (#1, Fig. 6). Because
of its abundance under current conditions, I postulate that it is a shade tolerant species
that has increased under conditions of minimal disturbance. The same explanation
may apply to Santiria apiculata (Burseraceae), the third most abundant woody species
in Jungle Fall Valley.
Urophyllum hirsutum was the most numerous species of sapling-size woody plant
(treelet) in both plots and showed highly significant clumping by the test of Clark
and Evans (1954) (Tables 4-7). It occupied a high average slope position in both plots
(#1, Fig. 5 and #2, Fig. 6), indicating greater reproductive success than other species
under upper elevational soil conditions. :
The arborescent palm, Oncosperma horridum, and at least two species of climb-
ing palms or rattans (Calamus sp. and Daemonorops sp.) were the next most numerous |
stems in Fern Valley (Table 4). Oncosperma was not present in Jungle Fall Valley —
or its vicinity. Historical accident could have played a part in the absence of On-
cosperma from Jungle Fall Valley as well as different soil conditions.
More frequent tree falls in Fern Valley than in Jungle Fall Valley may be a factor
that has aided the growth of rattans, which were especially dense in the northwest —
portion of the Fern Valley plot around three fallen trees. During the 11 months of ©
this study, three tree falls occurred in the Fern Valley plot (one standing dead Shorea
curtisii from outside the plot and two live trees within the plot belonging to the species
Ixonanthes icosandra and Eugenia duthieana). No tree falls occurred in the Jungle
Fall Valley plot. There was no significant difference between the two plots in total
length of fallen dead stems > = 20 cm in diameter. If soils are thinner in Fern Valley
than Jungle Fall Valley, a higher rate of uprooting of live trees could be expected
to continue there.
There were large differences between the two plots in numbers of both woody
(lianes) and herbaceous climbing plants. The Jungle Fall Valley plot had 67% more
lianes > = 2 cm dbh (45 or 188/ha vs. 27 or 112/ha) and 181% more climbers
<2 cm dbh (woody and herbaceous stems = 938) than the Fern Valley plot (woody
and herbaceous stems = 334). While the Fern Valley plot had 28 climbing palms
(Calamus and Daemonorops) > = 2 cm dbh and 11 Araceous climbers <2 cm dbh,
Jungle Fall Valley had two climbing palms > = 2 cm dbh but 214 Araceous climbers
<2 cm dbh. I suggest that these differences in numbers of climbers may indicate
significant differences between the two plots in available moisture as influenced by
soil depth. Putz and Chai (1987) found 164 and 348 woody vines/ha >2 cm dbh
in hilltop and valley study plots respectively within primary dipterocarp forest in Lam-
oir National Park, Sarawak, Malaysia.
Tree Distribution Patterns in Bukit Timah Nature Reserve 65
Table 2
Distribution by size class of plant species with stems
contributing the most basal area in the Fern Valley plot.
Distribution by
Species Basal Area dbh size classes (cm)
(cm?) 2-10 10-20 20-30 30-40 40+
Shorea curtisil 9,164 5 0 0 0 1
Pertusadina eurhyncha 7,235 0 0 0 0 1
Oncosperma horridum 5,174 9 21 2 0 0
Pellacalyx saccardianus 3,494 7 | 0 1 1
Artocarpus lanceifolius 2,952 0 0 0 0 1
Dipterocarpus penangianus 1,913 4 3 | 1 0
Meiogyne virgata 1,507 0 0 0 0 1
Gluta wallichii 1,265 1 0 0 1 0
Castanopsis lucida ‘251 0 0 0 0 1
Adenanthera bicolor 1,226 0 0 0 0 1
Litsea castanea 1,140 0 0 0 0 1
Licania splendens 1,123 0 0 0 0 1
Dalbergia parviflora 759 1 1 1 0 0
Artocarpus lowii 755 0 0 0 l 0
Myristica cinnamomea 743 3 y, 1 0 0
Ixonanthes icosandra 660 0 0 ] 0 0
Calophyllum ferrugineum 651 1 0 1 0 0
Gironniera parvifolia 580 6 3 0 0 0
Santiria sp. 491 0 0 1 0 0
Eugenia longiflora 491 0 0 1 0 0
Polyalthia angustissima 469 1 0 ] 0 0
Santiria apiculata 439 5 0 1 0 0
Macaranga triloba 419 3 2 0 0 0
Tabernaemontana peduncularis 410 7 l 0 0 0
Eugenia densiflora 394 3 0 1 0 0
146 other species 8,829 445 stems in all size classes
Totals 53,534 564 stems in all size classes
66 Gard. Bull. Sing. 41(2) (1988)
Table 3
Distribution by size class of plant species with stems
contributing the most basal area in the Jungle Fall Valley plot.
Distribution by
eas micah A Sas dbh size classes (cm)
(cm?) 2-10 10-20 20-30 30-40 40+
Shorea curtisii 15,469 23 0 0 0 3
Shorea parvifolia 7,860 1 0 0 0 1
_ Shorea macroptera 7,405 2 1 1 1 1
Gluta wallichii 4,232 5 1 2 1 1
Santiria griffithi 3,087 2 0 0 1 1
Dillenia grandifolia 1,752 2 1 0 0 1
Crypteronia cumingii 1,603 2 0 0 0 l
Gironniera parvifolia 1,366 34 9 0 0 0
Ixonanthes icosandra 1,046 l 6) 2 0 0
Dacryodes sp. 962 0 0 ] 0 0
Adenanthera bicolor 908 0 0 l 0 0
Shorea gratissima 888 0 l ] 0 0
Aporusa benthamiana 836 7 l l 0 0
Planchonella maingayi 707 0 0 l 0 0
Artocarpus rigidus 707 0 0 l 0 0
Strombosia ceylanica 651 20 3 0 0 0
Cyathocalyx remuliflorus 639 9 2 0 0 0
Garcinia griffithii 601 6 0 l 0 0
Euodia glabra 589 l 0) l 0 0
Eugenia duthieana 563 7 3 0 0 0
Xylopia malayana 549 3 2 0 0 (0)
Knema laurina 542 21 l a 0 0
Memecylon megacarpum 504 4 2 0 0) 0
Scorodocarpus borneensis 452 0) l 0) 0)
Unidentified climbers 425 34 0 0 0 0
190 other species 14,920 765 stems in all size classes
Totals 69,263 1,000 stems in all size classes
Tree Distribution Patterns in Bukit Timah Nature Reserve
Table 4
Relative density and distribution by dbh size class
of the most numerous species in the Fern Valley plot.
Species
Urophyllum hirsutum
Oncosperma horridum
Calamus-Daemonorops
Ganua kingiana
Koilodepas wallichianum
Urophyllum streptopodium
Pellacalyx saccardianus
Dipterocarpus penangianus
Gironniera parvifolia
Streblus elongatus
Macaranga triloba
Urophyllum glabrum
Tabernaemontana peduncularis
Dacryodes rostrata
Knema laurina
Aporusa symplocoides
Blumeodendron tokbrai
Polyalthia sp.
Myristica cinnamomea
Shorea curtisii
Santiria apiculata
Hopea mengarawan
148 other species
Total
Relative
Density
(%)
6.2
5a
Se
4.0
RB)
2.6
1.8
1.6
1.6
1.6
1.6
ee)
| Be)
14s
15
hg
1.1
1.1
ri
et
1.1
Act
Distribution by
dbh size classes (cm)
2-10 10-20
35 0
9 21
28 0
pA) 0
19 0
14 0
7
- 3
6 3
8
7 iz
8 0
7 1
8 0
7 1
5 2
6 0
5
3 2
5 0
5 0
6 0
296 stems in all size classes
564 stems in all size classes
20+
— ne Cm Com SC 1S or OS NaN ss On Oe iN SS
67
68
Relative density and distribution by dbh size classes
of the most numerous species in the Jungle Fall Valley plot.
Species
Gironniera parvifolia
Urophyllum hirsutum
_ Santiria apiculata
Koilodepas wallichianum
Santiria laevigata
Shorea curtisii
Dyera costulata
Buchanania sessilifolia
Strombosia ceylanica
Calamus-Daemonorops
Knema laurina
Baccaurea parviflora
Phaeanthus ophthalmicus
Ganua kingiana
Popowia fusca
Ardisia teysmanniana
Pimeleodendron griffithianum
Genystylus confusus
Glycosmis chlorosperma
Calophyllum tetrapterum
Cyathocalyx remuliflorus
Myristica cinnamomea
Gynotroches axillaris
Gluta wallichii
Eugenia duthieana
190 other species
Total
Table 5
dbh size classes (cm)
Relative
Density
(%) 2-10
4.3 34
4.2 42
2.8 29
2.3 27
2.7 27
2.6 23
pe 25
a3 ae
pe 20
sue 22
pe: 21
2.0 20
1.9 20
1.8 18
1.4 17
1.3 14
1.2 11
1.1 13
1.1 12
ia 11
‘4 9
1.0 9
1.0 9
1.0 5
1.0 7
530 stems in all size classes
1,000 stems in all size classes
Gard. Bull. Sing. 41(2) (1988)
Distribution by
10-20 20+
ee ee ME OF Oe © OOOO FS OO Ww OOo OO Oo ©
See Geta Sa) ee DC Oe OS 2S OS OS LOO FOr Woe - 0 -S4e) ©
Tree Distribution Patterns in Bukit Timah Nature Reserve
Summary of clumping tests for woody species in Fern Valley with 5 or more stems. One
asterisk indicates significance at P <0.05 and two asterisks, significance at P<0.01. Three in-
dices of aggregation are compared: c — Clark and Evans (1954); I — Grieg-Smith (1982);
and z — Johnson and Zimmer (1985). Significantly negative c values indicate positive skewness
and thus clumping, while significantly positive values indicate nearest neighbour distances greater
than expected by chance.
