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Reproductive Biology |
2Instituto Multidisciplinario de Biología Vegetal (CONICET-UNC), C. C. 495, 5000 Córdoba, Argentina; 3Department of Ecology and Evolutionary Biology, Storrs, Connecticut 06269-3043 USA
Received for publication May 13, 2003. Accepted for publication August 19, 2003.
| ABSTRACT |
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Key Words: conservation biology hummingbirds island biology nectar removal nectar secretion pollination biology reproductive biology
| INTRODUCTION |
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Unfortunately, more than 62% of the Juan Fernández flora is considered rare, and two species are already extinct (Stuessy et al., 1998
). Endemic floras of oceanic islands are lost at higher rates than continental floras (Reid and Miller, 1989
; Smith et al., 1993
), because human disturbance of the fragile island habitats has taken place on a greater scale than in most continental systems (Loope et al., 1988
; Mittermeier et al., 1999
). Interestingly, in the Juan Fernández archipelago there were no permanent human settlements before the 16th century (Woodward, 1969
); thus, disturbance has been occurring for less than 430 yr. However, its biota is particularly threatened by both anthropogenic and natural phenomena, including fire, erosion, vegetation cutting, grazing and predation by feral animals, and losses of habitat to aggressive introduced exotic weeds (Stuessy et al., 1998
). There is increasing urgency for studying and preserving plant species (Carlquist, 1998
; Raven, 1998
), because island species are part of our biological heritage and are often key organisms for the study of plant evolution and speciation (Crawford and Stuessy, 1997
; Baldwin et al., 1998
).
Among endemics of the Juan Fernández archipelago there are only two legume species, both in the genus Sophora L. (subfam. Papilionoideae) from tribe Sophoreae, a tribe recently shown to be nonmonophyletic (Doyle et al., 2000
). Both species belong to section Edwardsia, which is considered monophyletic and well differentiated from other Sophora (Peña and Cassels, 1996
; Hurr et al., 1999
; Peña et al., 2000
). This section includes 17 island tree species of classical Antarctic-circumpolar distribution across the Pacific, south Atlantic, and Indian Oceans and southwest South America (Polhill, 1981
; Peña et al., 2000
; Heenan et al., 2001
). Each of the two main islands of this archipelago supports one species: S. fernandeziana (Phil.) Skottsb. on Isla Robinson Crusoe and S. masafuerana (Phil.) Skottsb. on Isla Alejandro Selkirk.
The genus Sophora includes 4550 species of worldwide distribution with its center of diversity in North America (Polhill, 1981
; Sousa S. and Rudd, 1993
; Peña et al., 2000
). Peña et al. (2000)
proposed that Sophora migrated from North America to South America and subsequently to the Pacific Ocean, suggesting S. macrocarpa J. E. Sm. from continental Chile as the likely ancestor of both Fernandezian species. An alternative hypothesis, provided by Hurr et al. (1999)
, suggests recent dispersal around the southern oceans through buoyant seeds from other non-Edwardsia species of the northwest Pacific.
Sophora fernandezianalocally known as "madera dura"is a tree up to 10 m tall, with showy flowers and four-winged pods. Previous work on this species focused mainly on systematics (Skottsberg, 1922
, 1953
; Yakovlev, 1967
; Tsoong and Ma, 1981
), phylogeny (Peña and Cassels, 1996
; Peña et al., 2000
), chromosomes (Stiefkens et al., 2001
), alkaloids (Hoeneisen et al., 1993
), flavonoids (Ruiz et al., 1999
), and allozyme diversity (Crawford et al., 2001
).
Little is known of its reproductive biology, other than scattered information on floral visitors, nectar presence (Skottsberg, 1928
; Meza, 1988
; Colwell, 1989
; Bernardello et al., 2002
) and pollen morphology (Peña et al., 1993
). The same occurs for the genus as a whole: there are only limited data on floral ontogeny (Tucker, 1994
), nectar (Haragsim and Macha, 1969
; Clinch et al., 1972
), pollen (Chung and Lee, 1990
; Peña et al., 1993
; Ferguson et al., 1994
), breeding system (Arroyo, 1981
), and floral visitors (Cockerell, 1902
; McCann, 1952
; Clinch et al., 1972
; Godley, 1975
; Arroyo, 1981
).
