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Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73: e2025456, enero-diciembre 2025 (Publicado Set. 17, 2025)
Light preferences, population structure, and pre-dispersal fruit predation
in the reverse-phenology tree Bonellia nervosa (Primulaceae)
Gerardo Avalos1,2*; https://orcid.org/0000-0003-2663-4565
Esteban Marín-Castillo1; https://orcid.org/0009-0005-7129-694X
Valeria Acevedo-Fernández1; https://orcid.org/0009-0006-4620-8597
Esteban Zamora-Villalobos1; https://orcid.org/0009-0002-1980-3738
Tadeo Aguilar-Bermúdez1; https://orcid.org/0009-0009-8055-687X
1. Escuela de Biología, Universidad de Costa Rica, San José, Costa Rica; gerardo.avalos@ucr.ac.cr (*Correspondence), este-
ban.marincastillo@ucr.ac.cr, raquel.acevedo@ucr.ac.cr, esteban.zamoravillalobos@ucr.ac.cr, tadeo.aguilar@ucr.ac.cr
2. The School for Field Studies, Center for Ecological Resilience Studies, P.O. Box 506 West Boxford, MA 01885, United
States of America; gavalos@fieldstudies.org
Received 11-XI-2024. Corrected 30-IV-2025. Accepted 02-IX-2025.
ABSTRACT
Introduction: Bonellia nervosa is a dry forest understory tree with reverse leafing phenology, as it produces
leaves during the dry season and is deciduous during the wet season. Being a phreatophytic species, it relies on
substantial root biomass to access groundwater and flush leaves during the dry season.
Objective: To assess the population structure of B. nervosa in Santa Rosa National Park, Costa Rica; analyze the
relationship between stem diameter and plant height; and examine how canopy structure and light availability
influence its local abundance. Also, to evaluate fruit maturity and pre-dispersal fruit predation during the late
wet season to understand its reproductive success.
Methods: The study was conducted along the Indio Desnudo trail (6.16 ha). Hemispherical photographs were
taken at each B. nervosa (n = 33) and at 10 random sites where the species was absent. Principal component
analysis was used to consolidate seven light and canopy structural variables. The Chapman-Richards model was
applied to examine the relationship between stem diameter and height. Fruit weight and seed count were ana-
lyzed and each fruit inspected for the presence of Tortricidae larvae.
Results: Adults dominated the population. An inflection point was identified at 70.6 cm in height, indicating
a shift from relatively rapid to progressively slower growth. Bonellia nervosa sites had higher canopy openness
(14.68 %) and transmitted more diffuse light (21.05 μmol/m²/s) than sites where the species was absent (12.42
% and 18.22 μmol/m²/s, respectively). Pre-dispersal fruit predation was low (16 % of fruits, n = 39) and by
Tortricidae larvae.
Conclusions: Seedling scarcity creates a recruitment bottleneck. The dominance of adults, the low number of
seedlings, and specific light preferences limit the plasticity and adaptive capacity of B. nervosa to environmental
changes. Future research should focus on the physiological mechanisms underlying B. nervosas reverse leaf phe-
nology and its resilience to climate change.
Keywords: phenological strategies; reverse phenology; pre-dispersal seed predation; tropical dry forests.
https://doi.org/10.15517/pmde0d11
TERRESTRIAL ECOLOGY
2Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e2025456, enero-diciembre 2025 (Publicado Set. 17, 2025)
INTRODUCTION
Tropical dry forests rank among the most
endangered terrestrial ecosystems (Buchadas
et al., 2022; Miles et al., 2006; Murphy & Lugo,
1986; Sánchez-Azofeifa et al., 2013; Siyum,
2020), having been some of the first to be
extensively altered by recent human activity
(Buchadas et al., 2022; Janzen et al., 2016). As
a result, old-growth, mature tropical dry forests
are now rare, and most remaining areas are
disturbed or undergoing regeneration (Duan et
al., 2023; Griscom & Ashton, 2011; Quesada et
al., 2009). These forests endure a pronounced
seasonal drought (4-6 months) characterized by
high temperatures and significant water deficits
(Murphy & Lugo, 1995) and have evolved a dis-
tinctive phenology adapted to episodic growth
(Frankie et al., 1974; Janzen, 1967). During the
wet season, plants flush leaves and accumulate
reserves for reproduction during the following
dry period. As drought intensifies, most spe-
cies shed their leaves, reproduce, and release
seeds near the end of the dry period. With the
onset of the rains, seedlings establish and store
resources to withstand the prolonged drought
of the dry season (Janzen, 1967). While these
forests support a range of phenological strate-
gies to cope with extreme seasonality (Giraldo
& Holbrook, 2011; Lasky et al., 2016; Lópezara-
iza-Mikel et al., 2013), one particularly distinc-
tive adaptation is reverse phenology (Giraldo &
Holbrook, 2011; Janzen, 1970).