Species
. Urophyllum hirsutum
. Oncosperma horridum
. Ganua kingiana
. Koilodepas wallichianum
. Urophyllum streptopodium
. Pellacalyx saccardianus
. Dipterocarpus penangianus
. Gironniera parvifolia
. Streblus elongatus
. Macaranga triloba
— aa
—- © OO Oon~I ND NA Bh WwW NO —
. Knema laurina
12. Urophyllum glabrum
13. Tabernaemontana peduncularis
14. Dacryodes rostrata
15. Aporusa symplocoides
16. Myristica cinnamomea
17. Blumeodendron tokbrai
18. Santiria apiculata
19. Hopea mengarawan
20. Shorea curtisii
21. Dehaasia sp.
22. Canarium sp.
23. Xanthophyllum eurhynchum
24. Ardisia teysmanniana
25. Medusanthera affinis
26. Horsfieldia sp.
Percentage clumped
+ Skewed
— Skewed
Randomly dispersed
Table 6
NAA nrnuaynnnas AW ~ CO CO CO WOO OO O O
Cc
a i
O57
OT
iS
0.87
— 0.44
O82
0.82
0.82
0.42
— 0.02
0.73
eee a
0.27
= 100
1.75
2.08*
0.57
mat gi
554
— 0.80
oot et
— 4.43**
mee
—0.12
20%
4%
76
Z
OTT
— 0.89
1°35
BY eh
— 0.56
— 0.78
0.93
— 0.63
—0.74
| ee
— 0.04
PAA: hay
ai! He
— 0.76
— 1.34
=0.35
ie
¥2,5
87.5%
I
20.54
44 .96**
8 is ine
16.59
23.54**
ao i Vea
14.65
6.70
Tota
48 .95**
tose.
13.56
7395
48.65**
12.08
40.06**
10.48
2030"
5.50
vi Eb) ina
972
6.48
2.13
5 es J
18.50**
48%
52%
Growth Form
Treelet
Tree palm
Treelet
Treelet
Treelet
“Trce
Large tree
Tree
Large tree
Small tree
ree
Treelet
Treelet
Large tree
Treelet
Tree
Large tree
Small tree
Large tree
Large tree
Tee
Tree
Tree
Small tree
Treelet
Large tree
70
of stems one metre or less from the edge of the plot.
Species
ee
OmaeAnAN AN hRWNHORK CUO WON HNN FL WN
Nem NN NN NY NY WN W
OWeaerANI A vA ff WN = ©
. Urophyllum hirsutum
. Santiria apiculata
. Santiria laevigata
. Koilodepas wallichianum
. Shorea curtisii
. Dyera costulata
. Buchanania sessilifolia
. Strombosia ceylanica
. Knema laurina
. Baccaurea parviflora
. Phaeanthus ophthalmicus
. Ganua kingiana
. Popowia fusca
. Ardisia teysmanniana
. Pimeleodendron griffithianum
. Gonystylus confusus
. Glycosmis chlorosperma
. Calophyllum tetrapterum
. Cyathocalyx remuliflorus
. Myristica cinnamomea
. Gynotroches axillaris
. Gluta wallichii
. Eugenia duthieana
. Gomphandra quadrifida
. Anisoptera megistocarpa
. Litsea accedens
. Aporusa benthamiana
. Macaranga triloba
Table 7
Summary of clumping tests for woody species in Jungle Fall Valley with 5 or more stems.
One asterisk indicates significance at P<0.05 and two asterisks, significance at P<0.01. Three
indices of aggregation are compared: c — Clark and Evans (1954); I — Grieg-Smith (1982);
and z — Johnson and Zimmer (1985). Significantly negative c values indicate positive skewness
and thus clumping, while significantly positive values indicate nearest neighbour distances greater
than expected by chance. Numbers may be slightly less than in Table 5 due to elimination
Cc
3.46**
=o
0.86
1.14
—2.44**
= 1.83
= Lé6l
—1.63
— 0.80
— 0.54
—O.25
—='3.687*
~ 2. gee
0.65
0.92
— 1.38
—2.05*
1.16
1.98*
~ 1.03
0.24
— 1.93"
0.29
1.79
0.16
3.14**
1.65
1.27
aid t
Z
17
0.96
— 0.40
— 0.81
— 0.66
— 0.36
=e
0.82
0.8
0.14
a39"
3.60**
0.14
— 0,02
0.19
0.04
0.90
—0.41
— 1.23
0.68
0.11
0.69
— 1.38
0.83
I
78.49**
30.84
36.78
28.65
26.105"
21.32
36.38
66.55*
47.14**
35.10%"
21.90
113,.26°
13.19
16.67
93 .Ocs*
50). TO"
5.33
46.76**
8.58
52.20%
38.1**
43.42**
42.46**
32.3
17.24
21.02"
62,51"
5.10
136.01 RS
(Cont'd opposite page) 4
Gard. Bull. Sing. 41(2) (1988)
Growth Form
Tree
Treelet
Small tree
. Gironniera parvifolia
Large tree
Treelet
Large tree
Large tree
Tree
Small tree
Tres
Small tree
Small tree
Treelet
Tres
Small tree
Tree
Treelet
Treelet
Tree
Tree
Tree
Tree
Large tree
Tree
Treelet
Large tree
Tree
Tree
Small tree
Tree Distribution Patterns in Bukit Timah Nature Reserve 71
Table 7 (Cont’d)
Species n Cc Zz I Growth Form
30. Payena lucida 8 B1Gt* | 0315 11.38 Treelet
31. Palaquium microphyllum 8 2.18* 0.25 19.26** — Tree
32. Ardisia colorata 8 1.07 — 1.07 22.97** Small tree
33. Polyalthia sumatrana 8 0.28 0.30 51 .Ji**~ ‘Tree
34. Unknown Meliaceae 7 —2.36** —0.39 34.68** Tree
35. Calophyllum ferrugineum 7 1.47 — ZIT e- Tree
36. Garcinia griffithii 7 -1.26 — 8.66 Tree
37. Randia densiflora 6 0.25 0.11 34.97** Partial liana
38. Memecylon megacarpum 6 0.13 — 20.02** Treelet
39. Shorea macroptera 6 —0.31 0.004 3.03 Large tree
40. Polyalthia angustissima 6 —0.66 — 37.06** Small tree
41. Aporusa microstachya 6 1.54 —1.29 26.24** Treelet
42. Gaertnera grisea 5 0.10 — 4.67 Shrub
43. Microcos blattaefolia 5 0.71 — 3.63 Small tree
44. Eugenia longiflora 5 OMe 28 gg _ 5.39 Tree
45. Hopea mengarawan 5 —-1.45 — 0.29 Large tree
46. Archidendron sp. 5, 1.00 _— 18.19** Small tree
47. Cnestis platantha 5 -—2.91** — 1.86 Liana
48. Prunus polystachya 5 0.34 — 60.90* Tree
49. Actinodaphne malaccensis 5 —-—1.52 0.75 .J.28" «ihe
Per cent clumped 6.1% 57.1%
+ Skewed 18.4%
— Skewed 12.2%
Randomly dispersed 69.4% 93.9% 42.9%
Tests of Dispersion
There are no records of major disturbances from fire, typhoons or earthquakes
in the Bukit Timah Forest Reserve in the past 100 years. Therefore the degree of clum-
ping should be high due to the presence of regeneration patches from tree falls (Pickett
1983), the most common form of disturbance (Armesto et al. 1986).
Three tests of dispersion were used to evaluate the degree of clumping in all species
with > = 5 stems per plot [Clark and Evans (1954), Grieg-Smith (1983), and Johnson
and Zimmer (1985)]. By use of that criterion, 26 species were analysed in Fern Valley
(Table 6) and 49 in Jungle Fall Valley (Table 7). The test of Grieg-Smith (1983) declared
more species to be significantly clumped than the other two methods (48 and 57.1%
for Fern Valley and Jungle Fall Valley respectively.
Drought Deciduousness
Several species showed adaptations for deciduousness during the 1982-83 drought.
I observed one large individual of each of four species of trees, Parkia speciosa,
Anisoptera megistocarpa, Parishia sp., and Planchonella maingayi, become leafless
for a period of 3-6 weeks, and lianes also shedding many leaves. The large variation
in annual rainfall from 1969 to 1983 (4007-1642 mm/yr) probably is typical of past
§ ip Gard. Bull. Sing. 41(2) (1988)
variability. Holttum (1953) stated that over the previous 46 yr there had been 21
months with less than 6.2 cm of rain.