As for endangered species in general (Holsinger, 1991
; Anderson, 1995
), understanding the reproductive biology of S. fernandeziana is critical to successful conservation efforts. Its present conservation status is "vulnerable" (Hilton-Taylor, 2000) mainly because of its restricted area on a small island, the few remaining known populations (approximately five; Crawford et al., 2001
), and the small number of individuals left in the wild (between 50 and 100; T. F. Stuessy, Institüt für Botanik, Universität Wien, personal communication). In addition, Crawford et al. (2001)
reported low allozyme genetic diversity at the species level.
In a recent expedition to Isla Robinson Crusoe, we studied the reproductive biology of S. fernandeziana addressing the following issues: (1) generalized floral features and the stages of floral development, (2) the pattern of nectar secretion and effects of removal on nectar production, (3) floral visitors and how pollination is accomplished, (4) the breeding system, seed and fruit set, and (5) consideration of these data for the assessment of reproductive strategies and implications for conservation.
| MATERIAL AND METHODS |
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Flower lifetime
Randomly chosen flowers in the bud stage were tagged for identification and bagged using nylon net bags to exclude visitors. Flower longevity was determined from 15 flowers per tree by following their development until they wilted.
Floral morphology and anatomy
Flowers (n = 5 per tree) were fixed in 70% ethanol, dehydrated in an ethyl alcohol-xylol series, and embedded in Paramat (BDH Laboratory Supplies, Poole, UK). Serial cross- and longitudinal sections were cut at 12 µm, mounted serially, stained with safranin-fast green-hematoxylin, and observed with a compound microscope. To localize stomata or starch grains, nectary tissue was cleared with NaOH (10% aqueous solution), washed with acetic acid : water (1 : 3), spread on a slide, and stained with an aqueous I2-IK solution. Drawings were made using a camera lucida attachment on a stereomicroscope. Photomicrographs were taken on a Zeiss Axiophot microscope (Zeiss, Jena, Germany). using Kodak T-max film, 100 ASA (Kodak, Rochester, New York, USA).
Nectar
Due to the huge number of available flowers per tree, nectar extraction on the same tree is unlikely to introduce any bias in our results. Samples were extracted with capillary glass tubes without removing the flowers from the plant and taking special care to prevent damage to the nectaries. The presence of nectar was also checked in buds. Two variables were measured immediately after the extraction: volume (in microliters) using graduated micropipettes, and sugar concentration (percentage of sucrose, mass/total mass) with a pocket refractometer. The amount of sugar produced was expressed in milligrams following Kearns and Inouye (1993)
. Additional nectar drops were placed on Whatman #1 chromatography paper and dried rapidly. These samples were used subsequently to detect amino acids, lipids, phenols, alkaloids, and reducing acids after Baker and Baker (1975)
. Sugars were separated by paper chromatography on Whatman #3 chromatography paper with n-butanol : glacial acetic acid : water (3 : 1 : 1, volume/volume) as a solvent (Grant and Beggs, 1989
). Dried chromatograms were treated with aniline phthalate to visualize sugars.
The nectar secretion pattern was determined using 13 bagged sets of 57 randomly assigned flowers. Data were taken once for each set, allowing the nectar to accumulate until the measurement. Measurements were performed at 0700 and 1900 hours each day, covering the entire flower lifetime. Nectar secretion rate (NSR) per hour was calculated dividing the amount of sugar (in milligrams) produced by the number of hours between the measurements (in milligrams per hour). Nectar reabsorption rate (NRR) per hour was calculated by dividing the amount of sugar (in milligrams) reabsorbed by the number of hours of the time period considered (in milligrams per hour).