Bonellia nervosa is a dry forest under-
story tree exhibiting reverse leaf phenology.
Unlike most plants in this ecosystem, which
are deciduous during the prolonged dry season
and retain leaves in the wetter months (Frankie
et al., 1974; Murphy & Lugo, 1986; Murphy
& Lugo, 1995), B. nervosa produces a new
crop of leaves only during the dry period and
sheds them at the onset of the rains (Chaves &
RESUMEN
Preferencias de luz, estructura poblacional y depredación predispersión
de frutos en el árbol de fenología inversa Bonellia nervosa (Primulaceae)
Introducción: Bonellia nervosa es un árbol del sotobosque del bosque seco tropical con fenología foliar invertida
al producir hojas durante la estación seca y ser caducifolio durante la estación lluviosa. Esta especie freatofítica
depende de una biomasa radicular considerable para acceder al agua subterránea y desarrollar hojas durante la
estación seca.
Objetivo: Evaluar la estructura poblacional de B. nervosa en el Parque Nacional Santa Rosa, Costa Rica; analizar
la relación entre el diámetro del tallo y la altura de la planta; y examinar cómo la estructura del dosel y la dis-
ponibilidad de luz influyen en su abundancia local. También evaluar la madurez de los frutos y la depredación
predispersión al final de la estación lluviosa para entender su éxito reproductivo.
Métodos: El estudio se realizó a lo largo del sendero Indio Desnudo (6.16 ha). Se tomaron fotografías hemisféricas
de cada individuo de B. nervosa (n = 33) y en 10 sitios aleatorios donde la especie estaba ausente. Se utilizó análisis
de componentes principales para consolidar variables relacionadas con la luz y la estructura del dosel. Se aplicó
el modelo de Chapman-Richards para examinar la relación entre el diámetro del tallo y la altura. Se analizaron
el peso de los frutos y el número de semillas, y se inspeccionó cada fruto para detectar la presencia de larvas de
Tortricidae.
Resultados: La población estuvo dominada por adultos. Se identificó una transición de un crecimiento relati-
vamente rápido a uno progresivamente más lento a los 70.6 cm de altura. Los sitios con B. nervosa presentaron
mayor apertura del dosel (14.68 %) y mayor transmisión de luz difusa (21.05 μmol/m²/s) que los sitios donde la
especie estaba ausente (12.42 % y 18.22 μmol/m²/s, respectivamente). La depredación predispersión fue baja (16
% de los frutos, n = 39) y causada por larvas de Tortricidae.
Conclusiones: La escasez de plántulas genera un cuello de botella en el reclutamiento. El dominio de los adultos,
la escasez de plántulas y las preferencias específicas de luz restringen la plasticidad y capacidad de adaptación de
B. nervosa a cambios ambientales. Las investigaciones futuras deben centrarse en los mecanismos fisiológicos que
sustentan la fenología foliar invertida de B. nervosa y su resiliencia ante el cambio climático.
Palabras clave: estrategias fenológicas; fenología inversa; depredación predispersión; bosque tropical seco.
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Avalos, 2008; Janzen, 1970). This unusual phe-
nological pattern requires a highly specialized
resource-use strategy (Janzen & Wilson, 1974).
In addition to concentrating leaf production at
the beginning of the drought period, B. nervosa
also flowers and initiates fruit development;
fruit maturation and seed dispersal occur in
the late rainy season (Chaves & Avalos, 2008).