Future Trends in Forest Composition
The study plots and the reserve itself represent a mature phase rain forest (Whit-
more 1984) in a ‘‘state of structural and dynamic non-equilibrium’’ (Ho et al. 1987:
51, Hartshorn 1980). Features of a mature phase rain forest include abundant seedl-
ings and saplings of at least some tree species attaining the canopy, many tree, sapl-
ing and seedling size classes represented, low light intensities on the forest floor, a
lack of disturbance from fire and domestic animals, and minimal disturbance from
humans.
The small size of my study plots make it difficult to predict future changes in tree
species composition on the two areas. Reproduction of the more important tree species
must be studied over a larger area and longer period of time. Shorea curtisii dominated
_both plots in basal area and had some saplings in the smallest size class (Tables 2
and 3). However, eleven species in Fern Valley and five in Jungle Fall Valley were
represented by one large individual and no representation in the two smallest size
classes (Tables 2 and 3), while other species of mid-size and large trees were represented
by seedlings and saplings but no mature individuals, such as Pentace triptera in Fern
Valley and Santiria laevigata and Dyera costulata in Jungle Fall Valley. Wong (1987)
reported finding 3, 8 and 1 individuals of these species respectively of gbh > = 12
inches in his sample of 889 trees in a 3.24 ha area of the reserve. Dyera costulata
has been identified as a colonizer of gaps (Poore 1968) and a strong, light deman-
ding species (Whitmore 1973).
A low number of adult individuals of other known light-demanding species per-
sisted in the study plots without regeneration, such as Macaranga triloba (nine stems
in each plot), and /xonanthes icosandra, a long-lived pioneer according to Ho et al.
(1987). According to Hartshorn (1978), such tree species with little or no regenera-
tion may be gap species that are normally present in mature rain forest. Knight (1975)
concluded that the tropical forest reserve on Barro Colorado Island, Panama, had
not reached a climax equilibrium state after 130 yr of development and that in the
older part of the forest several species of trees probably depended on wind-created
canopy gaps for their persistence.
Evidence for Niche Differentiation
The graphs of slope position of 26 species in the Fern Valley plot and 49 in the
Jungle Fall Valley plot (Figs. 5 & 6) provide some evidence for niche separation of
woody species on hilly topography. These data support the position of Ashton (1976)
regarding mixed dipterocarp forest in the Malayan lowlands ‘‘that floristic variation
is unequivocally and consistently correlated principally with environmental factors,
among which physiography is clearly important.’’ Shorea curtisii, a ridgetop species
according to Whitmore (1984), occurred at a more extreme upper right position in
the Fern Valley (#20, Fig. 5) than in the Jungle Fall Valley graph (#6, Fig. 6). The
Fern Valley plot is more eroded and dissected than the Jungle Fall Valley plot and
may offer an environment more like ridgetop conditions than Jungle Fall Valley
would. Ashton (1978) described the differences between the canopy and sapling leaves
of Shorea curtisii and suggested that the mature phase canopy trees had evolved
characteristics to cope with moisture stress over a long lifetime. Dipterocarps in
Sarawak and Brunei appear to have strong site-specificity (Ashton 1964, 1969 and
Brunig 1973). .
Tree Distribution Patterns in Bukit Timah Nature Reserve 73
METRES
D-S
O 9.2 18.3 27.5 36.6 45..8
DLP —- METRES
Fig. 5: | Regression of the locations of stems of 26 woody species in the Fern Valley plot in which mean
perpendicular distance to the drainage path (D-S) is plotted against mean distance to the lowest
point in the plot (DLP). Single lines indicate one SE. Species numbers correspond to those in
Table 6. Multiple r = 0.85286, F = 32.015, 1/12 DF, P<0.002, two-sided test.
Of those species that were numerous in both plots, some displayed similar mean
elevational positions and some did not. Gironierra parvifolia (#8 in Fig. 5 and #1
in Fig. 6) occupied a similar mean elevational position to Shorea curtisii in the Jungle
Fall Valley plot, but their positions were widely separated in Fern Valley. Urophyllum
hirsutum occupied a high elevational position in both plots. Knema /aurina, listed
by Ho et al. (1987) as a common understory species of Malayan rain forests, occupied
similar central positions in both plots (#11 in Fig. 5 and #10 in Fig. 6). On the other
hand, Ardisia teysmanniana, a small tree, had a high position in Fern Valley (Fig. 5,
#24) and a low position in Jungle Fall Valley (Fig. 6, #15). Pimeleodendron grif-
fithianum occupied a low mean elevational position in Jungle Fall Valley (lower left
corner of Fig. 6, #16), presumably the wettest location. Ho et al. (1987) listed it as
a widely distributed species in lowland dipterocarp forest typically found in swampy
soils.
Differences in behavioural characteristics and environmental requirements other
than slope position may be especially important in reducing competition between two
Or more species in the same genus when these species are abundant in the same small
74 Gard. Bull. Sing. 41(2) (1988)
379 $2
2
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METRES
19.0
15.2-
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0 9.6 19.1 28.7 38.2 478
DLP —- METRES
Fig. 6: — Regression of the locations of stems of 49 woody species in the Jungle Fall Valley plot in which
mean perpendicular distance to the estimated drainage path (D-S) is plotted against mean
distance to the lowest point in the plot (DLP). Single lines indicate one SE. Species numbers
correspond to those in Table 7. Multiple r = 0.65364, F = 8.9516, 1/12 DF, P<0.05, two-sided test.
area. In the Fern Valley plot (Fig. 5), three species of Urophyllum, all treelets, (U.
hirsutum-#1, U. streptopodium-#5, and U. glabrum-#12) differed significantly in slope
position. However, two other pairs of species in Jungle Fall Valley (Eugenia
longiflora-#44, E. duthieana-#24, Ardisia colorata, #32 and A. teysmanniana-#15) did
not differ significantly in slope position between species within a genus.
The Need for Forest Conservation
Based on the 11 months I spent studying the Bukit Timah Forest Reserve, I have
become concerned that a nature reserve of only 71 ha would be in grave danger of
gradually losing its rarer species because of accidents to one or a few remaining in-
dividuals or because of poor reproduction (Lovejoy et al. 1983). According to Love-
joy and Oren (1981), there is some support for the hypothesis that small fragments
of ecosystems gradually become impoverished due to a predictable, sequential loss —
of species and possible invasion by weedy species. At Bukit Timah, the lack of the
original complement of animal species, human encroachments on the reserve due to
bull-dozing and quarrying of rock around its periphery, and intensive use as a city
park all threaten the health of this valuable, small reserve. May (1986: 1121) stated, —
Tree Distribution Patterns in Bukit Timah Nature Reserve FS
‘*in so far as any mathematical generalization exists, it is that randomly constructed
ecosystems are likely to become less stable — more prone to fluctuation and less able
to recover from disturbance — as they become more complex....”’
The number of species of animals that once dispersed seeds in the Singapore area
must be greatly reduced over that prior to 20,000 yr B.P. Absent species in the
Holocene might well include gibbons, langurs, elephants, bovids, rhinoceros, tapirs,
and pigs (Janzen 1978). Janzen (1970, 1974, 1975, 1978) has described the inter-
action of herbivores with tropical tree species, the irregular but abundant flowering
and fruiting of the dipterocarps, and their chemical defences in the form of resins
and gums. Putz (1979) stated that various animal species dispersed the seeds or fruits
of 90% of the canopy tree species at the Bukit Lanjan study area 25 km northeast
of Kuala Lumpur, Malaysia.
Ricklefs (1987) urged ecologists to study communities from a regional and historical
point of view. Broad regional processes over more than 80 million yr have produced
an unusually high diversity of flowering plant species in Southeast Asia (Fedorov
1966). Keng (1970) estimated that there are 8000 to 8500 plant species in the Malay
Peninsula. Plant conservation in Southeast Asia will require much cooperation bet-
ween Thailand, Malaysia, Singapore and Indonesia to establish a series of reserves,
each including a continuum of communities from high to low elevations and thus
to avoid the disastrous consequences of having only a small number of isolated
fragments by the 21st century.
The Republic of Singapore is on the threshold of becoming a major biotechnology
center of Southeast Asia. The more species of plants that can be grown in their natural
setting with reproductively viable populations, the greater will be the opportunities
for genetic manipulation of a vast treasure house of plant species and for future
restoration of moist tropical forest to degraded land.
It would be prudent therefore to protect and upgrade the nature reserve by the
following actions: establishment of 1) a stable buffer zone between the reserve and
rock and earth-moving activities nearby and 2) special plantations to propagate rare
species and others now extinct in Singapore so that plant species could be introduced
into suitable habitats from which they have disappeared.
The great advances that have been made in tissue culture, cell hybridization, and
genetic engineering have provided additional, urgent reasons for plant conservation
and for understanding the processes that sustain plant communities. The Republic
of Singapore has the scientific resources to capitalize on the enormous wealth of plant
species for food crops, enzymes, hormones, medicinal drugs, timber, and ornamen-
tals. Now is the time to act on the establishment, preservation and improvement of
nature reserves.
