Breeding system and pollination of Gesneria pauciflora (Gesneriaceae), a threatened Caribbean species
Introduction
Information on breeding systems may be critical for the development of successful strategies to facilitate recovery in rare, endemic, threatened, or endangered plant species (Cao et al., 2006; Pino-Torres and Koptur, 2009; Robertson et al., 2004; Rodríguez-Pérez, 2005). Breeding systems may influence processes at the reproductive stage that in turn influence the type of mating (selfing vs. outcrossing), the likelihood of fruit and seed production, and plant fitness. For example, Astrophytum asterias (Zucc.) Lem., a self-incompatible endangered cactus with a restricted distribution range, has a reproductive system that is highly dependent on the availability and effectiveness of its pollinators (Strong and Williamson, 2007). The same phenomenon has been shown for the threatened shrub Tetratheca juncea Sm. (Gross et al., 2003) and the endemic perennial shrub Polygala vayredae Costa (Castro, 2009; Castro et al., 2008). All of which faced reproductive constraints due to low biotic visitation rates and high pollinator dependence, which led to recommendations for management of their habitat as well as their plant-pollinator interactions to improve fruit and seed production. However, not all endangered or threatened species have an obligate pollination interaction but instead exhibit mixed pollination systems that may reduce their vulnerability (Yates and Ladd, 2004). The endangered herbs Helianthemum marifolium Mill. and H. caput-felis Boiss. are both self-compatible species that produce fruit and seeds in self-pollinated and outcrossed flowers (Rodríguez-Pérez, 2005); the endemic herb Petrocoptis viscosa Rothm, has an autonomous facultative self-pollination system that has the potential for outcrossing (Navarro and Guitián, 2002); and the endangered climbing vine species Jacquemontia reclinata House ex Small, is predominantly outcrossing but is also capable of producing fruits and seeds via late autogamy (Pino-Torres and Koptur, 2009). Thus, the observed variability in breeding system mechanisms across rare and endemic species may also be accompanied by variation in their reproductive capacity and in their demographic vulnerability.
Plants may exhibit a reduction in fitness during the pollination phase due to variation in biotic and abiotic factors, or by human-disturbance impacts through a variety of mechanisms. Large-scale disturbance events such as selective logging, metal soil contamination, wetland creation, may reduce the availability of pollinators and increase pollen limitation, but also diminish pollen loads on stigmas and in the process reduce outcrossing (Eckert et al., 2009). Likewise, forest patch isolation (habitat fragmentation) can reduce pollinator network connectivity and increase vulnerability in outcrossing species by reducing plant fitness (Vanbergen et al., 2014). Changes in climate (i.e. temperature and precipitation) by inducing early or late flowering events (Hamann, 2004; Iler and Inouye, 2013; Menzel et al., 2006) can lead to mismatches in plant-pollinator interaction that in turn may decrease fruit production (Hegland et al., 2009). Other vulnerabilities during the pollination phase may result from antagonist processes such as flower herbivory, in which pollinator' visitation rates might decrease due to a reduction in flower attractiveness, nectar production and delayed flowering (McArt et al., 2014; Schiestl et al., 2014). Given the tight link between pollination and plant fitness, it is important to evaluate the factors that influence pollination success directly or indirectly, especially for rare and endangered species as a way to gather information that may help improve natural seed production, seedling recruitment, and long-term population persistence.
For plants endemic to insular systems, the evolution of breeding systems may be influenced by ecological conditions that may characterize island ecosystems (Barrett, 1996; Charlesworth, 2006). This hypothesis, also known as Baker’s rule (Baker, 1955; Barrett, 1996), states that species with self-compatible and autonomous pollination systems should be more common in island ecosystems (relative to continental ones); where pollinator faunas are less diverse or where pollinators of species dispersing into islands are absent (Anderson et al., 2001; Ayre et al., 1994; Barrett et al., 2008; Jacquemyn et al., 2005; Wheelwright et al., 2006). Alternatively, novel pollinator interactions and generalized pollination systems are also expected in these environments (Martén-Rodríguez and Fenster, 2010; Martén-Rodríguez et al., 2009). Recent analyses comparing Gesneriaceae in mainland and island ecosystems suggested no differences in autofertiliy index between geographic areas, yet generalized systems were more evident in insular species (Martén-Rodríguez et al., 2015). While studies by Marten-Rodríguez and collaborators support some hypotheses on the evolution of plant breeding systems on islands, they also suggest that local habitats may also influence plant breeding systems. For example, rupiculous (i.e. growing on rocks) and epiphytic (i.e. growing on trees) gesneriad species exhibit autonomous breeding systems more often that terrestrial ones. One hypothesis is that on rupiculous and epiphytic habitats, autonomous breeding systems may be favored to maximize the use of available resources to reproduction under unpredictable pollinator environments (Martén-Rodríguez et al., 2015). Our target species, Gesneria pauciflora Urb., is a rupiculous species that grows along riverbanks that may experience periodic flash floods (or extended dry periods). Assuming that these habitats may offer uncertain pollinator environments as in other gesneriads, G. pauciflora may also exhibit an autonomous breeding system for reproductive assurance.
