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Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73 (S2): e64854, mayo 2025 (Publicado May. 15, 2025)
Climate seasonality and plant vigor effects on reproductive
phenology of Potalia turbinata (Gentianaceae) in Costa Rica
Rachel Salazar1*; https://orcid.org/0009-0001-0275-5277
Jorge González-Linares2; https://orcid.org/0009-0002-7073-597X
Mauricio Fernández Otárola3; https://orcid.org/0000-0001-9240-7569
Gilbert Barrantes4; https://orcid.org/0000-0001-8402-1930
Bernal Rodríguez-Herrera5; https://orcid.org/0000-0001-8168-2442
1. Sistema de Estudios de Posgrado, Universidad de Costa Rica, San José, Costa Rica; rachel.salazar867@gmail.com
(*Correspondence)
2. Sistema de Estudios de Posgrado, Universidad de Costa Rica, San José, Costa Rica; jorge.gonzalezlinares@ucr.ac.cr
3. Escuela de Biología y Centro de Investigaciones en Biodiversidad y Ecología Tropical (CIBET), Universidad de
Costa Rica, San José, Costa Rica; mauricio.fernandez@ucr.ac.cr
4. Escuela de Biología y Centro de Investigaciones en Biodiversidad y Ecología Tropical (CIBET), Universidad de
Costa Rica, San José, Costa Rica; gilbert.barrantes@ucr.ac.cr
5. Escuela de Biología y Centro de Investigaciones en Biodiversidad y Ecología Tropical (CIBET), Universidad de
Costa Rica, San José, Costa Rica; bernal.rodriguez@ucr.ac.cr
Received 31-VIII-2024. Corrected 20-IV-2025. Accepted 21-IV-2025.
ABSTRACT
Introduction: Potalia turbinata (Gentianaceae) is a treelet distributed from Nicaragua to Panama. Information
on its reproductive biology and phenology is lacking.
Objective: To describe the reproductive phenology of P. turbinata, morphologically characterize its fruits and
seeds, and determine whether flower and fruit production correlates with climate (temperature and precipita-
tion) and plant vigor.
Methods: The research took place at Tirimbina Biological Reserve in Costa Rica, January 2017–March 2019.
Monthly counts of flowers and fruits were conducted on 86 plants. We used circular statistics to determine the
duration and peak of flowering and fruiting. Fruit production was compared between years to describe repro-
ductive cycles. We correlated flower and fruit abundance with climatic conditions. Plant measurements included
height, basal stem diameter, leaf crop, seeds per fruit, fruit and seed dimensions, and fruit hardness. We used
height, diameter, and number of leaves as proxies for plant vigor and compared plant vigor between fruiting (i.e.,
number of fruits) and non-fruiting plants.
Results: Flowering lasted 2–6 months per plant, peaking in April, while fruiting was prolonged (3–10 months),
moderately peaking in August. Flower abundance was negatively correlated with precipitation, but fruiting
showed no significant correlation with climate. Fruit production negatively correlated with plant height and
positively correlated with basal stem diameter. Non-fruiting plants had more leaves than fruiting plants.
Conclusions: At the population level, P. turbinata flowered and fruited annually. Individuals were supra-annual,
an uncommon reproductive pattern for tropical species. The correlation between flowering and lower precipita-
tion supports possible insect pollination, though direct pollinator observations remain needed. The results con-
cur with other studies indicating a correlation between fruit number and plant size. This investigation provides
information on the reproductive phenology and fruit traits of P. turbinata, laying a foundation for future research
into its interactions with pollinators and dispersers.
Keywords: flower and fruit production; Gentianaceae; treelet phenology; tropical forest; fruit morphology;
Tirimbina Biological Reserve.
https://doi.org/10.15517/rev.biol.trop..v73iS2.64854
SUPPLEMENT
SECTION: REPRODUCTION
2Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73 (S1): e64854, mayo 2025 (Publicado May. 15, 2025)
INTRODUCTION
Phenology refers to the study of life cycle
events and the seasonal timing of each event for
individuals, populations, species, and commu-
nities (Rathcke & Lacey, 1985). Plant reproduc-
tive phenology includes the timing and patterns
of flowering and fruiting (Engel & Martins,
2005; Boyle & Bronstein, 2012; Numata et al.,
2022). Reproductive phenological events are
influenced by abiotic factors such as precipita-
tion and temperature, ecological interactions
with pollinators and dispersers (Pires et al.,
2018), as well as phylogenetic and genetic
constraints (Wright & Calderon, 1995; Fenner,
1998; Wilczek et al., 2010; Du et al., 2020).
Investigating the phenological strategies and
life cycles of plants provides insights into their
reproduction and survival (Rathcke & Lacey,
1985) as well as their interactions with herbi-
vores and other animals which use the plants
(van Schaik et al., 1993). Detailed information
on reproductive phenology is still lacking for
many tropical plant species.
Phenological patterns are more variable in
tropical wet forests than temperate and tropical
dry forests as the environment supports flower-
ing and fruiting year-round (Opler et al., 1980;
Boyle & Bronstein, 2012). Variation in tropical
plant phenology is reflected in their diverse pat-
terns that include subannual (reproducing more
than once per year), annual (reproducing once
a year), continuous (flowering and fruiting all
year), and supra-annual cycles (one reproduc-
tive cycle over more than one-year) (Newstrom
et al., 1994). Temperate plant species are more
RESUMEN
Efectos de la estacionalidad climática y el vigor de las plantas sobre la fenología reproductiva
de Potalia turbinata (Gentianaceae) en Costa Rica
Introducción: Potalia turbinata (Gentianaceae) es un arbusto distribuido desde Nicaragua hasta Panamá. La
información sobre la biología de esta especie es escasa y se desconoce su fenología reproductiva.
Objetivo: Describir en detalle la fenología reproductiva de P. turbinata, caracterizar morfológicamente sus frutos
y semillas, y determinar si la producción de frutos y flores se correlaciona con el clima (temperatura y precipit-
ación) y el vigor de la planta.
Métodos: La investigación se llevó a cabo en la Reserva Biológica Tirimbina, Sarapiquí, Costa Rica, desde enero
2017 hasta marzo 2019. Se realizaron conteos mensuales de flores y frutos en 86 plantas. Se utilizaron estadísticas
circulares para determinar la duración y el pico de las fenofases de flores y frutos. La producción de frutos se com-
paró entre años para describir los ciclos reproductivos. Se probó la correlación entre la cantidad de flores y frutos
y la estacionalidad climática. Las mediciones de las plantas incluyeron altura, diámetro basal del tallo, número de
hojas, semillas promedio por fruto, dimensiones de frutos y semillas, y dureza de los frutos. El vigor de la planta
(altura, diámetro basal, número de hojas fueron variables usadas como una aproximación de vigor) se evaluó en
relación con el tamaño de la cosecha de frutos.