Acknowledgements
I wish to thank Professor A.N. Rao, past Chairman, and the faculty of the Depart-
ment of Botany at the National University of Singapore for their hospitality during
the author’s sabbatical year in Singapore and the National University of Singapore
for its financial support. My sabbatical year was made possible also by a grant of
half pay over a nine-month period form West Liberty State College, West Liberty,
West Virginia, USA, which is under the authority of the State of West Virginia’s
Board of Regents and by an additional grant from the West Liberty State College
Foundation. Dr R.T. Corlett provided much encouragement and assisted with final
identification of specimens. Mr Samsuri bin Ahmad performed the vital function
of initially identifying specimens. Mr J.F. Maxwell of the Singapore Botanic Gardens
76 Gard. Bull. Sing. 41(2) (1988)
Herbarium helped with selection of plot locations and identification of species of
Memecylon. Assistance with plant identification was also provided by Mr Sidek bin
Kiah of the Singapore Botanic Gardens Herbarium. Ms Jeraldine W. Dailey, Associate
Professor of Mathematics at West Liberty State College, generously gave me advice
on statistical methods. Drs Richard T. Corlett, Kimball T. Harper, Dennis H. Knight,
and Francis E. Putz critiqued earlier versions of this paper. Finally I wish to thank
my wife, Patricia L. Swan, for her help with preparation of herbarium specimens
and constant encouragement.
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Tree Distribution Patterns in Bukit Timah Nature Reserve 719
Appendix
Species names and authorities, numbers of stems and basal areas (BA-cm7*)
in the Fern Valley and Jungle Fall Valley plots.
Obsolete scientific names are in parentheses.
“ee Fern Valley Jungle Fall
No. BA No. BA
Anacardiaceae
Buchanania sessilifolia BI. ] 29 23 420
Gluta wallichii (Hk. f.) Ding Hou Z 1,265 10 4,232
Parishia sp. 2 42 4 249
Annonaceae
Cyathocalyx remuliflorus (Maingay et Hk. f. et 0 0 11 639
Thoms.) Scheff.
Meiogyne virgata (Bl.) Miq. 1 1,507 0 0
Phaeanthus ophthalmicus (Roxb. ex Don) Sincl. 1 17 19 148
Polyalthia angustissima Ridley 2 469 6 227
Polyalthia sumatrana (Miq.) Kurz. 2 172 8 153
Polyalthia sp. 6 180 0 0
Popowia fusca King 0 0 14 302
Xylopia malayana Hk. f. & Thoms. 0 0 4 549
Apocynaceae
Dyera costulata (Miq.) Hk. f. 0 0 25 402
Tabernaemontana peduncularis Wall. 8 410 0 0
Burseraceae
Canarium sp. 5 46 ] 13
Dacryodes rostrata (Bl.) H.J. Lam. 8 142 2 44
Dacryodes sp. 0 0 1 962
Santiria apiculata Benn. 6 439 28 219
Santiria griffithii (Hk. f.) Engl. 0 0 4 3,087
Santiria laevigata Bl. 1] 6 oF 258
Connaraceae
Cnestis platantha Griff. 0 0 5 28
Dilleniaceae
Dillenia grandifolia Wall. ex Hk. f. et Th. 0 0 4 1,752
Dipterocarpaceae
Anisoptera megistocarpa Sloot. 1 6 9 196
Dipterocarpus penangianus Foxw. 9 1,913 0 0
Hopea mengarawan Miq. 6 130 5 117
Shorea curtisii Dyer 6 9,164 26 15,469
Shorea gratissima (Wall. ex Kurz.) Dyer 0 0 2 888
Shorea macroptera Dyer 1 14 6 7,405
Shorea parvifolia Dyer Z 140 2 7,860
Euphorbiaceae
Aporusa benthamiana Hk. f. 0 0 9 836
Aporusa microstachya Arg. l 5 6 70
Aporusa symplocoides (Hk. f.) Gage 7 288 | 16
Baccaurea parviflora Muell. Arg. 4 139 20 19]
(Cont'd next page)
80 Gard. Bull. Sing. 41(2) (1988)
Appendix (Cont’d)
N Fern Valley Jungle Fall
bacidcis No. BA No. BA
Blumeodendron tokbrai (BI.) Kurz 6 87 Z 8
Koilodepas wallichianum Benth. f. 19 104 2a 182
Macaranga triloba Muell. Arg. 9 419 9 89
Pimeleodendron griffithianum 3 a2 12 316
(Muell. Arg.) Benth.
Fagaceae
Castanopsis lucida (Nees) Soepadmo 1 are 2 236
Gonystylacaceae
Gonystylus confusus Airy Shaw 0 0 It 92
’ Guttiferae
Calophyllum ferrugineum Ridl. 2 651 ob 110
Calophyllum tetrapterum Miq. 0 0 1] 94
Garcinia griffithii T. Anders 0 0 7 601
Lauraceae .
Actinodaphne malaccensis Hk. f. 2 32 5 23
Dehaasia sp. 5 31 0 0
Litsea accedens (Bl.) Boerl. 3 51 9 177
Litsea castanea Hk. f. l 1,140 0 0
Leguminosae
Adenanthera bicolor Moon | 1,226 1 908
Archidendron sp. 0 0 5 48
Dalbergia parviflora Roxb. 3 759 0 0
Parkia speciosa Hassk. 0 0 2 19
Linaceae
Ixonanthes icosandra Jack 1 660 3 1,046
Lythraceae
Crypteronia cumingii (Planch.) Endl. 0 0 3 1,603
var griffithii (Clarke) Osinga
Melastomataceae
Memecylon megacarpum Furtado 0 0 6 504
Meliaceae
Unidentified species | 26 7 44
Moraceae |
Artocarpus lanceifolius Roxb. | 2,952 0 0
Artocarpus lowii King 1 why 0 0
Artocarpus rigidus BI. 0 0 | 707
Streblus elongatus (Miq.) Corner 9 266 l 4
Myristicaceae
Horsfieldia sp. 5 82 2 ST
Knema laurina Warb. 8 155 22 542
Knema sp. | 10 bd] 0 .
Myristica cinnamomea King 6 743 10
(Cont'd opposite pag
Tree Distribution Patterns in Bukit Timah Nature Reserve 81
Appendix (Cont'd)
iene Fern Valley Jungle Fall
No. BA No. BA
Mpyrsinaceae
Ardisia colorata Roxb. 1 4 8 41
Ardisia teysmanniana Scheff. 5 92 13 187
Myrtaceae
Eugenia densiflora Miq. 4 394 0 0
Eugenia duthieana King 4 68 10 563
Eugenia longiflora F.-Vill. 1 491 5 329
Olacaceae
Gomphandra quadrifida (Bl.) Sleum 1 13 9 Al
Medusanthera affinis (Miers.) Sleum 5 104 0 0
Scorodocarpus borneensis Becc. 1 154 1 452
Strombosia ceylanica Gardn. 3 46 23 651
Palmae
Calamus — Daemonorops sp. 28 335 22 103
Oncosperma horridum Scheff. 10 5,174 0 0
Polygaceae
Xanthophyllum eurhynchum Miq. 5 46 ] 6
Rhizophoraceae
Gynotroches axillaris Bl. 0 0 10 348
Pellacalyx saccardianus Scort. 10 3,494 0 0
Rosaceae
Licania splendens (Korth.) Prance 1 1,123 1 5
Prunus polystachya (Hk. f.) Kalkman. 3 115 5 191
Rubiaceae
Gaertnera grisea Hk. f. ex. Clarke 4 40 5 38
Pertusadina eurhyncha (Miq.) Ridsdale 1 (PE b 1 8
(Adina rubescens Hemsl.)
Randia densiflora Benth. 1 4 6 58
Urophyllum glabrum Wall. ex. Roxb. 8 132 ] 15
Urophyllum hirsutum Hk. f. 32 231 42 406
Urophyllum streptopodium Wall. 14 106 | 5
Rutaceae
Euodia glabra (Bl.) BI. 0 0 2 589
Glycosmis chlorosperma Spr. 3 21 1] 115
Sapotaceae
Ganua kingiana (Brace) van den Assem 22 338 18 351
Palaquium microphyllum King & Gamb. 0 0 8 39
Payena lucida (Don.) DC | 6 8 58
Planchonella maingayi (Clarke) van Royen 0 0 l 706
Tiliaceae
Microcos (Grewia) blattaefolia Corner 0 0 5 90
Pentace triptera Mast. 4 20 l 23
Ulmaceae
Gironniera parvifolia Planch. 9 580 43 1,607
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Notes on the Early Exploration and Botanical Collecting
in the Endau-Rompin Area of Peninsular Malaysia
K.M. WONG!, Y.S. WONG? and L.G. SAW?
