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Sunlight Foraging in Two Tropical Southeast Asian Pioneer Tree Species: Macaranga denticulata and Mallotus paniculatus PDF

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NAT. HIST. BULL. SIAM Soc. 49: 231-241,2 001 SUNLIGHT FORAGING IN TWOT ROPICAL SOUTHEAST ASIAN PIONEER TREE SPECIES: MACARANGA DENTICULATA ANDM ALLOTUS PANICULATUS Catherine Kleie ,J,Lisa Ainsworth2,a nd Philip Rundef ABSTRACT Photos戸E曲目icresponses to light intensity plus leaf and petiole architectures were com- pared to determine light ga白巴ringstra旬giesin two pioneer tropica1 tree species,M acaranga denticulata and Mallotus paniculatus [Euphorbiaceae],in am ixed deciduous fo陀stne訂 Chiang Mai,百lai1and.Despite growth in superficially simi1紅 habitats,these two species showed marked morphologica1 and physiological di白,rer悶 s,supp口氏ing出.ehypothesis that pioneer species utilize ag radient of adaptive characteristics. These釘eesshare the classica1 pioneer mo叩hologyof large leaves and long petioles,bu t their petiole arr釦 gementsdiffer. Macaranga showed a1 泊earcor問lationbetween petiol巴lengthand leaf area,b ut Mallotus showed no relation between leaf area and petiole length. This result suggests that Mallotus may a110cate relatively more carbon for leaf grow出泊fullsu凶ightand a1so suggests白紙thisspecies may have ah igher light lr叫uirementth釦 Macaranga.Because th巴maximumphotosynthetic ra旬 was hi酔erfor Mallotus (8.5μmol m-2.s-l)由加forMacaranga (7.1μmol mm--2.s一1),petiole growth in Mallotus is an adaptation to acquire sunlight more efficiently than if petiole grow由 we問 linearlyrelated to leaf area as in Macaranga. Key wor由:Macaranga denticulata,Ma llotus paniculatus,ph otosynthesis,pi oneer紅ees,peti・ ole length INτRODUCTION The ecological meaningfulness of the pioneer concept in tropical forest succession has recently been questioned (CLARK & CLARK,1 998). Tree species traditionally considered as干ioneers"may actually represent ag radient of physiological and mo中hologicals回.tegies of adaptation. In白issωdy,w e investigate pioneer strategies of two related Southeast Asian pioneer trees,M acaranga denticulata and Mallotus paniculatus [Euphorbiaceae]. Photosynthetic response to solar irradiance and display of photosynthetic tissues represent physiological and morphological components of light foraging s釘ategies.Differences in these traits,if present,mi ght correlate with growth paUerns that allow niche segregation between these two species. Pioneer tropical forest佐'eeshave many characteristics血atallow adaptation to rapidly chang泊genvironments. Pioneer species have been defined as species that germinate and grow in open釘'easwhere light is not limiting (SWAlNE & WHITMORE,1 988; RUNOEL & IOepartment of Biology,A dams State College,2 05 Edgemont Blvd.,A lamosa,C O8 1101 20ep釘tmentof Crop Sciences,Un iversity of lllinois,37 9 Edward R. Madigan La加ratory,1201 West Greagory Orive Urbana lllinois,6 1801 30epar簡略ntof Organismic Biology,Ec ology and Evolution,Un iversity of Ca1ifomia,L osA ngeles,62 1 Charles E. Young Orive,B ox 951606,L osA ngeles,C A 900951606 司 Received 5J uly 2000; accepted 3S eptember 2001. 231 232 CATHERINE KLEIER,LI SA AINSWORTH,A ND PHILlPR UNDEL GIBSON,1 996). Pioneers typical1yh ave an enh cedcapacity to use high photosynthetic 加 photon flux densities (PPFDs) within ag ap or ac le紅均 (BAZZAZ& PIC阻 π,1980). Pioneers have higher rates of photosynthesis,r espiration,t ranspiration,s tomatal and mesophyll conductance,an d quantum efficiency than non-pioneer species,w hose seedlings can persist in the shade of af orest (BAZZAZ & CARLSON,1 982; RmDocH ETA L.,1 991). Studies have also shown that pioneers (Cecropia,O chroma dTrema species) have lower 組 shade tolerances,sa turate at higher PPFDs,an d have higher nitrogen efficiency th tropical 佃 climax trees (OBERAUER & STRAIN,1 984; STRAuss-DEBENEDETTI & BAZZAZ,1 991; RAA町AMAKERSETA L.,19 95; TRAW &A c阻 RLY,1995). Pioneers also play叩 ecologically important role by stabilizing soil after disturbances and providing initial shading for primary forest seeds (P町MACK& LEE,1 991). 