We evaluated the breeding system and pollinators of the endangered species Gesneria pauciflora Urb. (Gesneriaceae) on the island of Puerto Rico. There are five additional species of Gesneria [G. citrina Urb., G. cuneifolia (DC.) Fritsch, G. pedunculosa (DC.) Fritsch, G. reticulata (Griseb.) Urb., and G. viridiflora subsp. sintenisii (Urb) L.E. Skog], all of which are self-compatible species as one would expect on insular ecosystems (Martén-Rodríguez and Fenster, 2008). With the exception of G. reticulata, all Gesneria species reported for Puerto Rico are endemic and only G. pauciflora is classified as a threatened species under the US Endangered Species Act. This species was listed due to its narrow distribution (endemic to serpentine soils in south-western Puerto Rico) and the potential for population extinction due to large-scale natural (i.e. hurricanes, landslides or severe flooding) and human disturbances (i.e. changes in the hydrology due to water extraction) (U.S. Fish and Wildlife Services, 1995). The study of this species’ reproductive biology and ecology are identified as recovery actions in the “Recovery Plan for G. pauciflora” (U.S. Fish and Wildlife Services, 1998). However, we lack information on its reproductive biology, potential pollinators, and on vulnerabilities experienced during the pollination phase. Gesneria pauciflora is a rupiculous and riverine species that may experience periodic disturbances. Assuming that G. pauciflora’s breeding system behaves in similar ways to other rupiculous gesneriads, we hypothesized that the species may exhibit an autonomous breeding system for reproductive assurance. Herein we address the information gaps in its reproductive biology by asking the following questions: What are the main pollinator(s) of G. pauciflora? Is fruit or seed production influenced by the type of pollination (self- vs. cross)? Is the breeding system of G. pauciflora different to those reported for other Gesneria species on Puerto Rico? Our goal was to carry out a comprehensive study to evaluate the reproductive biology of G. pauciflora focusing on events occurring at the pollination stage. We also compared the breeding system characteristics of G. pauciflora to those reported for other Gesneria species in the Caribbean to explore the ecological and evolutionary context of G. pauciflora’s breeding system.
Section snippets
Study site
The Maricao State Forest has an area of 4150 ha and lies at the western end of the Cordillera Central mountain system of Puerto Rico within the municipalities of Maricao, Sabana Grande, and San Germán (Anadón-Irizarry, 2006). The protected area's topography is dominated by rugged mountains and hills with steep slopes (between 40 and 60%), the majority of which (90%) is characterized by serpentine soils (Ricart Pujals and Padrón Vélez, 2010). This particular geological substrate distinguishes
Plant-animal interaction
During the 26 days in which the LTLACON camera was placed in the field, nine flowers were open at different times but no pollinator visits were recorded. Other animals (mouse, coqui frog, crabs, dragonflies, moths, and birds) were captured by the camera confirming that the equipment was working well. The overall visitation rate was low in the species averaging 0.07 visits/plant/hour. The years 2012 and 2016 scored the lowest and highest hummingbird visitation rate with 0.05 (±0.02) and 0.1
Discussion
Based on floral morphology and the ancestral pollination system in the insular clade of the Gesneriaceae (Martén-Rodríguez et al., 2010), hummingbirds are likely the sole pollinator of G. pauciflora. Although we had observed visits by two hummingbird species, visitation rates were very low yet consistent with other island species of Gesneriaceae, ranging from 0.01 to 0.21 visits/flower/hour (Martén-Rodríguez et al., 2015). In G. pauciflora, nectar production was constant in time, yet
Acknowledgements
Funds for this study were provided by U.S. Fish and Wildlife Service (Cooperative Agreement F12C0556, 2014). We thank The Department of Natural Resources of Puerto Rico, the Fish Hatchery facilities in Maricao, the Center for Applied Tropical Ecology and Conservation, and the Department of Environmental Sciences of the University of Puerto Rico-Río Piedras Campus for their logistical support. Thanks to José Fumero and Liza García for their collaboration in data collection during the study
References (81)
- et al.