'Forestry Department, Bandar Seri Begawan 2067, Brunei Darussalam
*Malayan Nature Society, 485 Jalan 5/53
46000 Petaling Jaya, Selangor, Malaysia
3Forest Research Institute of Malaysia,
Kepong, Selangor, Malaysia
Abstract
The earliest scientific expeditions to the Endau area of Peninsular Malaysia were those by J.R. Logan
(1847), N.N. Miklucho-Maclay (1874, 1875), D.F.A. Hervey (1879) and H.W. Lake (1891), although the
first documented botanical collections from the area were made in 1892 by H.J. Kelsall during his visit
with Lake. Kelsall’s collecting localities included Gunung Janing and the Semberong River. Subsequent
botanical visits to the area were made by personnel of the Forest Department of the Straits Settlements
and Federated Malay States during the 1920s and 1930s and later by botanists and staff based at the Forest
Research Institute at Kepong, the Singapore Botanic Gardens and the University of Malaya. A list is given
of these collectors and those during expeditions organised to the Endau-Rompin area by the Malayan
Nature Society in 1985-86, their collecting localities and periods. Mention is also made of the herbaria
where these collections are curated. This information is presented as a background to future attempts
at compiling resource inventories for the Endau-Rompin area, a significant portion of which is being pro-
posed for conservation.
Introduction
Much scientific work has been carried out during the Malayan Nature Soceity’s
Malaysian Heritage and Scientific Expedition of 1985-86 to the Endau-Rompin area,
where a significant portion of the Endau River basin is being proposed for conserva-
tion. In spite of this, it is not yet possible to provide a detailed inventory of the flora
of the area, which will be important for management purposes. Botanical studies
of the area began in the 19th century and a great many visits have been made to the
area since then. This account brings together information on early exploratory visits
to the area and the numerous recent botanical surveys carried out there until the end
of the Expedition in June 1986, as a background for a comprehensive inventory of
the flora in the future.
Early Scientific Visitors to the Endau Basin
The first scientific explorations of the Endau area took place in the 19th century
when much of the Malay Peninsula was still poorly mapped. Skinner (1878), discuss-
ing the progress made in the geography of the Malay Peninsula, wrote in the Journal
of the Straits Branch of the Royal Asiatic Society: ‘‘Of these ... journey’s [sic!]
sO important to our Cartography, some record should here be made; more especially
as no account of them has been published in a permanent or generally accessible form
... But it would be invidious not to refer also to certain earlier journeys, viz., that
83
84 Gard. Bull. Sing. 41(2) (1988)
... of Mr. Logan (via Singapore, Indau, Semrong, Blumut, and Johore in 1847 ...”’
James Richardson Logan was a Scotsman and Barrister-at-Law, based in Penang
and Singapore much of the time and interested in both geology and ethnology. He
also founded the Journal of the Indian Archipelago and Eastern Asia, in which he
wrote much about the livelihood of the Jakun people of Johore (Thomson 1881).
His visit to the Endau River brought him only as far as its confluence with the
Semberong River (some 15 km eastward from the boundary of the area presently
proposed as the Endau-Rompin national park), and his exploration was mainly along
the Semberong and southwards.
In 1874 the Russian geographer-ethnologist Nikolaj Nikolajewitsch Miklucho-
Maclay undertook an exploration of epic proportions which brought him to the En-
dau River also. He set out on 15 December 1874, up the Muar River on the west
coast of the Malay Peninsula, crossed southward to the Segamat River, made his
way eastward to the Semberong River and went down the Endau River to the South
China Sea. Thereafter he returned inland, explored the Kahang and Madek rivers, and
continued southward along the Johor river to the Tebrau Straits which he reached
on 2 February 1875 (Miklucho-Maclay 1875, 1878). In June 1875, Miklucho-Maclay
embarked on a second journey, following his earlier course until the Endau-Semberong
confluence, whence he travelled some 20 km further upriver on the Endau and climbed
Gunong Janing (at the eastern boundary of the presently proposed Endau-Rompin
park). However, he did not continue further up along the Endau, but instead turned
seawards to the town of Pekan in Pahang, where he followed the Pahang river in-
land and emerged to Kota Baharu on the northeast coast, and finally inland again
before arriving at the mouth of the Patani River. At this point, in October 1875,
he was compelled to abandon the expedition because of the advancing monsoonal
rains (Miklucho-Maclay 1878). Both Logan and Miklucho-Maclay appear not to have
collected any botanical specimens from these journeys (van Steenis-Kruseman 1950).
Following this Dudley F.A. Hervey also visited the Endau area in August 1879,
three years before he was to be Resident Councillor of Malacca (Hervey 1882). He
travelled (presumably by sea) from Singapore to the mouth of the Endau River, and
coursed along it only as far as where it met the Semberong River; he, too, turned
southwards to explore the Semberong and its tributaries, the Kahang and the Madek,
and made no further exploration of the Endau River itself. Hervey collected plants
in his time, but appears not to have collected during his visit to the Endau-Semberong
area (Burkill 1927, van Steenis-Kruseman 1950).
Most familiar to botanists are Harry Lake, miner and surveyor, and H.J. Kelsall,
who was a Lieutenant with the Royal Engineers in Singapore, because of the plant
specimens collected on their journey. Lake began his exploration of the Endau River
on 13 August 1891, on instruction from the Sultan of Johor, because the Endau was
at the time poorly known and existing maps then showed the river to be comparatively
small, with its source just a little beyond G. Janing. Lake traced the source of the
Endau to a point about 44% miles (about 72 km) upstream from the Endau-
Semberong confluence, near the base of G. Besar, and crossed over to the headwaters
of the Segamat River. He continued northward to the Jekati River and eventually
emerged at Muar on the west coast in early October (Lake 1894). Lake’s expedition
appears to be the first documented crossing of the Malay Peninsula from east to west
via the Endau River; however he did not collect any plant specimens.
Lake returned with Kelsall for another cross-peninsula expedition starting from
Kuala Endau on 17 October 1892, but this time following a different route. They
went upstream on the Endau only as far as the Lemakoh River (whence Kelsall
ascended and collected plants on G. Janing), and returned to the Semberong River
Notes on Endau-Rompin Area 85
which they followed upstream, eventually passing overland to the Bekok River and
downstream to Batu Pahat on the west coast, which was reached on 5 November
1892 (Lake & Kelsall 1895). Kelsall collected plants on this expedition, mostly on
the Semberong River, but these and his collections from G. Janing are important
as reference material for the botany of the area. These specimens were presented to
the herbarium of the Singapore Botanic Gardens where H.N. Ridley was able to name
most of them (Lake & Kelsall 1895), and today these specimens are still curated in
good condition at the herbarium there. The specimens were collected by Kelsall but
are labelled ‘‘Lake and Kelsall’s collections’’; these specimens bear numbers that must
have been given after the expedition because the numbers do not chronologically follow
the dates of collection.
These are the pioneering scientific visits to the Endau area. Subsequent botanical
visits to the area now proposed as the Endau-Rompin national park and its vicinity
have not been well documented except through the plant specimens preserved in her-
baria. In our discussions here of botanical collecting trips, the area of interest is taken
as the proposed park area itself (about 45 km across at its widest east-west span)
as well as a zone of about 15 km wide immediately surrounding the proposed park.
The collecting localities of different collecting parties dealt with in this account are
shown in Fig. 1; those localities visited before the Malayan Nature Society’s 1985/1986
Endau-Rompin expedition are represented by symbols whereas collecting localities
during the Society’s expedition are represented by alphabets.
Twentieth-Century Visits: Before the 1985/86 Expedition
Probably the earliest botanical visit to the Endau-Rompin area this century was
that of J.G. Watson and Yeob Abdul Rahim, of the Forest Department of the Straits
Settlements and Federated Malay States, who in July 1923 collected plants along the
Endau River east of Kuala Jasin. It was on this trip that Watson made the first col-
lection of a riverbank shrub endemic to the Endau river basin and which was later
named Phyllanthus watsonii, after him. Other early plant collectors who visited the
area were mainly Forest Department staff, including Forest Guard Mohamud (at
Sungai Kachah Putih, a tributary of the Rompin River, January 1930), Forest Guard
Sudin (along the Sungai Anak Endau east of the proposed park area, March-
November 1933), Forest Ranger Mohamed Said (Sungai Anak Endau, May 1935)
and a number of other uniformed staff of the Forest Department (who each collected
only one or several specimens on Gunung Lesong on the northern boundary of the
proposed park area, April 1956).
Following this further botanical collections in the area were carried out by the
following parties:
K.M. Kochummen, F.S.P. Ng (Forest Botanists) of the Forest Research Institute (FRI)
at Kepong, and Forestry students of the Forest Department, July 1964, in Labis
Forest Reserve just southwest of the proposed park area;
K.M. Kochummen and T. Suppiah (Herbarium assistant) of the FRI at Kepong, April
1967, southwest of the proposed park area;
T.C. Whitmore (Colombo Plan Botanist at the FRI at Kepong), May 1967, Bukit
Peta and Sungai Endau in its vicinity;
P.F. Cockburn (British volunteer attached to the FRI at Kepong) and K. Ogata
(botanist at the Tsukuba Forestry and Forest Products Research Institute),
March-April 1968, Gunung Janing, Sungai Endau in its vicinity and Sungai Anak
Endau;
86 Gard. Bull. Sing. 41(2) (1988)
P. Selvaraj (Herbarium assistant of the FRI at Kepong), November 1968, southwest
of the proposed park area;
K.M. Kochummen, July and September 1970, southwest of the proposed park area;
T.C. Whitmore, T. Suppiah and Samsuri Ahmad (plant collector at the Singapore
Botanic Garden), February 1971, in the vicinity of Sungai Ulu Pukin and Sungai
Jekatih on the west side of the proposed park area;
Y.C. Chan (Herbarium assistant of the FRI at Kepong), March 1972, southwest of
the proposed park area; June 1972, in the vicinity of Sungai Jekatih northwest
of the proposed park area;
E.A. Heaslett (Singapore-based medical doctor and plant collector), Mohamad Shah
(Herbarium assistant at the Singapore Botanic Garden), Ahmad Shukor and Sam-
suri Ahmad (plant collectors at the Singapore Botanic Garden), July 1972, Gunung
Janing and Sungai Endau in its vicinity;
B.C. Stone (Botanist at the University of Malaya) and the Botany Class of 1973,
August 1973, Bukit Peta and Sungai Endau in its vicinity;
Mohamad Shah, November 1973, Gunung Lesong;
J. Dransfield (Botanist at the Royal Botanic Gardens, Kew), June 1977, Gunung
Janing;
Y.C. Chan and Kamarudin Saleh (Herbarium assistants at the FRI at Kepong), June
1979, in the vicinity of Sungai Jekatih northwest of the proposed park area;
K.M. Wong (Forest Botanist, FRI at Kepong), T.D. Pennington (Botanist at the Royal
Botanic Gardens, Kew) and Kamarudin Saleh, September-October 1981, Bukit
Peta and Sungai Kemelai just east of the proposed park area.