Resultados: La floración duró entre 2 y 6 meses por planta, con un pico en abril, mientras que la fructificación
fue prolongada (3–10 meses), con un pico moderado en agosto. La abundancia de flores se correlacionó negativa-
mente con la precipitación, pero la fructificación no mostró una correlación significativa con el clima. La produc-
ción de frutos se correlacionó negativamente con la altura de la planta y positivamente con el diámetro basal del
tallo. Las plantas sin frutos tenían más hojas que las plantas con frutos.
Conclusiones: A nivel de población P. turbinata tiene un ciclo reproductivo anual pero los individuos tienen una
reproducción irregular supra-anual, un ciclo reproductivo poco común en especies tropicales.
La correlación entre la floración y menor precipitación respalda la posibilidad de polinización por insectos,
aunque aún se requieren observaciones directas de polinizadores. Los resultados coinciden con otros estudios que
indican una correlación entre el número de frutos y el tamaño de la planta. Esta investigación aporta información
sobre la fenología reproductiva y las características de los frutos de P. turbinata, sentando las bases para futuras
investigaciones sobre sus interacciones con polinizadores y dispersores.
Palabras clave: producción de flores y frutos; Gentianaceae; fenología de arbustos; bosque tropical; morfología
de frutos; Reserva Biológica Tirimbina.
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Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73 (S2): e64854, mayo 2025 (Publicado May. 15, 2025)
seasonal and predictable than tropical species
and often closely follow temperature, precipita-
tion, and light diel cycles (Ting et al., 2008).
In a tropical dry forest, where water stress
influences reproductive phenology, tree species
tend to flower in response to seasonal rainfall,
with dry-season flowering linked to drought-
resistant species (Lasky et al., 2016).
Precipitation influences productivity and
seasonality in tropical environments (Brearley
et al., 2007). Many studies report that fruiting
intensity and peaks increase with precipita-
tion in tropical rainforests (Mendoza et al.,
2017; Dunham et al., 2018), and in Costa Rica,
understory species show a fruiting peak in
the second half of the year during the rainier
period (Opler et al., 1980; Boyle & Bronstein,
2012). Understory species have irregular flow-
ering in rain forests, but more commonly,
shrubs show higher flower production during
the less rainy period at the beginning of the year
(Opler et al., 1980).
Plant flowering and fruiting are often
influenced by plant size because larger plants
can allocate more resources for reproduction
(Ollerton & Lack, 1998; Fernández Otárola et
al., 2013), and investigating the relationship
between plant size and fruit production pro-
vides insight about the strategies implemented
by the plant (e.g., resource allocation and size
at reproductive maturity). Larger plants tend
to have more and/or larger fruits (Herrera,
1993). A study on the legume Lotus cornicula-
tus showed that larger plants produced more
fruits and had lower seed predation (Ollerton
& Lack, 1998). In a wet tropical forest of Costa
Rica, 17 tree species showed the same pattern,
with larger plants producing more fruits; tree
size also predicted whether a plant reproduced
(Minor & Kobe, 2019). A study in a lowland
conifer forest investigated the effect of plant
size, plant age, site factors, and canopy density
on flower and fruit production of nine under-
story shrubs; the study stated that plant size
(closely followed by plant age) was the main
factor in predicting flower and fruit quantities
(Wender et al., 2004).
The family Gentianaceae comprises 16
genera and 30 hermaphroditic species in Costa
Rica (Sánchez, 2010). These species predomi-
nantly consist of herbs, although there are some
shrubs, trees, mycoheterotrophs, and epiphytes
(Sánchez, 2010). Potalia turbinata Struwe & V.
A. Albert is an understory treelet and the only
species of the genus in Costa Rica. Flowers of
P. turbinata have been observed from March
to May, and fruits in May, July, September, and
December (Struwe & Albert, 2004). There is
currently no formal description of the phenol-
ogy of this plant or the other eight species in the
genus (Frasier et al., 2008).
Information on the reproductive phenol-
ogy of P. turbinata would facilitate the study of
their use by floral visitors and frugivorous spe-
cies. Potalia turbinata is known to be utilized by
bats; for instance, Vampyriscus nymphaea uses
its leaves to build conical tents as refuge and
feeding sites (Villalobos-Chaves et al., 2016).
Tent construction may reduce flower produc-
tion by limiting the foliar area exposed to the
low light in the forest understory (Rodríguez-
Herrera et al., 2018). Describing the phenology
of P. turbinata establishes a foundation for fur-
ther studies on the dynamics of its interactions
with associated fauna.
The aim of this study was: 1) to describe
the reproductive phenology of P. turbinata and
the morphological characteristics of its fruits
and seeds, 2) to determine whether rainfall and
temperature correlate with flower and fruit pro-
duction in the population, and 3) to evaluate if
plant vigor (height, basal stem diameter, and
number of leaves) correlates with fruit produc-
tion. We expected P. turbinata to adjust its phe-
nology to maximize reproductive success. Since
this species is likely insect-pollinated (Rincón
et al., 1999), we predict that it will flower during
the early months of the year when precipitation
decreases and conditions are more favorable
for insect pollinators (Janzen, 1967). On the
contrary, we expected that fruiting occur with
the onset of heavier rains in the latter half of
the year, as happens in many insect-pollinated
plants in rainforests. Temperature exhibits min-
imal variation throughout the year and should
4Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73 (S1): e64854, mayo 2025 (Publicado May. 15, 2025)
not correlate with either of the phenophases
(flowering and fruiting). We expected plant
vigor to correlate with fruit production.
MATERIALS AND METHODS
Study site and species: We conducted
this study at the Tirimbina Biological Reserve
(hereafter Tirimbina), Heredia province, Costa
Rica (10°25’ N; 84°47’ W). Tirimbina includes
345 ha mostly covered by mature rain forest
(Holdridge et al., 1971). The mean annual tem-
perature and precipitation are 24.3 °C and 3 777
mm respectively, with an elevation of 180–220
m asl (Ley-López & Avalos, 2017). The rainy
season occurs from May through November,
while the dry season extends from December
through April.
Potalia turbinata is endemic to Central
America and has a restricted and patchy distri-
bution in southeastern Nicaragua, northeastern
Costa Rica, and northeastern Panama (Struwe
& Albert, 2004; Sánchez, 2010). Its habitat
ranges from sea level to 700 m (Sánchez, 2010).