官官earlysuccessional environment of pioneer species is both variable and unpredictable, thus providing for evolution of av ariety of adaptive traits and aw ide r geof responses 釦 to light environments (BAZZAZ &町CKET,1980; RUNDEL & GIBSON,1 996; ELLSWORTH & REICH,1 996). Research has supported the hypothesis that pioneer species have more flexible physiologies血anclimax species of more stable environments. For example,pi oneers have high degrees of photosynthetic plasticity,a nd they are thus able to change pattems of photosynthesis in rponseto varying light intensity levels (BAZZAZ & CARLSON,1 982; ,白 STRAUSS・.DEBENDETTI& BAZZAZ,1 991). Anatomically-based or cel1-based acclimation allows pioneers to maintain ap ositive carbon balance that supports rapid growth and survival (CHAZDON & KAUFMANN,19 93). This flexibility泊growthpattem is essential for pioneers to flourish in ac hanging environment. Changing environments also present ac hal1enge for org ismsto effectively exploit 加 available resour intheir environment. Foraging is one way organisms increase their ,回 resource acquisition (HUTCHINGS & DE KROON,19 94). Because plants are sessile organisms, those plants that have greater phenotypic plasticity and c exploitnearby patches with 叩 greater resources will be more success釦1foragers (G則ME,1979). However,u nless the plant is able to白l1yutilize available resources,th e ability to capture those resources is not of selective value. In this s旬dy,we investigate how two住opicalpioneer trees forage for light and th出 relativeabilities to utilize high light intensities. Phenotypic plasticity凶 lightforaging c組 involvechanges in leaf shape,b ranching pattems,in temode length,an d pattems of biomass allocation to various plant organs (EvA NS, 1992). Another form of plasticity involves petiole leng血 (ST回目R& HUBER,1 998). Given that newer leaves occur closer to the apex above older leaves,on togeny predicts that petiole lengths would be shorter for smal1er,y ounger leaves and longer for larger,o lder leaves. However,if petiole lengths do not correlate with leaf eas,then there is af actor 紅 other than leaf age or size determining petiole length. That factor may be light; if so, petioles of old and young leaves should grow until leaf surfaces receive high irradiances, at which point petiole growth should stop. Such growth govemed by irradiance levels is an ex倒npleof sunlight foraging. In order for light forag泊gto be佃 adaptivestrategy, leaves must be able to use fully the additional sunlight g幻nedvia foraging or else carbon would be expended without providing advantagefor the plant. To determine if differential 加 abilities to use high light intensities exist,w e performed light curves on two species of plOneer trees. SUNLIGHT FORAGING IN TWO PIONEER TREE SPECIES 233 MATERIALS AND METHODS Study Site Wec onducted 0町 studyat the Queen Sirikit Botanic Garden,n e紅 ChiangM氾,百四land (18054'N,9 8051'E; 770 m elevation). This region supports am ixed deciduous forest community with nualrainfall average of about 1200 mmt hat falls mostly between 組組 May and November.τbe forests near the study site at the garden bum on average every 1t o 3y ears (RUNDEL & BOONPRAGOB,1 995). Thes tudy took place between May 16 and 25,1 997,d uring the transition from dry to wet season. Study Species Macaranga denticulata (Bl.) M.-A. and Mallotus paniculatus (Lmk.) M.