The collections of Heaslett, Mohamad Shah, Ahmad and Samsuri (July 1972) and
of Mohamad Shah (November 1973) are principally deposited in the Herbarium of
the Singapore Botanic Gardens (SING), with duplicates distributed to the herbaria
at the Forest Research Institute of Malaysia at Kepong (KEP) and the Royal Botanic
Gardens at Kew (K). Ogata’s collections are principally housed at the Tsukuba Forestry
and Forest Products Research Institute with duplicates at KEP. Pennington’s collec-
tions are housed at K, and also duplicated at KEP. The collections of Stone are
deposited in part in the Herbarium of the University of Malaya (KLU) and in the
herbarium of the Academy of Natural Sciences of Philadelphia (PH); those of the
University of Malaya 1973 Botany students who accompanied Stone are deposited
at KLU. All other collections are principally deposited at KEP with main duplicates
Figure 1. (See opposite page)
a) Chan (Mar 1972 Labis For. Res., Jun 1972 Lesong For. Res.), Chan & Kamarudin (Jun 1979),
Cockburn & Ogata (Mar-Apr 1968), L) Dransfield (Jun 1977), %& Forest Dept., various uniformed staff
(Apr 1956), ¥ Forestry Students with Kochummen & Ng (Jul 1964), O Heaslett, Mohamad Shah, Ahmad
Shukor & Samsuri Ahmad (Jul 1972), © Kelsall & Lake (Oct 1892), % Kochummen (Jul-Sep 1970), ®
Kochummen & Suppiah (Apr 1967), * Mohamud (Jan 1930), {J Mohamad Said (May 1935), 4 Mohamad
Shah (Nov 1973), + Selvaraj (Nov 1968), * Stone & University of Malaya 1973 Botany Class (Aug 1973),
© Sudin (Mar, Jun, Jul, Nov 1933), @ Watson & Yeob Abdul Rahim (Jul 1923), § Whitmore (May
1967), @ Whitmore, Samsuri & Suppiah (Feb 1971), Bd Wong, Pennington & Kamarudin (Sep-Oct 1981);
a (Base Camp & K. Jasin), b (G. Janing), c (K. Marong & K. Jasin area), all collectors who visited during
the 1985-86 expedition (see text); d (Bukit Sengongong & ‘‘Buaya Sangkut’’ falls), P. Leong, Saw, Wong,
e (Padang Temambun), Davison, B.H. Kiew, R. Kiew, Masrom, Nik Mohamed, Razali Baki, Saw, Wong,
k (K. Kemapan), B.H. Kiew, R. Kiew, Saw, Wong, m (Sg. Kinchin), B.H. Kiew, n (Sg. Selai), B.H. Kiew,
x (Kg. Peta & Sg. Endau), R. Kiew, Ng, Phang, Saw, Taylor, Wong, z (Sg. Endau between K. Kinchin
& K. Jasin), R.P. Lim.
87
Notes on Endau-Rompin Area
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88 Gard. Bull. Sing. 41(2) (1988)
distributed to the Arnold Arboretum (A), Kew (K), Leiden (L), Sandakan (SAN),
Kuching (SAR) and Singapore (SING).
As a note of interest, expeditions of a purely botanical nature have not been the
only ones made to the Endau-Rompin area. Several other visits to the area have con-
cerned the vegetation there. During 1965-1966, the Forest Research Institute’s Forest
Resources Reconnaissance Surveys of the Mersing, Rompin and Segamat districts
by Cracium (1966), Lee (1966) and Gyekis (1966), respectively, included brief stand-
assessments of the vegetation types found in the Endau-Rompin area. Flynn’s survey
of Sumatran Rhinoceros populations in the area (Flynn 1978) also included an
enumeration of plant species known to be eaten by rhinos in the area. At the peak
of concern over logging threats to the Endau-Rompin area in July 1977, three groups
of Malayan Nature Society members visited the area; one group visited the Endau-
Jasin area, another the Jemai-Kemapan area and a third carried out brief aerial surveys
over the area, although apparently few or no plant specimens were collected during
these visits.
Botanical Collecting During the 1985/86 Expedition
The Malayan Nature Society’s Malaysian Heritage and Scientific Expedition to
Endau-Rompin between June 1985 and June 1986 created the opportunity for greater
botanical exploration of the area. In particular, the establishment of a base-camp
at Kuala Jasin provided facilities for a nearly continuous stream of scientists and
nature enthusiasts throughout this period and made repeated visits by scientists at
different times of the year a convenient undertaking. The support of the Royal Malay-
sian Air Force also enabled a botanical team to be transported by helicopter to Kuala
Kemapan, at the centre of the area.
Collectors of specimens for herbaria during the Expedition may be listed under
the following institutions (the collecting periods, plant groups and herbaria where
collections are kept are indicated after collectors’ names).
(1) the Forest Research Institute of Malaysia (FRIM), Kepong (herbarium KEP) —
Aminuddin Mohamad .............. 8-11 Oct 1985; palms, KEP
K.C. Ang. <:..i.ccitee ae 9-13 Sep 1985; dicots, KEP
Kamarudin. Salet | occ: ccdvid en eegeres 21-26 Oct 1985; dicots, KEP
K.M. Kochusnigens (ii¥essicuowketecks 5-10 Aug 1985; dicots, KEP
CM. LOW ii.%)cctvededssaccueenehae 8-11 Oct 1985; palms, KEP
Mat ASthacciccisckas Oe 8-11 Oct 1985; palms, KEP
F OSE ANE ., .i cvccvsdecsescnsaaci ee 30 Jul-2 Aug 1985; dicots, ferns, KEP
Ls Gh SQW sass. tiih licen eee 5-10 Aug & 21-26 Oct 1985, 23 Apr-2 May
& 25-31 May 1986; ferns, gymnosperms,
angiosperms, KEP
MS Wiig) 5.500 i. acdsee 5-10 Aug & 21-26 Oct 1985, 23 Apr-2 May
& 23-31 May 1986; algae, bryophytes,
pteridophytes, gymnosperms, angiosperms,
KEP
8 ey a We athe ee 9-13 Sep 1985; dicots, KEP
(2) the Malaysian Agricultural Research and Development Institute (MARDI), —
Serdang — :
Abdullah Titaai 2. .cccsteaisencceddecs, 24-28 Mar 1986; orchids, aroids, MARDI ©
Wale hin: ota reaseree 24-28 Mar 1986; orchids, MARDI
Notes on Endau-Rompin Area 89
(3)
(4)
(5)
Neasten.,Hastan) .¢.. cdi Wee. ccc: 20-25 Sep 1985, 7-16 Feb 1986; monocots,
dicots, MARDI
Mishiyah Katman .................... 20-27 Sep 1985; fungi, MARDI
Mohamad Hanifah we. 02.24. 22008 7-16 Feb 1986; dicots, MARDI
Mreiamiad YASS 6.2. .0cci<0 es cwxahs 23-26 Jul 1985, 24-28 Mar 1986; orchids,
MARDI
Mohammed Harum ».2...42.)2. 00... 7-16 Feb 1986; fungi, MARDI
i. rooney Oke. kbs oi 20-25 Sep 1985; orchids, MARDI
INI APO NAME 825 io2e5, no ed. olds lee 7-16 Feb 1986; fungi, MARDI
Noorshinah Hussin .................. 20-27 Sep 1985, 7-16 Feb 1986; fungi,
MARDI
Baral Bak coc cals LAW . ater 23-26 Jul 1985, 7-16 Feb 1986; monocots,
dicots, MARDI
MOskeAsaad ) Accatioi ike ie. 2k Fase 20-25 Sep 1985; orchids, MARDI
ROzanerGhanl. 2 fii vest hk ks 20-27 Sep 1985, 7-16 Feb 1986; fungi,
MARDI
Bena LOTS. oF. 242th chet 23-26 Jul 1985; dicots, MARDI
Bema MUG 4. dctled; ssl clock 23-26 Jul & 20-27 Sep 1985; fungi, MARDI
the Universiti Kebangsaan Malaysia (UKM, National University of Malaysia),
Bangi —
a PRMISOTD (5 os oho oensnae dd ansennocen 7-16 Feb 1986; angiosperms, UPM