The plant must also accumulate reserves for
fruit expansion and survival under the shaded
conditions of the forest understory during the
wetter months (Janzen & Wilson, 1974). This
strategy requires B. nervosa to allocate a sub-
stantial portion of its biomass to root develop-
ment (Chaves, 2002; Janzen, 1970), allowing it
to access the water table and clearly defining
it as a phreatophytic species. Similar leaf phe-
nology and biomass allocation strategies have
been observed in other phreatophytes, such as
Faidherbia albida in the arid forests of the Sahel
region in West Africa (Roupsard et al., 1999). A
reverse leafing phenology allows B. nervosa to
fix carbon during the dry season, maintaining
a competitive advantage relative to deciduous
plants. This strategy results in overall slow
growth (and growth in pulses, Schwinning &
Kelly, 2013), particularly during the seedling
stage, as the plant must first develop a suffi-
ciently large root system to tap the water table.
Bonellia nervosa establishes itself primar-
ily in shaded microhabitats, where light acts as
an environmental filter and plant abundance is
modulated by seed dispersal and seed predation.
In well-lit environments, the plant would incur
higher maintenance costs and face competition
from faster-growing species. Consequently, B.
nervosa thrives as a deciduous understory tree
under a closed canopy during the rainy season,
developing a full crown of leaves in the dry sea-
son when the canopy opens (Chaves & Avalos,
2008). Consequently, it is less common in
habitats with high light exposure—such as open
savannas, pastures, forest edges, or very young
secondary forests—or in areas with persistent,
dense shade throughout the rainy season, espe-
cially in forests dominated by evergreen species
with year-round canopies, such as old-growth,
mature dry forests. This pattern suggests that B.
nervosa performs best in intermediate shade or
moderately shaded environments, such as old
secondary forests (80-100 years), and is less fre-
quent in habitats with intense sunlight (Janzen
& Wilson, 1974) or dense shade, like riparian
or mature, late-successional forests. These latter
habitats have become rare in the tropical dry
forest ecosystem due to widespread deforesta-
tion and cattle ranching (Stan et al., 2024).
The pattern of habitat selection of B. ner-
vosa is congruent with our field observations
and what is reported in the literature (i.e.,
Enquist & Sullivan, 2001; Janzen, 1970; Janzen
& Wilson, 1974). Establishing under inter-
mediate shade has important implications for
its life history strategy and could influence its
population structure and reproductive strate-
gies (Avalos, 2019). Bonellia nervosa is found
in secondary forests and dry areas on hilltops
or cliffs providing competitive advantages at
the soil level (Enquist & Sullivan, 2001). At
Palo Verde National Park, we have observed it
along the Guayacán trail, which is dominated
by limestone outcrops. Under these conditions,
B. nervosa does not establish itself in purely
rocky areas but prefers flatter or slightly sloped
terrain that can accumulate enough soil for the
plants roots to reach the water table. The phe-
nological pattern of B. nervosa is unique, as no
other species in Costa Ricas dry forests exhibits
reverse phenology. This strategy comes with
significant trade-offs, as B. nervosa is typically
scarce and confined to habitats with intermedi-
ate shade such as old secondary forests. Reverse
phenology likely puts this species at risk under
climate change scenarios, where increased cli-
matic variability could threaten the survival of
early life stages during heat waves or fluctuating
conditions of radiation and water availability.
The main objective of this study was to
examine the population structure of B. nervosa
in Santa Rosa National Park (SRNP). Specifi-
cally, we aimed to: (i) assess the abundance of
adults, juveniles, and seedlings in an old sec-
ondary forest, (ii) evaluate the influence of
canopy structure and light conditions on the
occurrence of B. nervosa during the peak of the
wet season when canopy cover is highest, and
4Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e2025456, enero-diciembre 2025 (Publicado Set. 17, 2025)
(iii) analyze fruit maturity and the intensity of
pre-dispersal fruit predation five months into
the wet season. Given the slow and meta-
bolically demanding process of accumulating
root biomass and food reserves during early
life stages, we expected the population to be
dominated by adults, with relatively few seed-
lings. We hypothesized that population struc-
ture would be influenced by light availability,
as well as the activities of seed dispersers and
seed and seedling predators. Furthermore, we
anticipated that B. nervosa would establish most
successfully in moderately shaded environ-
ments, avoiding areas with either low canopy
cover (high light) or dense shade.