This species is a pachycaul understory shrub
or treelet with a height up to 4.5 m. The leaves
are simple, 30–75 cm long and 7.5–18 cm wide,
oblanceolate, and grouped distally on branches
(Sánchez, 2010). The flowers are produced on
a compact corymbose-cymose inflorescence,
with up to 30 flowers that vary in color from
white, yellow, pale green, yellow-green, or green
(Struwe & Albert, 2004; Sánchez, 2010). The
green fruits are turbinate with a transverse
ring and may darken slightly as they mature
(Sánchez, 2010).
Phenology: We located, marked, and
quantified P. turbinata plants in a high-den-
sity area along the Ajillo trail (ca. 805 m
long), including all individuals within 10 m on
either side of the trail. We sampled monthly
from January 2017 to March 2019, covering a
total of 27 months. A total of 83 P. turbinata
plants were sampled in 2017, increasing to 86
in 2018 and at the beginning of 2019. Sam-
pling frequency may affect the interpretation
of phenological patterns. For tropical trees, it
is advised to sample every two weeks, but if
monthly sampling is chosen, a minimum of 25
trees are recommended (Morellato et al., 2010).
Fournier and Charpantier (1975) comment
that monthly observations are appropriate to
obtain a good representation of tree phenology;
particularly in species that phenological phases
change slowly as is the case of Potalia turbinata
that changes slowly from flowering to fruit-
ing and fruit maturation (Rodríguez-Herrera,
unpubl.). Hence, we considered monthly sam-
pling appropriate.
During each survey, we counted flower
buds, flowers in anthesis, and fruits for each
plant, rather than per inflorescence. The num-
ber of inflorescences was not recorded. Imma-
ture and mature fruits were grouped together
due to difficulty in distinguishing their devel-
opment conditions because of the lack of con-
spicuous changes in color or size. To classify the
different reproductive stages of the plant, the
reproductive structures were classified as flow-
er buds if plants had unopened flowers, flower-
ing if at least one flower was open, and fruiting
if they had fruits at any stage of development.
A plant could have more than one reproductive
stage at a time.
The CircStat package (Berens, 2009) was
used to determine the circular mean and the
value of the vector-r for each phenophase.
Vector-r varies between 0 and 1, where values
closer to 1 indicate a strong seasonality (i.e., a
defined peak), and values closer to 0 indicate
low or absence of seasonality. To determine
if the circular distribution was seasonal, we
applied the Rayleigh test (Zar, 1999). This
information facilitated the determination of
the duration, peak, and frequency of the flower
and fruit phenophases at the population level.
Data from 83 plants from 2017 and 2018 were
combined in this analysis.
We implemented a Student’s t-test to com-
pare fruit production between 2017 and 2018
to assess interannual variability as basal infor-
mation on the annual variation in resources
for animals. Fruit production data were log-
transformed to improve normality. Normality
was assessed using the Shapiro-Wilk test, and
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Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73 (S2): e64854, mayo 2025 (Publicado May. 15, 2025)
variance homogeneity was tested using Lev-
ene’s test. Fruit production is defined as the
maximum number of fruits observed on each
plant at a given census rather than cumulative
fruit output over the entire reproductive season.
This method was chosen because cumulative
fruit counts were not feasible in our monthly
sampling design, and the maximum observed
count provides a standardized comparison
across individuals and years.
We tested for correlation (Pearson’s cor-
relation) between monthly 24-hour average
precipitation and temperature with monthly
total numbers of flowers and fruits in the popu-
lation during the study period. To account for
potential time-lagged effects of climate season-
ality on the reproductive phenology, we tested
for correlations with 0-, 1-, 2-, and 3-month
offsets of meteorological data. Climate data
with records for the duration of the study were
obtained from a local weather station at Tir-
imbina. This analysis helps determine whether
climatic factors such as rainfall or temperature
act as cues for triggering flowering and fruiting,
potentially influencing pollination success and
seed dispersal.
Plant morphological traits: We recorded
the morphological measurements for 81 plants
in January 2019. We measured the height of
each plant from the ground to the top of the
apical meristem, basal stem diameter at 10
cm above ground, and recorded the num-
ber of fully developed leaves per plant. Three
plants had modified leaves in 2018, presumably
altered by tent-roosting bats. These leaves were
included in the study as they were still living
and attached to the plant. Additionally, these
plants had already initiated their reproductive
cycles before leaves were modified.
In addition to the plant vigor traits, we
measured fruit and seed characteristics. Fruits
with well-developed transverse rings were col-
lected from plants near the study area to mea-
sure their morphological characteristics (2–10
fruits per plant), such as weight (OHAUS Scout
Pro scale, model SPE 123), length, and width at
the widest point of each fruit’s transverse ring.
A total of 185 fruits from 27 plants were col-
lected (19 in August 2017, 106 in October 2017,
and 60 in November 2018), and fruit hardness
was determined for 132 fruits. Fruit hardness,
defined as the strength required to perforate
the exocarp and mesocarp and access the seeds,
was estimated using a penetrometer with a 2
mm chisel (Chatillon, model DPPH-100). The
chisel was aligned perpendicular to the fruits’
transverse rings. We weighed 150 seeds from
30 fruits collected from 10 plants, with five
seeds taken per fruit, using a precision lab scale
(Sartorius, model GMBH 2842), and measured
their length, width, and thickness. Fruit and
seed dimensions were measured with a dial
caliper (SPI, model 31-414-6).
Plant vigor effects on fruit production:
To evaluate the effect of plant vigor on fruit
production of P. turbinata, we used a general
linear model with fruit production per plant
as the response variable and height, basal stem
diameter, and number of leaves as explana-
tory variables. The explanatory variables were
standardized (mean-centered and scaled by
standard deviation) to allow for interpreta-
tion of model coefficients on a common scale.
This analysis focused on data from the 2018
reproductive season because vigor traits from
the previous year were incomplete. Addition-
ally, we tested whether plant vigor traits dif-
fered between fruiting and non-fruiting plants
using a general linear model, with each trait
as a response variable and reproductive status
(fruiting vs. non-fruiting) as the explanatory
variable. Since a minimum reproductive size
has not been formally established for P. t u r bi -
nata, no size threshold was applied to exclude
potential juveniles among the non-fruiting
plants. Additionally, individuals at the mini-
mum recorded height and basal stem diameter
in our dataset were observed fruiting. All statis-
tical analyses were conducted in R v.4.0 (R Core
Team, 2024).
6Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73 (S1): e64854, mayo 2025 (Publicado May. 15, 2025)
RESULTS
Phenology: Flower buds began in Febru-
ary, with a peak in March (Fig. 1A). Records
of open flowers began in March and peaked in
April (Fig. 1B), about a month after the flower-
bud peak. Fruit production was prolonged,
starting in April and continuing until February
of the following year, with peak production
occurring in May, July, and August (Fig. 1C);
June 2018 was not sampled, and this may have
affected the fruiting pattern observed in Fig.