the University of Malaya, Kuala Lumpur (UM) (herbarium KLU) —
BPP OIAINICT cc ccinsccincsecdevenscess 26 Sep-1 Oct 1985; bryophytes, pterido-
phytes, KLU
Peete lew, AEE Le ah 2-6 Sep 1985, 20-27 Mar, 16-22 Apr &
20-28 May 1986; algae, bryophytes,
pteridophytes, angiosperms, UPM, KLU
g's 0) Oe Tn ae ee 14-18 Jun 1985, 23-31 May 1986; algae,
KLU
Rob Dis ee A 12-13 Feb 1986; algae, KLU
SA ane: Beer olds Ween Ak NS 2-7, 14-18 Jun & 25 Sep-1 Oct 1985; algae,
KLU
E. Soepadmo & students ........... 25 Sep-1 Oct 1985; gymnosperms,
angiosperms, KLU
GIP Tayior 2 Auek Pea Sa 25 Apr-2 May & 19 May-9 Jun 1986;
pteridophytes, angiosperms, KLU, KEP
the Universiti Pertanian Malaysia (UPM, Agricultural University of Malaysia),
Serdang (herbarium at Department of Biology UPM; at Forestry Faculty
UPMF) —
Se PMENOINYSAUNY occiceces cs cncccee +20. 26-30 Aug 1985, 4-6 Feb 1986; pterido-
phytes, angiosperms, UPM
Toran’ IGRAM 3.6.) 0). 000k. s6 eS 19-23 Aug 1985; angiosperms, UPMF
Jamaluddin Basharuddin ........... 19-23 Aug 1985; angiosperms, UPMF
NOW eee ee kl i von so) wo ois ae 2-7 Jun & 26 Aug-7 Sep 1985, 4-6 Feb,
16-22 Apr & 13-22 May 1986; fungi,
pteridophytes, gymnosperms, angiosperms,
UPM
NR ARUAV DI 209s 0 ois ode wn ocd sees 26-30 Aug & 2-6 Sep 1985; pteridophytes,
angiosperms, UPM
Razali Salam & students ........... 26-30 Aug 1985; angiosperms, UPM
90 Gard. Bull. Sing. 41(2) (1988)
(6) the Botanic Gardens, Singapore (herbarium SING) —
it ead |b) nnn oh 0 Ser. 25 Oct-1 Nov 1985; ferns, dicots, SING
(7) the National University of Singapore (NUS) (herbarium SINU) —
Ahmad Samsurt, 7220/55... 0.05.4. fdaks 16-20 Jun 1986; pteridophytes, angiosperms,
SINU)
| Sots =; eC eee rere. 28 Apr-2 May 1986; angiosperms, SINU
Hy AON Pos 2 GS ee eee 28 Apr-2 May 1986; angiosperms, SINU
LL Beh 2s. Soe Shee 28 Apr-2 May 1986; fungi, SINU
A.N. Rao 2 students | .2.02.1.220.8, 16-20 Jun 1986; angiosperms, SINU
Ah 5 (Ae ot ee 2 28 Apr-2 May 1986; angiosperms, SINU
H.. Tan &. Students .2ccnn.20 cece 16-20 Jun 1986; bryophytes, pteridophytes,
angiosperms, SINU
TK FAM csoeve ccnuc'enene a eee 28 Apr-2 May 1986; fungi, SINU
Y .C Wee @ students:1272. 2205 16-20 Jun 1986; pteridophytes, angiosperms,
SINU
(8) the Royal Botanic Gardens, Kew (herbarium K) —
S. Andtews: i...AKU. AP 4-7 Feb 1986; dicots, K
J: (Dransiteld > ...4-... cet 4-7 Feb 1986; palms, K
PJ. Hdwards 21.5%). sai. ite 4-7 Feb 1986; pteridophytes, K
The localities from which specimens for herbaria have been collected during the
expedition were:
(a) Kampung Peta and the Sungai Endau downstream from Kuala Jasin (eastern por-
tion of the area), by R. Kiew, Ng, Phang, Saw, Taylor, Wong.
(b) Gunung Janing and the Kuala Marong-Kuala Jasin area (eastern portion), by
all collectors except G. Davison and R.P. Lim.
(c) Bukit Sengongong and the ‘‘Buaya Sangkut’’ Falls on the Jasin River
(southeastern portion), by Leong, Saw, Wong.
(d) Padang Temambun (southeastern portion), by Davison, B.H. Kiew, R. Kiew,
Masrom, Nik Mohmed, Razali Baki, Saw, Wong.
(e) the Kuala Kemapan area and Gunung Beremban massif (central region), by B.H.
Kiew, R. Kiew, Saw, Wong.
(f) the Kinchin River valley (northeastern portion), by B.H. Kiew.
(gz) the Endau River between Kuala Kinchin and Kuala Jasin, by R.P. Lim.
(h) the Selai River valley (southwestern portion), by B.H. Kiew.
Besides specimens for herbaria, live-plant propagules were collected by a few in-
dividuals. These included the following:
pteridophytes — P. Bradley (Royal Botanic Gardens, Kew).
orchids — Abdullah Thani, W.H. Lim, Mohamad Yassin, M. Mooruthy, Rosli Asaad,
Salmah Idris (MARDI), L.G. Saw (FRIM), Shaharin Yussof (Malayan Nature
Society).
palms — Khelikuzzaman Hussain, Mohamad Nasir and Safie Hussin (MARDI), Mat
Asri and C.M. Low (FRIM), Mustapha Mohamad (UM), J.J.H. Tan (Malayan
Nature Society).
wild yams — Abdullah Thani, Khelikuzzaman Hussain, Mohamad Nasir and Safie
Hussin (MARDI).
bananas — Anthonysamy and R. Kiew (UPM), Abdul Malek and Mohamad Sham-
sudin (MARDI).
monocots other than as named above — Khelikuzzaman (MARDI), Mustapha
Mohamad (UM).
Notes on Endau-Rompin Area 9]
dicots — Mat Asri, L.G. Saw and S.K. Yap (FRIM), Abdul Malek, Khelikuzzaman
Hussain, Mohamad Nasir, Mohamad Shamsudin and Safie Hussin (MARDI),
Mustapha Mohamad and C.E. Taylor (UM), J.J.H. Tan (Malayan Nature
Society), C.J. Goh (NUS).
All of the above were collected in the vicinity of Kuala Jasin, Kuala Marong and
Gunung Janing, except those by Shaharin Yussof (which also included collections
from the vicinity of G. Tiong, the Buaya Sangkut falls on the Jasin, and Padang
Temambun) and J.J.H. Tan (which included collections from the vicinity of Kuala
Kemapan, the Buaya Sangkut falls, Padang Temambun and the Lemakoh valley).
References
Burkill, I.H. (1927). Botanical collectors, collections and collecting places in the Malay
Peninsula. Gard. Bull. S.S. 4(4 & 5): 113-202.
Cracium, G.C.J. (1966). Forest Resources Reconnaissance Survey of Malaya, no.
2. Mersing District, Johore. Forest Research Inst., Forest Department, Malaya.
Flynn, R. (1978). The Sumatran Rhinoceros in the Endau-Rompin National Park
of Peninsular Malaysia. Mal. Nat. 4(2): 5-12.
Gyekis, K.D. (1966). Forest Resources Reconnaissance Survey of Malaya, no. 7.
Segamat District, Johore. Forest Research Inst., Forest Department, Malaya.
Hervey, D.F.A. (1882). The Endau and its tributaries. J. Str. Br, Roy. As. Soc. no.
8: 93-124.
Lake, H.W. (1894). A journey to the source of the Indau. J. Str. Br, Roy. As. Soc.,
no. 25: 1-9.
Lake, H.W. & H.J. Kelsall. (1895). A journey on the Semberong River. From Kuala
Indau to Batu Pahat. J. Str. Br, Roy. As. Soc., no. 26: 1-33.
Lee, P.C. (1966). Forest Resources Reconnaissance Survey of Malaya, no. 3. Rom-
pin Forest District, Pahang. Forest Research Inst., Forest Department, Malaya.
Miklucho-Maclay, N. (1875). Ethnologische excursion in Johor. S. Natuurkundig Ti-
Jdschrift voor N. Indie, Thiel 35: 251-258.
Miklucho-Maclay, N. (1878). Dialects of the Melanesian tribes in the Malay Penin-
sula. J. Str. Br, Roy. As. Soc., no. 1: 38-44.
Skinner, A.M. (1878). Geography of the Malay Peninsula. J. Str. Br, Roy. As. Soc.,
no. 1: 52-62.
Steenis-Kruseman, M.J. van. (1950). Malaysian Plant Collectors and Collections,
being a Cyclopaedia of Botanical Exploration in Malaysia and a guide to the
concerned literature up to the year 1950. In: C.G.G.J. van Steenis (ed.), Flora
Malesiana, Series 1, Vol. 1, cliit+ 639 p.