Effects of removal on total nectar production were assessed using 12 bagged sets of 57 flowers each, on the same trees used for nectar secretion. Nectar was removed and measured from the same flower repeatedly, at 0700 and 1900 hours, throughout the flower lifetime. Sets were subjected to a different number of nectar removals: set 1 = removed 12 times, starting at flower opening; set 2 = removed 11 times, starting 12 h after flower opening; set 3 = removed 10 times, starting 24 h after flower opening; and so on, until reaching set 12 = removed once, at the end of the nectar secretion, having allowed nectar to accumulate until the measurement. To accurately compare the results, the set not involved within the reabsorption period was used as the control.
Floral visitors
The 10 trees of both populations studied were observed for a total period of about 30 h. Periods of observation ranged from 10 min to 1 h and were mostly done during daylight hours (07001000 hours, 12001400 hours, and 18002000 hours). Two nocturnal observations of 30 min each were made as well.
The P/O ratio and pollen viability
Buds examined for P/O ratios (15 per tree) were near anthesis, i.e., pollen was mature, but anthers had not dehisced. Pollen quantity was estimated using Anderson and Symon's (1989)
modification of Lloyd's (1965)
technique. With the aid of a dissecting microscope, all ovules were counted. Pollen viability was estimated as the percentage stainability of 100 grains from each of 15 flowers (five per tree) using aniline blue in lactophenol (Hauser and Morrison, 1964
).
Experimental crosses
Branches with unopened flowers were tagged and bagged with nylon net bags to exclude visitors. Two days later, after the flowers had opened (stages 34, Fig. 1), autogamous hand crosses were performed by applying self-pollen from recently opened anthers (using the anthers themselves as pollen applicators) to stigmata. Pollinated flowers (n = 45, 15 from each of three trees) were collected and fixed in 70% ethanol 24, 36, and 48 h after pollination for analysis of pollen tube growth. Additional tagged and bagged sets were used to check for autonomous self-pollination and untreated, unbagged flowers for natural pollination; these flowers were collected 5 d after anthesis (n = 45, 15 from each tree). Gynoecia were softened with 8 mol/L NaOH for 1 h at 60°C in a water bath, rinsed, and stained in aniline blue 0.1 NK3PO4 for 2 h (Martin, 1959
). Then, they were dissected from the flower on glass slides and flattened. The distance of pollen tubes growth was measured under an epifluorescence microscope.
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Statistical analyses
Tests were performed using methods described in Sokal and Rohlf (1995)
. All distributions were tested for randomness of nominal data (Runs test), homogeneity of variance (Levene test), and departures from normality (Kolmogorov-Smirnov test for goodness of fit). The effects of nectar removal on total nectar sugar production was compared using one-way analysis of variance (ANOVA). Sets subjected to nectar removal were compared with control sets with t tests.
| RESULTS |
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Floral features
Inflorescence axes, and consequently the flowers, are typically pendulous or subpendulous (Figs. 1, 2A). Flowers are showy, golden yellow, odorless, open diurnally, and last for 6 d. They are borne in reduced panicles with 212 flowers (Fig. 2A) or rarely singly. There is usually a maximum of three open flowers per inflorescence at the same time. Flowers are zygomorphic with a bowl-shaped, pubescent, fleshy, and obliquely truncated calyx with five small teeth. The corolla has a standard that does not reflex; this petal has a well-formed claw. The lower petals are more or less undifferentiated (i.e., wings and keel are quite similar in length). Wings have abaxial hidden sculpturing on the basal part. Both fertile whorls are exserted: the androecium with 10 free stamens and a stipitate, pubescent ovary with a glabrous style and a moist, small, capitate stigma. There 10 ± 0.6 ovules per flower (mean ±1 SE), whereas amount of pollen reaches a mean of 273 080 ± 48 400 pollen grains; the P/O ratio is 27 069.