1C. Flower bud and flower production were
highly seasonal, with a significant unimodal
pattern (Fig. 1A, Fig. 1B). However, fruit pres-
ence showed a more prolonged, barely seasonal
pattern (Fig. 1C). The onset of the different
floral stages did not vary between the two sam-
pling years.
The presence of fruits lasted for up to 10
months from the initial detection of the fruit-
ing phase until all fruits had either fallen from
the plants or been removed. The fruiting period
of individual plants averaged 7 months with a
range of 3 to 10 months. Flower bud and flower
presence per plant ranged from 2 to 6 months.
The number of plants flowering each year
varied up to 369%. There were 13 flowering
plants in 2017, 48 in 2018, and 20 by March
2019. All plants that flowered in 2017 and 2018
produced fruits; observations in 2019 ended
before the fruiting phase. Nine plants (69.2 %)
flowered subsequently from 2017 to 2018, and
18 plants (37.5 %) from 2018 to March 2019.
Four plants that produced flowers in 2017 also
produced flower buds in 2019, three of which
flowered all three years.
Fruit production was significantly lower in
2017 than 2018 (28.15 ± 21.24 SD versus 43±
27.16 SD: t = -2.07, df = 56, p = 0.043). The
number of fruits per plant at the peak count
ranged between 10 to 81 in 2017, and 4 to 136
fruits in 2018. The mean value of the peak count
of fruits per fruiting plant during the study was
39.67 (± 26.53 SD) and for flowers it was 29.94
(± 21.81 SD). The number of flowers observed
per plant ranged from 2 to 107. The maximum
fruit count across the population was 344 fruits
in June 2017 and 1667 in May 2018. Flower
buds and flowers considered together had a
maximum count across the population of 543
in 2017 and 1658 in 2018, both in March.
The number of flowers in the population
correlated negatively with monthly precipita-
tion (r=-0.442, p=0.040), so the number of
flowers increased when precipitation decreased.
However, the number of fruits did not correlate
with precipitation (r=0.359, p=0.101). Flower-
ing remained negatively correlated with precip-
itation at a 1-month offset (r=-0.451, p=0.040),
but this relationship weakened at 2-month (r=-
0.087, p=0.709) and 3-month offsets (r=-0.046,
p=0.842). Fruit production did not correlate
significantly with precipitation at any offset
Fig. 1. Rose graphs of reproductive phenology in Potalia turbinata (Gentianaceae) showing the percentage of individuals
with: A. flower buds, B. open flowers, and C. fruits. The arrow indicates the circular mean, and its length represents the value
(0-1) of the vector-r (greater length equals greater seasonality). P-values for the Rayleigh test indicate a clear seasonality of
the three reproductive stages.
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Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73 (S2): e64854, mayo 2025 (Publicado May. 15, 2025)
(all p>0.1). Flowering (r=0.017, p=0.939) and
fruiting (r=-0.170, p=0.449) did not correlate
with temperature which had a 24-hour aver-
age monthly temperature of 25.5 °C, with a
narrow range from 22.4 to 31.7 °C during the
study. Correlations with temperature were non-
significant across all offsets (all p-values>0.1).
Plant morphological traits: Table 1 sum-
marizes the measurements of the plants, fruits,
and seeds. Of the 81 plants measured in January
2019, 55.6% had fruited in 2018.
Plant vigor effects on fruit production:
Among the analyzed plant vigor traits, basal
stem diameter showed a strong positive correla-
tion with fruit production (Table 2). In contrast,
taller plants were associated with lower fruit
production (Table 2; Fig. 2). Of these variables,
only the number of leaves was significantly
Table 1
Descriptive values of plant vigor, fruit, and seed traits of Potalia turbinata (Gentianaceae).
Plant vigor traits Height (cm) Basal Stem Diameter (cm) Number of Leaves
Mean ± SD 245.7 ± 80.4 3.2 ± 0.8 16.9 ± 6.2
Range 60–450 1.9-5.1 4–38
Fruit traits Weight (g) Length (mm) Width (mm) Hardness (N)
Mean ± SD 2.7 ± 0.5 18.9 ± 1.1 21.3 ± 1.6 44.6 ± 8.1
Range 1.4–3.9 16.0–21.5 16.1–24.7 16.0–68.0
Seed traits Seeds per Fruit Weight (mg) Length (mm) Width (mm) Thickness (mm)
Mean ± SD 36.2 ± 7.3 13.8 ± 2.8 4.8 ± 0.4 2.9 ± 0.3 1.4 ± 0.2
Range 11.0–46.0 1.3–20.4 3.6–5.6 1.8–3.8 0.8–1.9
Table 2
Results of a GLM on the effect of plant vigor traits on fruit production in Potalia turbinata (Gentianaceae).
Factor Estimate S.E. t-value P-value
Intercept 42.91 2.95 14.53 <0.001
Height -12.51 4.24 -2.95 0.005
Diameter 26.24 4.23 6.21 <0.001
No. leaves 4.51 3.00 1.50 0.140
Fig. 2. The relationship between A. plant height, B. basal stem diameter, and C. number of leaves with fruit production in
plants of Potalia turbinata (Gentianaceae) in Costa Rica.
8Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73 (S1): e64854, mayo 2025 (Publicado May. 15, 2025)
higher in non-fruiting plants (p=0.007); the
other two variables did not differ between fruit-
ing and non-fruiting plants (Fig. 3).
DISCUSSION
Phenology: Phenological patterns in flow-
ering and fruiting often differ between indi-
vidual and population levels (Sakai et al., 2005;
Fenner, 1998). In contrast, a study at La Selva
(20 km from Tirimbina) analyzing 226 treelets
and shrubs across 35 species found that despite
some individual variation, phenological pat-
terns at the individual level generally reflected
those of the population (Boyle & Bronstein,
2012). Potalia turbinata exhibited lower con-
sistency between individual and population-
level phenology. As a population, P. turbinata
followed an annual phenological pattern, but
differed at the individual level with a small
fraction of the individuals exhibiting annual
patterns, while the majority were supra-annual.
Many species follow an annual cycle at La
Selva in accordance with precipitation fluc-
tuation, similar to the documented pattern in
Potalia turbinata at the population level (Sakai,
2001). At the individual level at La Selva, suban-
nual phenological patterns were predominant,
followed by annual patterns, while continuous
and supra-annual strategies were rare (News-
trom et al., 1994; Sakai et al., 2005), making P.
turbinata a notable exception at the individual
level. This suggests that P. turbinata individuals
may require longer recovery periods between
reproductive events, potentially due to resource
limitations or other ecological constraints.