-A. are two common colonizing species of Northeast Thailand. Macaranga and Mallotus etwo related 訂 genera within Euphorbiaceae; they are grouped in the位ibeCrotoneae and the sub回be Mallotinae (P阻MACK& LEE,1 991). Both species are evergreen and have moderately to deeply dormant seeds with widely distributed seed banks in North Thailand (CHEKE ETA L., 1979). Macaranga denticulata (hereafter refered to as Macaranga) is as mall tree,u p to 20 m in height,t hat is widely distributed in open woods and clearings from the Eastem Himalayas and Southem China to Sumatra and Java. It is ac ommon member of secondary forests up to 1400 m in elevation (RIDLEY,1 967). Thel eaves訂ethin and住iangularwith round peltate or cordate bases. Thep etioles egenerally 7-13 cm long and young leaves 紅 and petioles are rust-colored. Mallotus paniculatus (hereafter refered to as Mallotus) is similar in size to the Macaranga species,a lso reaching 20 m in height (AIRY SHAW,1 971), and ranges from Southem China throughout Malaysia to New Guinea and Queensland. It is commonly found in evergreen or dry deciduous forest at low and medium altitudes (up to 1500 m) (RIDLEY,1 967). Leaves are altemately a gedand ovately shaped,of ten tricuspidate or 汀叩 trilobed. The leaves have whitish,re f1ective undersides with long,f1 exible petioles that are qui旬f1exibleand may flip over to reveal the white leaf surface in high light,w ater stress, high leaf temperature,o r a combination of these factors. Mallotus paniculatus characteristically has large macular glands at the base of the leaves. Photosynthetic Rates and Light Response Curves Photosynthesis measurements and light response curves were obtained using aL iCor “ 6200 portable photosynthesis system (Li-Cor; Lincoln,N ebraska,U SA) and ab attery powered light source (100 W halogen light). By putting al eaf in as ealed cuvette and measuring the drawdown of carbon dioxide (C02)i nside the cuvette with an infrared gas analyzer,th e Li-Cor system provides ag ood approximation of carbon dioxide assimilation (A) into the leaf,a nd this is am easure of photosynthetic activity. Assimilation is thus reported asμmol CO2m -2.s-1. A 450 cold mirror was positioned to reduce cuvette and leaf temperatures. Leaf temperatures for both species ranged from 2TC to 34-C when photosyn出eticmeasurements were recorded. Wire screens controlled ambient light levels 234 CATHERINE KLEIER. LISA AINSWORTH. AND PHILlPR UNDEL dab lack drop cloth was used for dark photosynthetic readings. Photosynthesis was 加 measured in stepwise increments beginning in full (2000μmol m-2.s-1p hotons) light. At each subsequent lower light level the leaf was allowed at least ten minutes to acclimate to the new light intensity. One leaf at at ime was measured at all light increments,a nd measurements were taken from at least two leaves on each individual plant. Additionally, numerous photosynthetic ineasurements were recorded at various naturallight levels (ranging from 400 to 1600μmol photons m-2.S- I). TheC O2c oncentration in the cuvette was maintained at approximately 375 p紅白 permi1lion. Photosynthetic measurements were taken in the moming (0900ー1200h) to avoid attenuation due to water or heat s回 ss. Light curves were fit according to血enon-rectangular hyperbolic equation using Sigma Plot version 2.01 (Jandel Scientific,F airfax,C A). The light saturated maximum of photosyn曲目isand the maximum CO2a ssimilation rate (Amax) were both calculated with Photosyn Assistant,V er. 1.1.2 (Dundee Scientific,D undee,U K). The light saturation maximum of photosynthesis estimates the light level at which photosynthesis is no longer limited by light,b ut is instead limited by carboxylation activity (LAMBERS ETA L.,1 998). Additionally,t he maximum CO2a ssimilation rate (Amax) is the light saturated rate of net CO2a ssimilation. Both Amax and the light saturation maximum of photosynthesis are estimated from the asymptote of the light curve. Leaf Sampling and Measurements Leaf and petiole samples were removed from six Mallotus and eight Macaranga. Leaf samples were taken from trees,y ounger seedlings,a nd saplings. Leaves were chosen haphazardly from the bottom ptof the c opy.On individual trees in both species,th e 紅 叩 shortest petioles belonged to the youngest leaves,w hich were easily identified by rust coloration. Extremely young leaves were not used. At least two leaves were removed from each plant. Petiole lengths were measured with am ilimeter ruler,an d leaf and petiole eas 訂 were measured with ap ortable leaf area meter (Li-Cor 1600,Li ncoln,Ne braska). Weights of petioles and leaves were measured with 10 and 100 gp esola balances. Alllength,ar ea, and weight measurements were taken within 12 ho f collecting the samples. Isotope Analysis ln order to determine water use efficiency (WUE),fi ve leaves of each species were collected,dr ied,a nd placed in sealted plastic bags. Upon retum to UCLA,th e leaves were finely ground into powder and 2m gs ub-samples of each leaf were weighed. Samples were combusted in an elemental analyzer coupled to an isotope ratio mass spectrometer ([Duke University,Du rham,N .CふDataare presented relative to the intemational Pee Dee Belemnite standard. Carbon isotope ratios (OI3)a re used as al ong-teロnindicator of plant water-use efficiency (FARQUAR ETA L.,1 989). Discrimination again~! I3C02 occurs during diffusion into the stomata and during carbon fixation. Since OI3C is proportional to stomatal conductance and hence inversely related to WUE,it was expected that if there were ecological differences pertaining to plant water use,t here would be ad ifference in o13C levels. SUNLIGHT FORAGING IN TWOP IONEER TREE SPECIES 235 Statistics Student's t-tests were preformed to detect for differences泊leafand stem measurements between Macaranga and Ma/lotus. Degrees of freedom are reported as subscripts to血et value and the probability (P) of the difference being due to random ch ceis also reported. 佃 For relations between petiole and leaf measurements,li near regressions were done,a nd r, the product moment correlation coefficient,wa s evaluated. R号gressionsfor leaf area against petiole length were made using Origin version 2.8 (MicroCal,N orthhampton,M A). SigmaStat,ve r. 8.0 (Jandel Scientific,Fa irfax,C A) was used for all t-tests. RESULTS Light Response Curves τ 'hel ight curves presented are best-fit lines through the data using the rectangular hyperbolic regression equation (Fig. 1). Light response c町vesfor Macaranga and Ma/lotus have similar va1ues at very low light intensities; for photosynthetic photon fIux density (PPFD) lower血an100μmol m-2.s-1,ph otosynthesis va1ues for both species were less than lμmol CO ,.m-2.s-1. At PPFD levels from 100 to 800μmol m-2.S-I ,Ma caranga had higher photosynthetic ra旬S出anMallotus. Above aP PFD of 1,000μmol m-2.S-I ,th e Ma/lotus curve continues to increase while that of Macaranga approaches saturation. Light saturation occurs where there is no longer an increase in assimilation of CO2w ith ac o汀'espond加g increase in light level (PPFD). Photosyn Assistant calculated light saturation estimates of 742μmol m-2.S-1 photons for Macaranga and ah igher estimate of 1001μmol m-2.s-1 photons for Mallotus. Photosyn Assistant estimated maximum assimilation of CO ,.into the leaf as 6.7μmol m-2.S-1 for Macaranga and 10.2μmol m-2.S-1 for Ma/lotus. However,白e highest assimilation values measured in血isstudy were 7.1 !lmol m-2.s-1fo r Macaranga and 8.5μmol m-2.S-1 for Ma/lotus. Leaf Measurements Macaranga and Mallotus both display plagiotropic branching. Branches develop rhythmica11y from the trunk,bu t the intemode length between secondary branches decreases dista11y. Leaves are arranged in clusters from the branches with variable petiole lengths in MaLlotus. Leaves釘eoriented horizontally and have leaf angles between 1400 and 190。 from the petioles. Petiole lengths of mature leaves did not differ between Macaranga and Mallotus (t24 =--u .276,P = 0. 