Analyzing the population structure, habi-
tat selection and predispersal fruit predation
of this species is crucial to understanding the
adaptive consequences of reverse phenology
(Stan & Sanchez-Azofeifa, 2019). The rarity
of the reverse leaf strategy may explain why it
has been largely excluded from phenological
analyses (Giraldo & Holbrook, 2011; Schwin-
ning & Kelly, 2013). This stresses the need to
develop effective conservation protocols that
account for the phenological diversity of tropi-
cal dry forests to improve our understanding of
their resilience in the face of climate change and
habitat degradation (Miles et al., 2006; Siyum,
2020; Stan & Sanchez-Azofeifa, 2019).
MATERIALS AND METHODS
Site description: This study was conduct-
ed in SRNP, Guanacaste, Costa Rica (10°50’04”
N & 85°36’45” W, 295 m.a.s.l) in September
2024, along the entire length of the Indio Des-
nudo trail. The forest in this area is classified
as a tropical premontane forest (Holdridge &
Grenke, 1971), with a canopy height of 25 m.
It is dominated by representative dry tree forest
species, including Bursera simaruba, Enterolo-
bium cyclocarpum, Manilkara chicle, and Caly-
cophyllum candidissimum. The average annual
rainfall is 1 423 mm, with September and Octo-
ber being the wettest months. The mean annual
temperature is 25.7 °C, and the relative humid-
ity averages 81 % (SRNP Climatic Records).
Established in 1974 to protect significant his-
torical sites, SRNP also initiated an ongoing
ecological restoration process (Griscom & Ash-
ton, 2011). SRNP maintains transitional areas
between tropical moist and tropical dry forests
(Kalacska et al., 2004). It is estimated that the
Indio Desnudo trail has undergone approxi-
mately 80 years of regeneration and is classified
as a late secondary forest, since it contains three
layers of vegetation with 50-90 % of the canopy
being occupied by evergreen species. This fol-
lows the terminology of Cao et al. (2015),
Castillo et al. (2011) and Kalacska et al. (2004).
Study species: Bonellia nervosa (C. Presl)
B. Ståhl & Källersjö (Primulaceae, formerly
classified as Jacquinia pungens, and then J. ner-
vosa in the Theophrastaceae, Morales, 2003)
has been described as an understory shrub
abundant in deciduous and semi-deciduous
forests throughout the Pacific coast of Meso-
america, from Southern Jalisco, Mexico, to
Northwestern Costa Rica (Ståhl, 1989; Ståhl &
Källersjö, 2004). However, we have observed
individuals reaching 4.86 m in height (this
study) and up to 7 m (pers. obs.), indicating
that B. nervosa should be considered a small
understory tree. Mature individuals can attain
not only these heights but also substantial stem
diameters (20-30 cm). This species is associ-
ated with tropical dry forests, although Morales
(2003) indicates it could reach moist forests.
The overall structure of B. nervosa is xerophytic
(Janzen, 1983) and drought-tolerant (Romero et
al., 2023). Leaves are coriaceous, with the apex
modified as a spine, and once with a complete
crown, the plant seems like a cactus with very
sharp spines pointing out (Janzen, 1970). The
leaves are produced synchronously at the start
of the dry season (Chaves & Avalos, 2008) but
begin to senesce and drop two weeks after the
beginning of the rainy season. Senescing leaves
often can remain in the plant for more than five
months into the rainy season (while finishing
reallocation of resources). The species remains
leafless–or if leaves remain, they are not func-
tional–throughout the rainy season. The spe-
cies is phreatophytic with a deep root system
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(2 m tall individuals have roots reaching 3 m in
depth; Janzen, 1970; Janzen, 1983), which taps
the subsoil water allowing it to produce leaves
during the dry season while most of the plant
community is deciduous. Seventy-eight percent
of the biomass of very young seedlings (8.5 cm
tall, n = 15) goes into roots (Chaves, 2002).
There is limited data on water relations. For
instance, the range in predawn water potential
spanned -2.62 MPa during mid-March, one
of the widest ranges compared to the species
examined by Oberbauer (1985) in Palo Verde.