Several factors influence fruit and seed
production, including resource allocation, floral
herbivory, and effective pollination (Cunning-
ham, 2000). Insufficient resource accumulation
in certain plant species can lead to a supra-
annual fruiting pattern, as these plants require
longer periods to replenish between fruiting
years (Fenner, 1998). Boyle and Bronstein
(2012) mentioned light variation, rainfall, and
nutrient availability as possible factors affecting
flowering and fruiting patterns; although, in
their study, precipitation was not an influencing
factor. Other contributing factors to variation
include competition and herbivory (Sakai et al.,
2005). Cunningham (2000) studied an under-
story plant and found that floral herbivory was
the main limiting factor on fruit production
followed by the proportion of flowers visited by
pollinators. Genetics may also influence plant
phenology, flowering, and fruiting (Wilczek et
al., 2010; Tang, et al., 2016). Abiotic and biotic
factors may control plants with conservative
genomes to a lesser extent (Fenner, 1998).
The average annual fruit production in
Potalia turbinata was significantly lower in
2017 than in 2018, highlighting interannual
variation in reproductive output. This varia-
tion further suggests that resource availability
and environmental factors may have a stron-
ger influence on fruit production than floral
Fig. 3. Comparison of plant vigor traits between fruiting plants and non-fruiting plants of Potalia turbinata (Gentianaceae)
in Costa Rica. Data from the year 2018: A. height, B. basal stem diameter, and C. number of leaves.
9
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73 (S2): e64854, mayo 2025 (Publicado May. 15, 2025)
herbivory, which was not observed during this
study. While we described flowering and fruit-
ing patterns, future research could examine
additional reproductive metrics, such as fruit
set and seed viability, to better understand
reproductive success in P. turbinata.
Tropical plants tend to have longer fruit-
ing periods, averaging four months (Jordano,
1992). Potalia turbinata is one example of an
extremely lengthy fruiting period at the popula-
tion level (ten months) and at the level of indi-
vidual plants (approximately seven months).
In this study, immature and mature fruits were
considered together due to difficulty in dis-
tinguishing the categories because of cryptic
color and size changes. Immature fruits in early
development present an underdeveloped trans-
verse ring. In future studies, to avoid ambiguity
while deciding whether fruits are immature or
mature, color could be measured and the diam-
eter of the fruit ring across the months could be
considered. Though it would be more demand-
ing in the field, a higher resolution of the timing
of phenological events could be achieved, such
as a more precise timing of fruit maturation.
Additionally, the start of fruit dispersal could be
used as an indicator of fruit maturity.
Potalia turbinata only had one flower-
ing period per year at Tirimbina. Flowering
took place at the beginning of the year (lower
precipitation) and fruiting at the middle to
second half of the year (higher precipitation),
which is consistent with flowering and fruit-
ing tendencies reported by Opler et al. (1980)
of treelets and shrubs in Costa Rican tropical
wet forests. Flowering periods were shorter for
supra-annual species and tended to occur in the
dry season more than for annual or subannual
plants (Bawa et al., 2003), which is similar to
P. turbinata with a population level flowering
period of four to five months during a period
of less rainfall.
Flowering in the dry season may influence
pollination success in P. turbinata by aligning
reproductive timing with seasonal changes in
pollinator availability. Tree and shrub species
pollinated by bees, butterflies, flies, and wasps
tend to reach their peak flowering during the
dry season in Venezuela (Ramírez, 2006). All
flowering plants of P. turbinata successful-
ly produced fruits and exhibited pronounced
flowering seasonality. Plants with high flower-
ing synchrony are more likely to reproduce
successfully, as they attract more pollinators
(Bruno et al., 2019). Successful cross-pollina-
tion, autonomous self-pollination, and apomix-
is are possible mechanisms contributing to seed
development. While P. turbinata had strong
flowering seasonality, its pollination strategy
remains uncertain. Rincón et al. (1999) sug-
gested that the species may be insect-pollinated,
but no direct observations confirm this. Fur-
ther research is needed to identify pollination
strategies and explore the environmental fac-
tors influencing fruit production in P. turbinata.
Though the onset of the rainy season
was not a significant determinant in the P.
turbinata fruiting cycle, the flowering signifi-
cantly correlated with less rain which in turn
led to the presence of fruit during the rainy
months. Seed germination facilitation is one
factor that may influence fruiting occurring
during the rainy season (Garwood, 1983). The
lack of correlation between temperature and
flowering and fruiting may be a consequence
of the little, non-seasonal variation in this
environmental variable.
The timing of flowering and fruiting of P.
turbinata in this study overlapped with herbar-
ium collected phenological information. Sán-
chez (2010) states that flowers are found from
March to June, while Struwe and Albert (2004)
mention March to May and specify fruiting
observations in May, July, September, and
December. This investigation further detailed
the reproductive phenophases by examining
their full extension and patterns.
Plant morphological traits: The plant
height of P. turbinata plants in this study is con-
sistent with the values reported by Struwe and
Albert (2004). The number of flowers was pre-
viously reported as up to 30 per plant (Struwe &
Albert, 2004), but we observed a range beyond
that number. We also documented a larger stem
diameter at 3.21 cm, compared to 14 mm, and
10 Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73 (S1): e64854, mayo 2025 (Publicado May. 15, 2025)
fruit size was slightly larger in this study (16–22
x 16–25 mm compared to 10–14 x 11–18 mm).
However, Struwe and Albert (2004) collected
measurements from dry material which could
lose 10–15 % of its mass. Sánchez (2010)
described the seeds as 4–5.5 mm which is in
accordance with our findings. Additionally, we
provided novel data on the number of seeds,
weight, width, and thickness, as well as fruit
hardness.
Plant and fruit morphological traits are
noteworthy for further investigations involving
fruit consumption or seed dispersal mecha-
nisms of P. turbinata. The seeds of Neotropi-
cal woody species are primarily dispersed by
vertebrates (Howe & Smallwood, 1982), and
the size of the seeds influences whether they
are ingested (Sebastián-González, 2017, Ong et
al., 2021). Smaller seeds are more likely to be
swallowed by a disperser and pass through the
digestive tract; larger seeds (> 12 mm) tend to
only be swallowed by large vertebrates includ-
ing primates, tapirs, and peccaries (Fuzessy et
al., 2018). Seed weight and length can influence
whether a seed is swallowed or dropped as well
as which frugivores act as dispersers. Large-
seeded fruits are less likely to be consumed by
birds, bats, and small mammals (Fuzessy et al.,
2018), although bats and small sized rodents
have been observed dispersing large-seeded
fruits by synzoochory (Melo et al., 2009; Ong et
al., 2021). Potalia seeds are small and numerous,
suggesting they are likely dispersed through gut
passage, as observed in Carollia perspicillata
dispersing Potalia amara seeds (Lobova et al.,
2009). Bats have also been observed removing
fruits of P. turbinata (Salazar, unpubl.). Further
investigation into Potalia seed dispersal is war-
ranted due to a lack of information.