785),bu t leaf areas were sig凶白cantlyhigher in Macaranga (t24 =_ -3.651, P= 0 .001). Macaranga denticulata leaves varied in size from 203 to 1144 cm'" in our Snpleswith larger leaves commonly seen in the field. Mallotus paniculatus leaves were 創 not as large or as variable in size,ra nging from 112 to 502 cm2,b ut the petiole lengths were more unpredictable than the petiole lengths of Macaranga. Ther elation of petiole length to leaf eav;ui.ed greatly between the two species. Leaf increaseslinearly with 紅 紅白 petiole length in Macaranga (日=0.82,P < 0 .001; Fig. 2). Although one petiole measured 45 cm,a nd this point may bec onsidered an outlier,M a/lotus leaves show no relationship 236 CATHERINE KLEIER, LISA AINSWORTH, AND PHILIP RUNDEL 10 • Mallotus paniculatus 8 I! • ....,.. -., 6 I Vl N I- s 4 0 ], < 2 0 10 Macaranga denticulata 8 • •• ...,... -., 6 I Vl N I s 4 0 §_ ...._, < 2 0 -2 0 500 1000 1500 2000 PPF.D (f.!mol m-2s-1) Figure I. Light curves for Mallot!ts paniculatus and Macaranga denticulata performed in the morning with both artificial and natural light. Points represent one of at least two leaves from ten individuals. Light curves were fit to the rectangular hyperbolic equation. They-axis shows carbon assimilation (A) and the x-axis shows photosynthetic photon flux density (PPFD). SUNLIGHT FORAGiNG IN TWO PIONEER TREE SPECIES 237 1200 • Macaranga denticulata 2 R = 0.81961492 1000 P<O.OOl • 800 ,-.-. N •• E u • '-' ".Q..'). 600 •• "' ....... "' • Q) ......1 400 • • • 200 # 0 Mallotus paniculatus 1000 2 R =0.45119101 P=0.1585 800 ,-.-. N E u '-' ".Q..'). 600 ..."...'. • "' Q) ......1 400 200 0 0 5 10 15 20 25 30 35 40 45 50 Petiole length (em) Figure 2. Linear regression for leaf petiole length to leaf area for Macaranga denriculata (top). Linear regression for leaf petiole length to leaf area for Mal/arus paniculatus (bottom). 238 CATHERINE KLEJER,LJ SA AJNSWORTH,A ND PHILJP RUNDEL = = between leaf area and petiole length (r2 0.45,P 0.158; Fig. 2). Additionally,t he coefficient of variation (CV =s tandard deviation/sample mean) was calculated for leaf area and petiole length for both species. The CVr atio of petiole length to 1eaf area was greater in Mallotus血佃泊 Macaranga,1.044 to 0.643 respectively,a nd this also supports more variable petiole lengths加Mallotus.Mean petiole weights and petiole surface areas did not differ between species. Average leaf weight of Mallotus was smaller than that of Macaranga = (t24 4.197,P < 0 .001). In addition to higher le~f area and leaf weight,Ma caranga also showed significantly higher leaf mass area (gmー)(t =7 .342,P <0 .001),in dicating that 24 Macaranga had thicker leaves than Mallotus. Stable Isotope Analysis Three samples of each species were processed for o13 carbon isotope levels. Them ean for Macaranga was -28.481 :t 1.537,a nd the mean for Mallotus was -29.181 :t 1.515. = = 百lerewas no statistical di百'erencebetween the two species (t24 0.562,P 0.604). DISCUSSION In this study,M acaranga and Mallotus exhibit the classic morphology for pioneer 岡崎(HALL邑ETAL.,19 78). They have branch units that釘'earranged in an umbrella-shaped monolayer of large leaves with long petioles (HALLE ETA L.,1 978). Both Macaranga and Mallotus can be characterized by Rauh's model,w hich is defined by monopodial growth of the trunk with tiers of branches that form morphogentically identical to the trunk. Branch growth is plagiotropic and“escape asymme句"can occur distally,ca using shorter intemode lengths between secondary branches,出usminimizing self-shading. Although phyllotaxy seems to be genetically constrained,fa ctors such as leaf morphology,al lometry, and physiological plasticity c overridephyllotaxic constraints to increase light reception 組 and carbon gain (NIKLAS,1 988). In this study despite their similarities as pioneer species, Macaranga and Mallotus display significant differences in their photosynthetic capabilities and leaf morphologies. Although the similarities of overall morphology may be due to sh edphylogenetic histories,th e photosynthetic and leaf morphology differences between 紅 these two species suggest that ag radient of niche selection may exist in pioneer habitats. Macaranga and Mallotus showed am arked difference in light harvesting strategies via leaf and petiole grow由.Macaranga shows al inear relationship between leaf size and petiole length; such ar elationship is intuitive in ad evelopmental and biomechanical sense. However,in Mallotus,t here is no correlation between leaf size and petiole length. L ge 紅 leaves with short petioles can be found on the