This indicates water stress during the peak of
the dry season. The fruits are round berries
(mean width = 2.6 ± 0.3 cm, mean length = 2.7
± 0.2 cm, mean weight = 8.48 ± 2.76 g, n = 39),
indehiscent and coriaceous, with the number
of seeds proportional to fruit size, ranging from
four to 24 (average 13 (5), n = 39).
Determination of population structure:
We conducted thorough visual surveys for
seedlings, juveniles, and adults of B. nervosa
along the road from the Park Administration to
the entrance of the Indio Desnudo trail near the
Santa Rosa historical site, extending 30 m into
the forest on both sides throughout the entire
trail (our sample area was approximately 6.16
ha). We meticulously searched for seedlings
(height < 0.6 m), juveniles (height > 0.6 and <
1.5 m), and adults (height > 1.5 m). For each
plant, we measured height and stem diam-
eter 10 cm above the ground and analyzed the
allometry of the height and stem diameter rela-
tionship using the Chapman-Richards model
(Domínguez-Calleros et al., 2017).
Relationship between canopy structure
and the presence of B. nervosa: We took hemi-
spherical photographs 1.5 m above the ground,
directly above or next to individual plants, and
at 10 random points along the Indio Desnudo
trail where B. nervosa was absent. We used a
Nikon Coolpix 5 000 camera with a fisheye
lens, mounted on a tripod with the lens ori-
ented vertically toward the canopy. The top of
the image was aligned with the magnetic North
as determined using a compass. Photographs
were taken under overcast skies, near dusk,
or after dawn, to minimize glare and prevent
direct sunlight from obscuring parts of the
image. We analyzed the photographs using Gap
Light Analyzer (GLA, version 2.0; Frazer et al.,
1999) and measured the percentage of visible
sky (% sky area), canopy openness (% canopy
openness), leaf area index (LAI, measured at
zenith angles of 0°-LAI 4- to 60° and 0° to 75°
-LAI 5-), and the percentage of direct, diffuse,
and total light transmitted through the canopy.
Intensity of predispersal fruit predation:
We inspected all B. nervosa plants for the pres-
ence of fruits and randomly selected 39 fruits.
Using Scout Pro Ohaus Portable Electronic Bal-
ance, we weighed the fresh fruits and seeds and
calculated the percentage of seed weight relative
to the total fruit weight. We also recorded the
number of fruits eaten by Tortricidae larvae
and calculated the percentage of fruit damage.
Additionally, we observed varying degrees of
seed maturation; some fruits contained visibly
unripe beige seeds, while others housed mature
brown seeds.
Statistical analyses: We applied the
Chapman-Richards nonlinear growth function
(Domínguez-Calleros et al., 2017; Zhao-Gang
& Feng-Ri, 2003) to model the relationship
between height and diameter. This flexible sig-
moidal model captures the trajectory of plant
growth, characterized by an initial phase of
rapid height increase followed by a gradual
deceleration as the plant approaches its maxi-
mum size. The Chapman-Richards model is
expressed as H = a (1-b × exp (-k × D))
m, where H is height, D is diameter, and a,
b, k, and m are parameters controlling the
asymptote, growth rate, and curve shape. This
approach allows for accurate estimation of
inflection points, reflecting critical shifts in
growth dynamics throughout plant´s ontogeny.
The height-diameter allometric relationships
provide insights into resource allocation strate-
gies, responses to environmental changes, and
transitions between life stages (i.e., inflection
6Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e2025456, enero-diciembre 2025 (Publicado Set. 17, 2025)
points), which often indicate shifts from vegeta-
tive to reproductive growth.
In addition, to explore the relationships
among the seven light and canopy structure
variables mentioned earlier, we conducted a
principal component analysis (PCA). We select-
ed the first two components, which accounted
for 82.27 % of the variation, as response vari-
ables summarizing canopy structure. Subse-
quently, we performed a one-way ANOVA to
compare these components between locations
where B. nervosa was present and randomly
selected points where it was absent. Addition-
ally, we assessed the relationship between fruit
weight and seed count using an ordinary least
squares regression. We checked the adjustment
to the assumptions of normality and equality of
variances of parametric analyses. All statistical
analyses were conducted using R software (R
Core Team, 2024).