Thomson, J.T. (1881). A sketch of the career of the late James Richardson Logan,
of Penang and Singapore. J. Str. Br, Roy. As. Soc. no. 7: 75-81.
A Further Chromosome Count for Osmmunda (Osmundales)
from Peninsular Malaysia
AZIZ BIDIN
Botany Department, Faculty of Life Sciences
Universiti Kebangsaan Malaysia, 43600 Bangi, Selangor, Malaysia
The near cosmopolitan fern genus Osmunda has been well studied cytologically.
Autotetraploid and triploid plants were experimentally produced by Manton (1950).
In Peninsular Malaysia, the genus is represented by two species, namely O. javanica
Bl. and O. vachellii Hook., and both are uncommon, restricted to a few localities
in the primary forests of Pahang. O. javanica is also found in the highlands (Cameron
Highlands and Fraser’s Hill) whilst O. vachellii is a species of both higher and lower
elevations (Bidin, 1984a).
The cytology of all the three genera in Osmundales (Osmunda, Todea and Lep-
topteris) is distinctive and uniform, all have n= 22 (Lovis, 1977). Bidin (1984b) has
reported the chromosome number of O. vachellii (n=22) from the National Park
Tembeling, in Pahang. The cytology of O. javanica is studied and the chromosome
number is reported in this paper for the first time.
Squashes made from the tapetal cells of O. javanica collected from Telom Valley,
Cameron Highlands and grown in the Universiti Kebangsaan Malaysia Glasshouse
(UKMB) also showed clearly 2n = 44 (Fig. 1). This finding confirmed the uniformity
of the cytology of the genus in Peninsular Malaysia as well as the world.
All the specimens gathered and kept at UKMB were from several localities in un-
disturbed forests of Pahang, growing in fairly deep shade in permanently damp and
fe ote * ese, WR OE es AS —
Fig. 1: Mitosis in Osmunda javanica Bl. from Cameron Highlands, Pahang. 2n=44. 1000X
93
94 Gard. Bull. Sing. 41(2) (1988)
wet habitats. O. javanica was collected from Telom Valley, Cameron Highlands and
Fraser’s Hill (elevation c.4000 ft.); whilst O. vachellii was collected from the rocky
bank of River Tembeling in Malaysia’s National Park (elevation c.50 m).
The plants grew well in the glasshouse and produced sporangia.
Acknowledgements
The author wishes to thank Mr R. Jaman and Miss A. Shaari for assistance in
the field and in the laboratory respectively.
References
Bidin, A. (1984a). Ferns of family Osmundaceae in Peninsular Malaysia. Nature
Malaysiana 9(1): 28-31.
Bidin, A. (1984b). A chromosome count for Osmunda vachellii from Peninsular
Malaysia. Fern Gaz. 12(6): 360-362.
Lovis, J.D. (1977). Evolutionary patterns and processes in ferns. Adv. Bot. Res. 4:
229-415.
Manton, I. (1950). Problems of cytology and evolution in the Pteridophyta. Cam-
bridge University Press, London.
Book Review
Wayside Trees of Malaya
By E.J.H. Corner, FRS
Third Edition
Published by
The Malayan Nature Society
P.O. Box 10750
50724 Kuala Lumpur
Malaysia
Two volumes, 861 pages. 236 black and white photographic plates. 260 sets of black and white line drawings.
Malaysian Price: M$200.00 plus M$5.00 p and p.
“Wayside Trees of Malaya’ is the classic reference for interested laymen, botanists
and silviculturists for more than four decades. It has facilitated access to the wonder-
fully rich and diverse tree flora of the Malay Peninsula since the publication of the
first edition in July, 1940. The second edition, published in 1952, has long since been
out of print. The advent of this third edition is therefore occasion for rejoicing.
Improvements over previous editions are notable. Numerous corrections and up-
dating of scientific names have been made. The index of scientific names has been
extended to the species level. Additional and updated information of ‘Trees of local
interest’ has been provided, as has information on growth forms. A guide to tree
models is also included.
The text, figures and plates have been divided into two nearly equal volumes, each
faced with an attractive colour plate. This is arguably a more practical format than
that of previous editions.
Minor mistakes, errors and Omissions do crop up: both spellings, Cratoxylon
and Cratoxylum are used (Pg 365); Kurrimia is the synonym of Bhesa (Pg 246);
Drepananthus is misspelled as Drepanthus (Pg 132); Anisophyllea is missing in the
new edition, and ‘‘Pacific’’ is printed as ‘‘Facific’’ on the back cover of both volumes.
The publishers have noted the error in pages 692 and 694 where SAPINDACEAE
should read SAPOTACEAE.
These items seem niggardly in the face of the greater achievement of bringing forth
this third edition. Congratulations are in order for Professor Corner, The Malayan
Nature Society and Dr Chang Kiaw Lan for her editorial and indexing work.
Reviewed by:
Dr Tan Wee Kiat
Director
Singapore Botanic Gardens
95
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34-A LORONG 11, GEYLANG ROAD
SINGAPORE 1438
TEL: 4822362, 7477172
SPECIALISE IN:
Redecoration
Grass-cutting, civil engineering
Painting and roofing partition works
BOK K. S. TAN
Manufacturer and Distributor
of Agricultural Chemicals
e Insecticides e Rodenticides
e Herbicides e Fertilizers
e Fungicides e Adhesive Agents and Adjuvants
e Fumigants e Application Equipment
e Plant Growth Regulators
WE ALSO OFFER FORMULATION AND PACKAGING
UNDER PRIVATE LABELS
ASIATIC AGRICULTURAL INDUSTRIES PTE LTD
19, TRACTOR ROAD, SINGAPORE 2262
TEL. 2654700. CABLE: ASGRITCO
TELEX NO: RS 33406 AASTC
With Compliments
TOH ENG HOCK
BLOCK 140, #05-215
LORONG AH SOO
SINGAPORE 1953
TEL: 2853490
SPECIALISED IN:
* TURFING
* PLANTING OF TREES & SHRUBS
With Compliments
HAI JOO CONTRACTOR CO.
1214, UPPER THOMSON ROAD
SINGAPORE 2678
TEL: 4570055, 4577054
CIVIL ENGINEERING ¢ LANDSCAPING ¢ TREE CUTTING
TURFING
LIAN MIN MIN CONSTRUCTION CO.
251 UPPER EAST COAST ROAD
SINGAPORE 1646
TEL: 4433328 PAGER: 5029129
WE PROVIDE FOR ALL KINDS OF HORTICULTURAL WORKS:
@ Planting
@ Turfing
@ Maintenance of Landscape works
; PARKS AND RECREATION DEPARTMENT
x PUBLICATIONS FOR SALE
_ 1. The Gardens’ Bulletin, Singapore (Series IV).
ae te Soe
om nee AT
Price.
13(1) new impression: $12 33(1): $21.50, 33(2): $12.50, Index: $1.90
* 17(3): $12.50 | 34(1): $21.50, 34(2) with Index for 34: $11.50
4 18 & 19: $25 per vol. 35(1): $17.50, 35(2) with Index for 35: $21.50
x 20(1): $8 36(1): $21.50, 36(2): $14.00
F 25(1): $9, 25(2): $12 37(1) with Index for 36: $18.50
2 26(1): $18, 26(2): $18 37(2) with Index for 37: $16.50
Pd 27(1): $18, 27(2): $8.50 38(1): $20.00, 38(2): $13.00
2 28(1): $18, 28(2): $15 39(1) with Index for 38: $15.50
e 29: $30 39(2): $15.50
Pe 30: $48 40(1) with Index for 39: $15.50
311): $10, 31(2): $12.50 40(2): $13.00
r 32: $15.50 41(1) with Index for 40: $6.50
The Freshwater Swamp-forest of S. Johore. 41(2): $14.00
and Singapore by E.J.H. Corner (Gard.
Bull. Sing. Suppl. 1) $35
eh ee Apert, ,
2. Selected Plants & Planting for a Garden City — Forty Shrubs, $1.20.
. Selected Plants & Planting for a Garden City — Forty Climbers, $3.00.
ame Mee
w
ig
tT
a
. A Guide to Tree Planting, $4.00.
f 5. Malayan Orchid Hybrids by M.R. Henderson and G.H. Addison, $15 (1969).
_ 6. A Revised Flora of Malaya.
(a) Vol. 1, Orchids, by R.E. Holttum, $50 (3rd ed. 1980 Impr.).
(b) Vol. 2, Ferns, by R.E. Holttum, $20 (2nd ed. 1968).
(c) Vol. 3, Grasses, by H.B. Gilliland, $30 (1971).
7. Boletus in Malaysia by E.J.H. Corner, $50 (1972).
& Items 1-4 can be purchased from the Commissioner, Parks & Recreation Department,
_ Botanic Gardens, Cluny Road, Singapore 1025; tel. no. 4709917.
For overseas orders, payment should be by bank draft or International Money Order and made
payable to the Commissioner of Parks & Recreation, Singapore.
| I lems 5-7 can be purchased from Singapore National Printers (Pte) Ltd, 303 Upper Serangoon
_ Road, Singapore 1334, tel. no. 2820611 ext. 240, 241 or 231.
All prices quoted are in Singapore_-Dollars
Overseas postage is extra
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