same branch as smaller leaves with longer petioles. Although there is relatively much less variation in leaf size in Mallotus than泊 Macaranga,th e former still has more variable petiole lengths,w hich may be controlled by light availability rather than the size of the leaf. TheR auh architectural model is found in trees that demand high light. Because Mallotus shows highly variable petiole lengths白紙donot coηespond with leaf areas,th ere must be another factor determining petiole length aside from age or size of the leaf. Our data support the hypothesis that the determining factor for petiole growth is light availability, and that petioles grow sufficiently to place leaves in easof high irradiance. Excess 訂 SUNLIGHT FORAGING IN TWO PIONEER TREE SPEClES 239 petiole growth should provide an advantage for the plant or carbon is wasted. Because Mallotus can utilize higher light levels than Macaranga,th e excess light does provide 卸 advantage,a nd variable petiole growth in Mallotus represents an adaptive exarnple of foraging for light. Foraging has been shown in clonal plants by ramet production occurring in favorable patches when grown in ah eterogeneous soil resour environment (EVANS & CAIN,1 995). Similarly,Ma llotus extends leaves into favorable sun patches when grown in ah eterogeneous light environmen .tIn Plantago major,f ull-sun plants developed widening leaf laminas, whereas shaded plants devoted more resources toward lengthening the larnina (NIKLAS & OWENS,1 989). By increasing larnina surface through producing longer leaf blades,a l eaf has ag reater chance of reaching am ore favorable light environment. In ah eterogeneous light environment,p lastic leaf petiole lengths would enable optimal foraging for light patches. Such af oraging strategy would be expected in Mallotus only if it were able to use the extra light resource,w hich was demonstrated by the higher A~oV in this species. .u Although the present study did not differentiate between light qantity and light spectral composition,it has been reported that light quantity primarily affects growth and that spectral composition (i.e. red to far-red ratio) mainly affects developmental processes (LEE ETA L.,19 97) and plant morphogenesis (ST回目R& HUBER,1 998). Thus,th e differences in growth between the two tree species were most likely due to light quantity rather than light quality. The maximum CO2 assimilation rates Amax for Macaranga and Mallotus are lower thmmmyv alues forAmaxrepomd for pioneer species-For Cecropia,Ficus,叩dDidymopnax 一. species,A ~oV values have been reported as high as 23.1 !!mol m S-l to 33.1 !!mol m-2• S-1 (reyl長wedin Rundel&Gibson,1996).The highest Arylax reported for Mallotus was 14μmol m-2.s-1at PPFD of 500μmol m-2• S-1 measured in an Oevergreen forest in Singapore (TAN,O NG,& TuRNER,1 994). The present study was conducted in al ess mesic,m ixed deciduous forest,du ring the transition from dry to wet season,an d because rain fell before and during our study,w ater stress is unlikely to have been an issue in our measurements. Relatively low rates of maximum photosynthesis have also been found in other pioneer tree species (RUNDEL ETA L.,u npublished data). Pioneers generally have the capacity to vary rates of photosynthesis with light availability and moisture availability (BAZZAZ & CARLSON, 1982) (ISHIDA ETA L.,1 999),s o perhaps the leaves that were measured were adapted to lower light levels and thus had lower photosynthetic rates. Howerver,a s tudy of nine MGcarangaspecies from Southeast Asia showed ar mge for Amax of7-13μmol CO 2 m-2.S- 1 (DAV IES,1 998). Responses to light may be important in determining ecological niches of tropical forest trees (BARKER ETA L., 1997). Niche separation according to plant architecture may be more important in understory trees where light is limiting (TrwA RI & SHUKLA,1 995). Variation in shade tolerance is strongly correlated with life history traits (DAV lES,1 998),a gain supporting the importance of light in defining niche segregation. Foraging for light may also be related to ability to forage for nutrients (HUANTE,E TA L., 1998). Finally,a r ecent review concluded that individual plant fitness,gr owth of plant populations,a nd the degree of growth inequality arnong neighbors are all strongly dependent on sunlight foraging (BALLA阻 ETAL.,1 997).