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Nectary
A structural floral nectary is located in the receptacle between the stamens and the ovary. It is disc-shaped and measures ca. 2 mm lateral, having several protuberances that increase the secretory surface (Fig. 3). Anatomically, it is composed of 1012 layers of nectaripherous tissue, the cells bear druses, and it is supplied by vascular bundles with phloem and xylem (Fig. 3AC). Stomata are found uniformly distributed in the epidermis of the nectary.
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Data on the nectar secretion pattern throughout the flower life span are plotted in Fig. 4. Nectar is first secreted when flowers are approximately 3 d old (after 48 h; Fig. 4). When nectar secretion starts, the volume and mass of sugar increase slowly until flowers are ca. 84 h old (NSR = 0.104 mg/h); then, both the volume and mass of sugar increase rapidly (NSR = 0.83 mg/h) until they reach maximum production around the fifth day (120 h) after anthesis (Fig. 4A, C). Nectar concentration behaves differently. It increases rapidly as soon as secretion starts and until flowers are about 72 h old. After this, the concentration remains relatively constant (Fig. 4B). At the end of the flower lifetime, there is an active nectar reabsorption period just after the peak of production (Fig. 4C) with a NRR = 0.32 mg/h.
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Visitors
Both sexes of the two hummingbird species that inhabit Isla Robinson Crusoe (Sephanoides fernandensis, endemic, and S. sephaniodes, native) have been observed as regular visitors in the study sites. Hummingbirds can be observed throughout the day at blooming trees, aggressively defending the trees. Given that each tree has a large number of simultaneously open flowers, hummingbirds take nectar from several flowers of an individual tree before going to another one.
On the cultivated specimens, introduced Argentine ants (Linepithema humile, Formicidae) were observed visiting the flowers and taking nectar, and an introduced curculionid species (Naupactus xanthographus, Entiminae) was detected actively eating flowers.
Fruit and seed production
Pods are typically four-winged, dry, coriaceous to subligneous, brown, and ultimately dehiscent (Fig. 2B). The natural fruit set is low. Flowering branches average 91 ± 41 flowers (n = 30, 10 per tree, range 25169), and fruiting branches average 7.4 ± 4.40 fruits (n = 30, 10 per tree, range 116). Thus, the indirectly estimated fruit production is about 8%. Seeds are dark brown, dry, and hard. The number of seeds per fruit ranges from 1 to 4 (x = 2.0 ± 0.8; n = 70), i.e., 20% of the ovules became seeds.
| DISCUSSION |
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The nectary type we observed in S. fernandeziana is characteristic of Papilionoideae (e.g., Waddle and Lersten, 1973
; Fahn, 1979
; Davis et al., 1988
). The presence of stomata is a common feature of floral nectaries of legumes in general (Davis et al., 1988
). Studies in Vicia faba have demonstrated that the main functions of stomata seem to be those of assisting nectar escape from the gland and, perhaps, enhancement of reabsorption of uncollected nectar (Davis and Gunning, 1993
).
Nectar
Nectar is the most common reward for the archipelago flora as a whole (Skottsberg, 1928
; Bernardello et al., 2000
, 2002
; Anderson et al., 2001b
), including S. fernandeziana. Flowers of S. fernandeziana do not secrete nectar in bud stage nor on the first 2 d after flower opening. Individual flowers have a large variance in nectar content because nectar removal decreases production and nectar is also reabsorbed. Given that each tree bears many inflorescences throughout the flowering season and that each includes many flowers of different ages at all times, pollinators enjoy a constant nectar supply when dealing with Sophora. The amount of reward encountered by animals may affect pollinator behavior, which in turn determines pollen transport and deposition at least within the populations, and therefore the number of autogamous and xenogamous seeds produced (Zimmerman and Pyke, 1986
).
Nectar concentration remains relatively constant throughout the flower lifetime, as has been observed in other South American legume species (Cocucci et al., 1992
; Galetto et al., 2000
). However, nectar volume and the amount of sugar progressively increase as the flower ages. Thus, one might predict an increase in pollination events and mating opportunities (either xenogamous or geitonogamous), during middle and late stages of the flower lifetime (vs. early stages), a conclusion that may also be inferred from morphological traits (see later).