Fruit hardness may also affect fruit con-
sumption as there is a limit to the hardness that
can be handled by different species. Dumont
(1999) documents changing behaviors of phyl-
lostomid bats when they consume fruits of
varying hardness and indicates that some spe-
cies have morphological traits that aid in con-
sumption. Additional studies on P. turbinata
could contribute information on animal diets,
particularly regarding fruit hardness.
Plant vigor effects: The height of fruiting
plants of P. turbinata was negatively correlated
with fruit production, while basal stem diam-
eter showed a positive correlation with fruit
production. These findings partially align with
previous studies reporting that tree size is often
positively associated with reproductive out-
put or influences initial reproductive activity
(Herrera, 1991; Susko & Lovett-Doust, 2000;
Fernández-Otárola et al., 2013). A study at La
Selva Biological Station of approximately 2,000
trees from 17 species showed that the number
of fruits produced could be predicted by plant
size (Minor & Kobe, 2019). This trend has also
been shown in other plants such as a cactus
species studied by Bustamante and Búrquez
(2008), which had higher flowering intensity
and plant fecundity in larger plants.
The amount of light available through
canopy gaps may influence plant size (Wender
et al., 2004). Competition can also affect plant
size, and increased plant growth usually cor-
relates with more access to resources; crowd-
ing affects the plant reaching its maximum
potential size and in turn, affects its crop size
or fecundity (Tracey & Aarssen, 2011). Fig
tree fruit production may be influenced by the
amount of time the trees are able to restore
nutrients between reproductive cycles (Huang
et al., 2019), which is another factor along with
plant size that could be considered in future
studies on P. turbinata.
The number of leaves did not correlate
with fruit production in P. turbinata when ana-
lyzing only fruiting plants, indicating that leaf
number does not directly influence the number
of fruits. However, there was a significant dif-
ference in leaf number between fruiting and
non-fruiting plants, with non-fruiting plants
having more leaves, while fruiting plants had
fewer. This pattern suggests an inverse rela-
tionship between leaf production and fruiting,
potentially driven by resource allocation trade-
offs. This finding aligns with studies show-
ing a balance between vegetative growth and
11
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73 (S2): e64854, mayo 2025 (Publicado May. 15, 2025)
reproductive effort. Wheelwright (1986) found
that fruit production and new leaf production
in the same year were negatively correlated in
12 of 15 studied tree species of the Lauraceae
family in Monteverde, Costa Rica. In most spe-
cies, vegetative growth and reproduction were
negatively associated, which may explain why P.
turbinata fruiting plants exhibited fewer leaves.
This suggests that resource allocation toward
fruit production may come at the expense of
vegetative growth. In trees, vegetative growth
(leaf production) and reproductive develop-
ment (flower and fruit production) are closely
linked (Borchert, 1983). The extent and driv-
ers of this potential trade-off in P. turbinata
remain unclear.
Previously, specific phenological informa-
tion was lacking for the genus Potalia apart
from knowing in which months flowering and
fruiting herbarium specimens were collected.
We found that P. turbinata produces flowers
and fruits annually at the population level with
varying patterns at the individual level. Higher
flower abundance coincides with drier months,
as predicted. The initial expectation of the
fruiting phenophase correlating with rainfall
was not supported. Fruit production of P. t u r -
binata correlates with plant size (height and
diameter), concurring with predictions. The
information gathered serves as a foundation
for further investigations on P. turbinata. Next
steps include identifying pollinator and dis-
perser interactions with the plant and the abiot-
ic factors that influence phenological strategies.
Ethical statement: The authors declare
that they all agree with this publication and
made significant contributions; that there is no
conflict of interest of any kind; and that we fol-
lowed all pertinent ethical and legal procedures
and requirements. All financial sources are fully
and clearly stated in the acknowledgments sec-
tion. A signed document has been filed in the
journal archives.
ACKNOWLEDGMENTS
We thank Emmanuel Rojas Valerio for his
help during the field work and Marco Vinicio
Sáenz Murillo at the Centro de Investigaciones
Agronómicas (CIA) at Universidad de Costa
Rica for his assistance in measuring the fruits
and seeds of the plant of study. Furthermore,
we would like to express our appreciation to the
staff at the Tirimbina Biological Reserve.
REFERENCES
Bawa, K., Kang, H., & Grayum, M. (2003). Relationships
among time, frequency, and duration of flowering in
tropical rain forest trees. American Journal of Botany,
90(6), 877–887. https://doi.org/10.3732/ajb.90.6.877
Berens, P. (2009). CircStat: A MATLAB Toolbox for Cir-
cular Statistics. Journal of Statistical Software, 31(10),
1–21. https://doi.org/10.18637/jss.v031.i10
Borchert, R. (1983). Phenology and control of flowering
in tropical trees. Biotropica, 15(2), 81–89. https://doi.
org/10.2307/2387949
Boyle, W. A., & Bronstein, J. L. (2012). Phenology of tropi-
cal understory trees: patterns and correlates. Revista
de Biología Tropical, 60(4), 1415–1430. https://doi.
org/10.15517/rbt.v60i4.2050
Brearley, F. Q., Proctor, J., Nagy, L., Dalrymple, G., &
Voysey, B. C. (2007). Reproductive phenology over
a 10-year period in a lowland evergreen rain forest
of central Borneo. Journal of Ecology, 95, 828–839.
https://doi.org/10.1111/j.1365-2745.2007.01258.x
Bruno, M. M. A., Massi, K. G., Vidal, M. M., & du Vall Hay,
J. (2019). Reproductive phenology of three Syagrus
species (Arecaceae) in a tropical savanna in Brazil.
FLORA, 252, 18–25.
Bustamante, E., & Búrquez, A. (2008). Effects of plant size
and weather on the flowering phenology of the Organ
Pipe Cactus (Stenocereus thurberi). Annals of Botany,
102, 1019–1030. https://doi.org/10.1093/aob/mcn194
Cunningham, S. A. (2000). What determines the number
of seed produced in a flowering event? A case study
of Calyptrogyne ghiesbreghtiana (Arecaceae). Aus-
tralian Journal of Botany, 48, 659–665. https://doi.
org/10.1071/BT99012
Du, Y., Li, D., Yang, X., Peng, D., Tang, X., Liu, H., Li, D.,
Hong, X., & Song, X. (2020). Reproductive phenology
12 Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73 (S1): e64854, mayo 2025 (Publicado May. 15, 2025)
and its drivers in a tropical rainforest national park
in China: Implications for Hainan gibbon (Nomascus
hainus) conservation. Global Ecology and Conserva-
tion, 24, e01317. https://doi.org/10.1016/j.gecco.2020.
e01317
Dumont, E. R. (1999). The effect of food hardness on fee-
ding behaviour in frugivorous bats (Phyllostomidae):
an experimental study. Journal of Zoology, 248(2),
219–229. https://doi.org/10.1111/j.1469-7998.1999.
tb01198.x
Dunham, A. E., Razafindratsima, O. H., Rakotonirina, P., &
Wright, P. C. (2018). Fruiting phenology is linked to
rainfall variability in a tropical rain forest. Biotropica,
50(3), 396–404. https://doi.org/10.1111/btp.12564
Engel, V. L., & Martins, F. R. (2005). Reproductive phenolo-
gy of Atlantic Forest tree species in Brazil: An eleven
year study. Tropical Ecology, 46(1), 1–16. 