Genetic diversity of Sinojackia dolichocarpa (Styracaceae), a species endangered and endemic to China, detected by inter-simple sequence repeat (ISSR)
Biochem. Syst. Ecol.
(2006) Effects and outcomes of Caribbean hurricanes in a climate change scenario
Sci. Total Environ.
(2000)- et al.
The role of floral biology and breeding system on the reproductive success of the narrow endemic Petrocoptis viscosa Rothm. (Caryophyllaceae)
Biol. Conserv.
(2002) Hummingbirds’ nectar concentration preferences at low volume: the importance of time scale
Anim. Behav.
(1996)- et al.
Short- and long-term limitations to fruit production in a tropical orchid
Ecology
(1990) - et al.
A meager nectar offering by an epiphytic orchid is better than nothing
Biotropica
(1994) - et al.
Expanding the limits of the pollen-limitation concept: effects of pollen quantity and quality
Ecology
(2007) Distribution, Habitat Occupancy and Population Density of the Elfin-Woods Warbler (Dendroica angelae) in Puerto Rico
(2006)- et al.
Breeding system and pollination of selected plants endemics to Juan Fernández Islands
Am. J. Bot.
(2001) - et al.
Pollen limitation of plant reproduction: ecological and evolutionary causes and consequences
Ecology
(2004)
Unexpectedly high levels of selfing in the Australian shrub Grevillea barklyana (Proteaceae)
Heredity
Self-compatibility and establishment after ‘long distance’ dispersal
Evolution
Sugar concentrations in nectars from hummingbird flowers
Biotropica
Plant reproductive systems and evolution during biological invasion
Mol. Ecol.
The reproductive biology and genetics of island plants
Philos. Trans. R. Soc. B
Why do hummingbirds flowers secrete dilute nectar?
Biotropica
Evolutionary demography of orchids: intensity and frequency of pollination and the cost of fruiting
Ecology
Resource and pollen limitation to lifetime seed production in a natural plant population
Ecology
How flower biology and breeding system affect the reproductive success of the narrow endemic Polygala vayredae Costa (Polygalaceae)
Bot. J. Linn. Soc.
Biología reproductiva y conservación del endemismo Polygala vayredae
Ecosistemas
Serpentine endemism in the flora of Puerto Rico
Caribb. J. Sci.
Vascular Flora of the Rio Maricao Watershed, Maricao Commonwealth Forest, Maricao, Puerto Rico
Evolution of plant breeding systems
Curr. Biol.
Potential Autonomous selfing in Gesneria citrina (Gesneriaceae), a specializad hummingbird pollinated species with varible expression of herkogamy
J. Integr. Plant Biol.
Plant-hummingbird interactions in the West Indies: floral specialization gradients associated with environment and hummingbird size
Oecologia
Variation in pollen limitation and floral parasitism across a mating system transition in a Pacific coastal dune plant: evolutionary causes or ecological consequences?
Ann. Bot.
Responses of insect pests, pathogens, and invasive plant species to climate change in the forests of northeastern North America: what can we predict?
Can. J. For. Res.
Plant mating system in a changing world
Trends Ecol. Evol.
Consequences of floral visits by ants and invasive honeybees to the hummingbird-pollinated: Caribbean cactus Melocactus intortus
Plant Species Biol.
Reproductive assurance and the evolutionary ecology of self-pollination in Clarkia xantiana (Onagraceae)
Am. J. Bot.
Reproductive assurance and the evolution of pollination specialization
Int. J. Plant Sci.
Relative pollination effectiveness of floral visitors of Pitcairnia angustifolia (Bormeliaceae)
Am. J. Bot.
Effects of nectar robbing on pollinator behavior and plant reproductive success of Pitcairnia angustifolia (Bromeliaceae)
Plant Species Biol.
Response of a traplining hummingbird to changes in nectar availability
Behav. Ecol.
Review of the Neotropical species of the family Pterophoridae, part I: Ochyroticinae, Deuterocopinae, Pterophorinae (Platyptiliini, Exelastini, Oxyptilini) (Lepidoptera)
Zool. Meded.
Floral structure, breeding system and fruit-set in the threatened Tetratheca juncea Smith (Tremandraceae)
Ann. Bot.
Flowering and fruiting phenology of a Phillipine submontane rain forest: climatic factors as proximate and ultimate causes
J. Ecol.
How does climate warming affect plant-animal interactions?
Ecol. Lett.
Food for pollinators: quantifying the nectar and pollen resources of urban flowers
PLoS One
Effects of climate change on mast-flowering cues in a clonal montane herb, Veratrum tenuipetalum (Melanthiaceae)
Am. J. Bot.
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