A nectar reabsorption period takes place before the flower wilts. Nectar production obviously involves a cost to the plant in terms of growth and/or reproduction (Pyke, 1991
), consequently, the decline in total nectar production following removal and nectar reabsorption in aging flowers would reduce this cost. Reabsorption of nectar allows the plant to reuse the source of carbon for alternative purposes such as developing seeds (Zimmerman, 1988
; Burquez and Corbet, 1991
), presumably with a consequent reproductive advantage.
Nectar removal strongly decreased nectar production, indicating that nectar secretion may be reduced or stopped after pollinator visits. This reduction in nectar investment also could benefit seed production (Heinrich, 1983
). This mechanism also maximizes pollen transfer because hummingbirds would need to visit different flowers and thus perhaps different plants in order to satisfy their metabolic requirements (Feinsinger, 1978
).
Pollination and breeding system
In oceanic islands pollinator faunas are generally small with many groups completely absent (Carlquist, 1974
; Woodell, 1979
; Barrett, 1998
; McMullen, 1999
). This trend was found in the Juan Fernández Islands as well, where floral visitors other than hummingbirds are rare or unknown (Skottsberg, 1928
; Anderson et al., 2001; Bernardello et al., 2002
). Thus, the wide extent of nectar rewards is a manifestation of the origin of this flora more than it is of its current pollination status (Bernardello et al., 2000
; Bernardello et al., 2002
). The fauna of the Juan Fernández archipelago is known partly because of the two hummingbird species: one of them is the only endemic known on oceanic islands (Sephanoides fernandensis); the other (S. sephaniodes) is also found south of the Atacama desert in Chile (Colwell, 1989
; Roy et al., 1998
). Both sexes of the two species have been recorded as regular visitors of 14 woody angiosperms, i.e., 9% of the flora (Bernardello et al., 2002
), including S. fernandeziana (Brooke, 1987
; Meza, 1988
; Colwell, 1989
; Bernardello et al., 2000
, 2002
; Anderson et al., 2001b
).
Assuming that there is a coevolutionary relationship between nectar features and type of pollinator, several authors have proposed that certain nectar volumes and concentrations attract different pollinator guilds (e.g., Baker, 1975
; Pyke and Waser, 1981
; Cruden et al., 1983
; Opler, 1983
). In particular, hummingbird flowers often bear large amounts (ca. 1016 µL) of dilute nectar (ca. 20% sugar) (e.g., Cruden et al., 1983
; Opler, 1983
; Tamm and Gass, 1986
). Neither the mean nectar volume (8 µL) nor mean concentration (52%) in S. fernandeziana accord with these values. However, under laboratory conditions, hummingbirds given a choice of sugar solutions prefer the highest sugar concentration offered over an equal volume presentation (e.g., Hainsworth and Wolf, 1976
; Stiles, 1976
; Tamm and Gass, 1986
; Mitchell and Paton, 1990
). Bees could certainly use this reward as well, but the only bee on Isla Robinson Crusoe (Lasioglossum fernandezis; Engel, 2000
), is a recent adventive (Anderson et al., 2001a
) and is restricted to San Juan Bautista, the only permanent settlement. Even though the cultivated plants (in the CONAF experimental garden) of S. fernandeziana are within this range, these small bees were never observed taking S. fernandeziana nectar.
Sophora elsewhere includes both insect- and bird-pollinated species (Tucker, 1994
). Among the pollinating birds are hummingbirds, honeycreepers, honeyeaters, and lorikeets (e.g., McCann, 1952
; Clinch et al., 1972
; Godley, 1975
; Arroyo, 1981
; Tucker, 1994
). McCann (1952)
indicated that the bird pollination of S. tetraptera in New Zealand is supplemented or replaced at times by insect pollination, both resulting in fruit set. Bernardello et al. (2002)
suggested that the first Sophora colonists on the Juan Fernández archipelago would have already been ornithophilous and with the arrival of hummingbirds would have been able to maintain hummingbird pollination. This suggestion is supported by the existence of hummingbird-pollinated species closely related to S. fernandeziana in southern South America (Arroyo, 1981
), the probable origin of this species (Peña et al., 2000
).