Fenner, M. (1998). The phenology of growth and repro-
duction in plants. Perspectives in Plant Ecology,
Evolution and Systematics, 1(1), 78–91. https://doi.
org/10.1078/1433-8319-00053
Fernández-Otárola, M., Sazima, M., & Solferini, V. N.
(2013). Tree size and its relationship with flowering
phenology and reproductive output in Wild Nutmeg
trees. Ecology and Evolution, 3(10), 3536–3544.
https://doi.org/10.1002/ece3.742
Fournier, L. A., & Charpantier, C. (1975). El tamaño de
la muestra y la frecuencia de las observaciones en el
estudio de las características fenológicas de los árboles
tropicales. Turrialba, 25, 45–48.
Frasier, C. L., Albert, V. A., & Struwe, L. (2008). Amazo-
nian lowland, white sand areas as ancestral regions
for South American biodiversity: biogeographic and
phylogenetic patterns in Potalia (Angiospermae:
Gentianaceae). Organisms, Diversity & Evolution, 8,
44–57. https://doi.org/10.1016/j.ode.2006.11.003
Fuzessy, L. F., Janson, C., & Silveira, F. A. O. (2018) Effects
of seed size and frugivory degree on dispersal by
Neotropical frugivores. Acta Oecologica, 93, 41–47.
https://doi.org/10.1016/j.actao.2018.10.004
Garwood, N. C. (1983) Seed germination in a seaso-
nal tropical forest in Panama: A community study.
Ecological Monographs, 53, 159–181. https://doi.
org/10.2307/1942493
Herrera, C. M. (1991). Dissecting factors responsible for
individual variation in plant fecundity. Ecology 72,
1436–1448. https://doi.org/10.2307/1941116
Herrera, C. M. (1993). Selection on floral morphology and
environmental determinants of fecundity in a hawk
moth-pollinated violet. Ecological Monographs, 63,
251–275. https://doi.org/10.2307/2937101
Holdridge, L. R., Grenke, W. C., Hatheway, W. H., Liang, T.,
& Tosi, J. A. (1971). Forest environments in tropical life
zones: A pilot study. Pergamon Press.
Howe, H. F., & Smallwood, J. (1982). Ecology of seed dis-
persal. Annual Review of Ecology, Evolution, and Syste-
matics, 13, 201–228. https://doi.org/10.1146/annurev.
es.13.110182.001221
Huang, Y., Lee, Y., Kuo, Y., Chang, S., & Wu, C. (2019).
Fruiting phenology and nutrient content variation
among sympatric figs and the ecological correla-
tes. Botanical Studies, 60, 27. https://doi.org/10.1186/
s40529-019-0275-9
Janzen, D. H. (1967). Synchronization of sexual repro-
duction of trees within the dry season in Cen-
tral America. Evolution, 21(3), 620–637. https://doi.
org/10.2307/2406628
Jordano, P. (1992). Fruits and frugivory. In M. Fenner (Ed.),
Seeds: The Ecology of Regeneration in Plant Communi-
ties (pp. 105–156). CAB International.
Lasky, J. R., Uriarte, M., & Muscarella, R. (2016). Syn-
chrony, compensatory dynamics, and the functional
trait basis of phenological diversity in a tropical dry
forest tree community: effects of rainfall seasonali-
ty. Environmental Research Letters, 11. https://doi.
org/10.1088/1748-9326/11/11/115003
Ley-López, J. M., & Avalos, G. (2017). Propagation of
the palm flora in a lowland tropical rainforest in
Costa Rica: Fruit collection and germination patterns.
Tropical Conservation Science, 10, 1–12. https://doi.
org/10.1177/1940082917740703
Lobova, T., Geiselman, C., & Mori, S. (2009). Seed dispersal
by bats in the Neotropics. New York Botanical Garden
Press.
Melo, F., Chazdon, R. L., Medellín, R. A., Ceballos, G., &
Rodríguez-Herrera, B. (2009). Small tent-roosting
bats promote dispersal of large-seeded plants in a
Neotropical forest. Biotropica, 41(6), 737–743. https://
doi.org/10.1111/j.1744-7429.2009.00528.x
Mendoza, I., Peres, C. A., & Morellato, L. P. C. (2017). Con-
tinental-scale patterns and climatic drivers of fruiting
phenology: A quantitative Neotropical review. Global
and Planetary Change, 148, 227–241. https://doi.
org/10.1016/j.gloplacha.2016.12.001
Minor, D., & Kobe, R. K. (2019). Fruit production is
influenced by tree size and size-asymmetric crowding
in a wet tropical forest. Ecology and Evolution, 9,
1458–1472. https://doi.org/10.1002/ece3.4867
Morellato, L. P. C., Camargo, M. G. G., D’Eca Neves,
F. F., Luize, B. G., Mantovani, A., & Hudson, I. L.
(2010). The influence of sampling method, sam-
ple size, and frequency of observations on plant
phenological patterns and interpretation in tropical
forest trees. In I. L. Hudson & M. R. Keatley (Eds.),
13
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73 (S2): e64854, mayo 2025 (Publicado May. 15, 2025)
Phenological Research. Springer Science. https://doi.
org/10.1007/978-90-481-3335-2_5
Newstrom, L. E., Frankie, G. W., & Baker, H. G. (1994).