百四, specific niches that pioneer trees are able to occupy may be defined by the extent of plasticity those trees are able to display. In conclusion,M acaranga denticulata leaves have al inear relationship between leaf 240 CATHERINE KLEIER,L lSA AINSWOR'四,AND PHILIP RUNDEL 紅eaand petiole length and a1so may be more tolerant of shade白血Mallotuspaniculatus leaves. Light curves suggest白紙Macarangadenticulata leaves may have an enchanced abi1ity to acc1imate photosyn也氏iccapacity to lower light levels,wh ich might explain why Macaranga has aw ider distribution than Mallotus (AIRY SHAW,1 971). ACKNO"江ADG勘ffiNTS Thea uthors with to由ankDr. Kansri Boonpragob,th e Queen S註泳itBotanic Garden, 血.egovernment of Thailand,a nd UCLA who provided fmancia1 support for也iswork 出roughthe Field Biology Quarter program. REFERENCES AIRY SHAW,H. K. 1971. Euphorbiaceae of Siam. Kew Bulletin 26(2): 191-363. BALLA阻,C. L.,A . L. SCOPEL,A ND R. A. SANCHEZ. 1997. Foraging for light: Photosensory ecology and agricul- tura1 implications. Plant,C ell Environ. 20(6): 820-825. BARK殴,M. G.,M . C. PRESS,A ND N. D. BROWN. 1997. Photosynthetic characteristics of dipterocarp seedlings 泊由民巴町opicalrain forest light environments: ab asis for niche partitioning? Oecologia 112: 453-463. BAZZAZ,F. ,A ND R. CAR凶ON.1982. Photosynthetic acclimation to variability in the light environment of early and 1蹴 successionalplants. Oecologia 54: 313-316. BAZZAZ,F. ,A ND S. PICK回'T.1980. Physiological ecology of回picalsu∞ession: ac omparative review. Ann. Rev. Ecol. Syst. 11: 287-310. CHAZDON,R. ,A ND S. KAUFMANN. 1993. PIωticity and leaf anatomy of two rain forest shrubs泊 relationto photosyn曲目iclight acclimation. Funct. Ecol. 7: 385-394. CHE阻,A., W. NANAKORN,A ND C. YANKOSES. 1979. Dormancy and dispersal of seeds of secondary forest s戸cies under the canopy of primary tropic叫rainforest恒No泊施m唄lai1and.Biotropica 11: 88-95. CLA阻,D. B.,A ND D. A. CLA蹴.1998. Pion町田especies. An ecologically mean加前11concept? Biotropica 30(2) SUPPL.: 1. DAVIお, S. J. 1998. Photosynthesis of nine pioneer Macaranga species台。mBomeo in relation to life history. Ecology 79(7): 2292-2308. ELLSWORTH,D. ,AN D P. REICH. 1996. Photosynthesis and leaf nitrogen in five Amazonian町民speciesduring early secondary succession. Ecology 77(2): 581-594. EVANS,J. P. 1992. Thee ffect of local resource avai1abi1ity and clonal integration on ramet functional morphology in Hydrocoのlebonariensis. Oecologia 89: 265-276. Ev刷 s,J. P.,刷DM.L.CA到.1995. As patially explicit回tofforaging behavior泊aclonal pl釦t.Ecology 76(4): 1147-1155. GRIME,J. P. 1979 Plant Strategies and Vegetation Processes. Wiley,Ch inchester. HALL,邑F.,R. A. A. OLDEMAN,A ND P. B. TOMLINSON. 1987. Tropical Trees and Forests. Cambridge University Press,C ambridge,U .K. ∞ HUAN百, P.,E . RlN N,A ND F. S. CHAPIN. 1998. Foraging for nutrients,r esponses to changes in light,組d competition in加 picaldeciduous tree seedlings. Oecologia 117(1-2): 2仰ー216. HUTCHlNGS,M . J.,A ND H. DE KROON. 1994. Foraging in plants: the role of morphological plasticity泊reso町'ce acquisition. Advances in Ecological Research 25: 159-238. ISHlDA,A .,T. TA KESH1, AND MARJ聞 HA.1999. Leaf gas exchange and chlorophyll flu日間scencein relation to leaf angle,a zimuth,組dc組opyposition in the tropical pioneer tree Macaranga conifer. Tree Physiol. 19(2): 117-124. LAMBERS,H .,F. S. CHAP刑,m,馴oT. L. PONS. 1998. Plant Physiol. Ecol. Springer-Verlag,N ew York,N Y. L凪 D.W.,S. F. OBERBAUER,B . KRISHNAPILAY,M . MANSOR,H . MOHAMAD,A ND S. K. YAP. 1997. E飾ctsof irradianc巴andspec住'alquality on seedling development of two Southeast Asian Hopea sμcies. Oecologia 110: 1-9.

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