Because fertilized flowers take more than a year to develop into fruits, experimental crosses to absolutely determine the breeding system of S. fernandeziana were not possible. Self-pollen is capable of germinating and growing in self-stigmas and styles, but self-pollen tubes were not observed penetrating the ovules. However, open-pollinated flowers showed pollen tubes entering the ovules. Under this scenario, ovarian self-incompatibility may be operating in this species, as previously found in several members of the family (Gibbs and Bianchi, 1999
), but additional experimental data are needed.
With a large simultaneous floral display on individuals, as in this species, pollinators (particularly hummingbirds) may tend to spend more time among flowers of the same individual, a behavior yielding more geitonogamous than xenogamous pollen transfer, thereby increasing selfing (Lloyd and Schoen, 1992
).
Based on the P/O ratio categories proposed by Cruden (1977)
, S. fernandeziana would be obligately xenogamous. Nevertheless, the general pattern found in 25 endemic species from 17 families of the Juan Fernández Islands indicate that most of the cosexual species were found to be self-compatible and to promote selfing through geitonogamy (Anderson et al., 2001).
Conservation biology
It is clear that the vulnerable S. fernandeziana is prone to the direct and indirect effects of human activities and natural erosion and, within a short period of time, may become critically endangered or even extinct. As an example, the only two specimens found in the Damajuana hill populationat 430 m high along a steep cliff facein our 1991, 1996, and 1997 field studies (Anderson 1616, CONN), had disappeared in 2000, thus reducing the already few wild populations. This unfortunate fate befell the congeneric Sophora toromiro, also belonging to sect. Edwardsia, endemic to Easter Island. Once it formed part of the natural vegetation on this island, but it is now extinct in the wild and only survives in cultivation in several botanical gardens of the world (Maunder et al., 2000
). The significant corollary of the declining S. fernandeziana is the potential effect on the two hummingbird species, the "signature vertebrates" of the Juan Fernández, both of which may be imperiled by the decline of S. fernandeziana.
The possibility of having a self-incompatible breeding system, together with low fruit and seed set, low genetic diversity, and reduced population size are threats to the continued survival of this species. The ultimate fate of S. fernandeziana may depend on preserving the planthummingbird relationship including the web of organisms that affect both plant and pollinator, as suggested for the other hummingbird-pollinated species on these islands (Roy et al., 1999
; Bernardello et al., 2002
) and in general for endangered mutualisms (Kearns et al., 1998
). Hummingbirds are pollen transfer agents promoting outcrossing as well as selfing, but reciprocally, S. fernandeziana is important for the birds nutrition because when it blooms, there are comparatively few nectar-bearing species available (Skottsberg, 1928
).
Sufficient density of conspecifics is fundamental to maintain the level of inter-plant pollen transfer and of effective pollination visits (Kunin, 1997
). Many invasives (e.g., Rubus ulmifolius Schott, Rosaceae) outcompete endemic species for habitat. If they produce abundant nectar and are visited by hummingbirds, the hummingbirds may be saved, but endemics like Sophora may be lost to insufficient visitation and pollination (Brooke, 1987
; Colwell, 1989
; Bernardello et al., 2000
, 2002
). Introduced animals are a problem in another context. They may reduce the hummingbird population mainly by eating their eggs (Colwell, 1989
) or reduce the plant fruit set by eating flowers, as does the curculionid we observed. This insect species is a serious vineyard pest in Chile and Argentina (Ripa, 1983
; Artigas, 1994
). It was already known as introduced on Easter Island but not on the Juan Fernández archipelago. Unfortunately, given that it is a polyphagous species, the beetle must be consuming other endemic species on the island as well, and it should be eradicated immediately.
| FOOTNOTES |
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