A new classification for plant phenology based on
flowering patterns in lowland tropical forest trees
at La Selva, Costa Rica. Biotropica, 26(2), 141–159.
https://doi.org/10.2307/2388804
Numata, S., Yamaguchi, K., Shimizu, M., Sakurai, G., Mori-
moto, A., Alias, N., Azman, N. Z. N., Hosaka, T., &
Satake, A. (2022).Impacts of climate change on repro-
ductive phenology in tropical rainforests of Southeast
Asia. Communications Biology, 5, 311. https://doi.
org/10.1038/s42003-022-03245-8
Ollerton, J., & Lack, A. (1998). Relationships between flowe-
ring phenology, plant size and reproductive success in
shape Lotus corniculatus (Fabaceae). Plant Ecology,
139, 35–47. https://doi.org/10.1023/A:1009798320049
Ong, L., McConkey, K. R., & Campos-Arceiz, A. (2021). The
ability to disperse large seeds, rather than body mass
alone, defines the importance of animals in a hyper-
diverse seed dispersal network. Journal of Ecology, 110,
313–326. https://doi.org/10.1111/1365-2745.13809
Opler, P. A., Frankie, G. W., & Baker, H. G. (1980). Com-
parative phenological studies of treelet and shrub
species in tropical wet and dry forests in the lowlands
of Costa Rica. Journal of Ecology, 68, 167–188. https://
doi.org/10.2307/2259250
Pires, J. P. A., Marino, N. A. C., Silva, A. G., Rodrigues, J.
F. P., Freitas, L. (2018). Tree community phenodyna-
mics and its relationship with climatic conditions in a
lowland tropical rainforest. Forests, 9(3), 114. https://
doi.org/10.3390/f9030114
R Core Team. (2024). R: language and environment for
statistical computing. R foundation for statistical com-
puting, Vienna, Austria. https://www.R-project.org/
Ramírez, N. (2006). Pollination in the Venezuelan Central
Plain: Relationships between flowering phenology,
pollination modes, and pollinating agents. Ameri-
can Journal of Botany, 93(7), 997–1006. https://doi.
org/10.3732/ajb.93.7.997
Rathcke, B., & Lacey, E. P. (1985). Phenological patterns of
terrestrial plants. Annual Review of Ecology and Syste-
matics, 16, 179–214. https://doi.org/10.1146/annurev.
es.16.110185.001143
Rincón, M., Roubik, D. W., Finegan, B., Delgado, D., &
Zamora, N. (1999). Understory bees and floral resou-
rces in logged and silviculturally treated Costa Rican
rainforest plots. Journal of the Kansas Entomological
Society, 72(4), 379–393.
Rodríguez-Herrera, B., Rodríguez, M. E., Fernández-
Otárola, M. (2018). Ecological networks between
tent-roosting bats (Phyllostomidae: Stenodermatinae)
and the plants used in a Neotropical rainforest. Acta
Chiropterologica, 20(1), 139–145. https://doi.org/10.3
161/15081109ACC2018.20.1.010
Sánchez, J. (2010). Gentianaceae. In B. E. Hammel, M. H.
Grayum, C. Herrera & N. Zamora (Eds.), Manual de
plantas de Costa Rica Vol. V. Monographs in Systema-
tic Botany from the Missouri Botanical Garden, 119,
821–840.
Sakai, S. (2001). Phenological diversity in tropical forests.
Population Ecology, 43, 77–86. https://doi.org/10.1007/
PL00012018
Sakai, S., Momose, K., Yumoto, T., Nagamitsu, T., Nagama-
su, H., Karim, A., Nakashizuka, T., & Inoue, T. (2005).
Plant Reproductive Phenology and General Flowe-
ring in a Mixed Dipterocarp Forest. In D. W. Roubik,
S. Sakai, A. A. Hamid Karim (Eds.), Pollination ecolo-
gy and the rain forest. Ecological studies (analysis and
synthesis) (Vol.174). Springer.
Sebastián-González, E. (2017). Drivers of species’ role
in avian seed-dispersal mutualistic networks. Jour-
nal of Animal Ecology, 86, 878–887. https://doi.
org/10.1111/1365-2656.12686
Struwe, L., & Albert, V. (2004). A Monograph of Neo-
tropical Potalia Aublet (Gentianaceae: Pota-
lieae). Systematic Botany, 29, 670–701. https://doi.
org/10.1600/0363644041744428
Susko, D. J. & Lovett-Doust, L. (2000). Plant-size and fruit-
position effects on reproductive allocation in Alliaria
petiolata (Brassicaceae). Canadian Journal of Botany,
78(11), 1398–1407. https://doi.org/10.1139/b00-110
Tang, J., Korner, C., Muraoka, H., Piao, S., Shen, M., Thac-
keray, S. J., & Yang, X. (2016). Emerging opportunities
and challenges in phenology: a review. Ecosphere,
7(8), e01436. https://doi.org/10.1002/ecs2.1436
Ting, S., Hartley S., & Burns, K. C. (2008). Glo-
bal patterns in fruiting seasons. Global Ecolo-
gy and Biogeography, 17, 648–657. https://doi.
org/10.1111/j.1466-8238.2008.00408.x
Tracey, A. J., & Aarssen, L. W. (2011). Competition and
body size in plants: the between-species tradeoff for
maximum potential versus minimum reproductive
threshold size. Journal of Plant Ecology, 4(3), 115–122.
https://doi.org/10.1093/jpe/rtr008
Van Schaik, C. P., Terborgh, J. W., & Wright, S. J. (1993). The
phenology of tropical forests: Adaptive significance
and consequences for primary consumers. Annual
Review of Ecology and Systematics, 24, 353–377.
https://doi.org/10.1146/annurev.es.24.110193.002033
Villalobos-Chaves, D., Vargas Murillo, J., Rojas-Valerio,
E., Keeley, B. W., & Rodríguez-Herrera, B. (2016).
Understory bat roosts, availability and occupation
patterns in a Neotropical rainforest of Costa Rica.
Revista de Biología Tropical, 64(3), 1333–1343. https://
doi.org/10.15517/rbt.v64i3.21093
14 Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73 (S1): e64854, mayo 2025 (Publicado May. 15, 2025)
Wender, B. W., Harrington, C. A., & Tappeiner, J. C., II.
(2004). Flower and fruit production of understory
shrubs in western Washington and Oregon. Northwest
Science, 78(2), 124–140.
Wheelwright, N. T. (1986). A seven-year study of indivi-
dual variation in fruit production in tropical bird-
dispersed tree species in the family Lauraceae. In
A. Estrada & T. H. Fleming (Eds.), Frugivores and
seed dispersal (pp. 19–35). Springer. https://doi.
org/10.1007/978-94-009-4812-9_3
Wilczek, A. M., Burghardt, L. T., Cobb, A. R., Cooper,
M. D., Welch, S. M., & Schmitt, J. (2010). Genetic
and physiological bases for phenological respon-
ses to current and predicted climates. Philosophical
Transactions of the Royal Society of London. Series B,
Biological Sciences, 365(1555), 3129–3147. https://doi.
org/10.1098/rstb.2010.0128
Wright, S. J., & Calderon, O. (1995). Phylogenetic patterns
among tropical flowering phenologies. Journal of Eco-
logy, 83(6), 937–948. https://doi.org/10.2307/2261176
Zar, J. H. (1999). Biostatistical Analysis (4th ed.). Prentice
Hall.