RESULTS
Population structure: We found 33 indi-
viduals ranging in height from 15 to 486 cm.
Three individuals were under 50 cm, main-
tained functional leaves, and were classified as
seedlings. The rest were classified as reproduc-
tive individuals since we found mature or rotten
fruits still attached to the plant. These results
support our expectation that seedlings will be
rare, and that the population will be dominated
by reproductive individuals (Fig. 1A). Stem
diameter and height were significantly related
(Fig. 1B). The inflection point was located at
1.1 cm in diameter and 70 cm in height (at this
size, the model estimates the switch from fast
to slower growth). The asymptotic maximum
value of height was 437.74 cm.
Canopy structure: Sites with B. ner-
vosa had significantly higher canopy open-
ness (14.68 %) than random sites (12.42 %;
F₁,₄₁ = 7.49, p = 0.009; Table 1, Fig. 2A),
as well as greater transmitted diffuse light
(21.05 vs. 18.22; F₁,₄₁ = 9.11, p = 0.004; Fig.
2B). However, these differences were mod-
est in magnitude. Leaf Area Index (LAI4 and
LAI5) was similar between groups, showing
no significant differences.
The percentage of transmitted direct light
and total transmitted light showed the strongest
correlation (0.96), followed by transmitted dif-
fuse light, canopy openness, and leaf area index
(LAI) at zenith angles of 0°-60° (0.89, LAI 4,
Table 2). Two principal components explained
82.27 % of the variation in canopy structure
(Table 3). The first component (PC1, 50.61 % of
the variation) was dominated by canopy open-
ness and transmitted diffuse light. The second
component (PC2, 31.66 %) was dominated by
transmitted direct light.
Fig. 1. A. Height distribution in the population of Bonellia nervosa. B. Chapman-Richards nonlinear growth model applied
to the relationship between height and diameter (R2 = 0.78, F3,29 = 34.62, p < 0.001) in 33 individuals of B. nervosa, SRNP,
Costa Rica.
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One-way ANOVA was used to test the
hypothesis that B. nervosa prefers intermediate
shade conditions and compared the sites where
it was present relative to random sites where
it was absent using these two components
as response variables. PC1 scores (percentage
canopy openness and percentage trans diffuse)
were higher at B. nervosa sites (average = 0.42
± 1.81) compared to random sites (average =
-1.41 ± 1.38; F₁,₄₁ = 8.68, p = 0.005). There were
no significant differences in PC2 scores (per-
centage of trans direct) between B. nervosa sites
(average = 0.04 ± 1.61) and random sites (aver-
age = -0.12 ± 1.04; F₁,₄₁ = 0.09, p = 0.76; Fig. 2).
Fig. 2. Differences in light conditions between sites occupied by Bonellia nervosa and random sites in SRNP, Costa Rica. A.
Percentage of canopy openness. B. Percentage of transmitted diffuse light.
Table 1
Summary of canopy structure variables at the Indio Desnudo trail, SRNP, during the late wet season of 2024.
Site NPercentage
sky area
Percentage canopy
openness LAI 4 LAI 5 Percentage t
rans direct
Percentage
trans diffuse
B. nervosa 33 99.88 (0.01) 14.68 (2.42) 2.11 (0.36) 2.10 (0.33) 25.84 (6.19) 21.05 (2.76)
Random 10 99.88 (0.01) 12.42 (1.82) 2.36 (0.42) 2.30 (0.36) 22.76 (2.88) 18.22 (1.92)
Values are means (± 1 SD) of 43 hemispherical photos taken at random sites and at sites occupied by B. nervosa.
Table 2
Correlation matrix of 7 canopy structure variables in the SRNP Forest in 2024 (n = 43 hemispherical photos).
Percentage
sky area
Percentage
canopy openness LAI 4 LAI 5 Percentage
trans direct
Percentage
trans diffuse
Percentage sky area 1
Percentage canopy openness 0.17 1
LAI 4 -0.15 -0.76 1
LAI 5 -0.34 -0.71 0.89 1
Percentage trans direct -0.14 0.30 0.12 0.18 1
Percentage trans diffuse 0.10 0.89 -0.50 -0.40 0.59 1
Percentage trans total -0.06 0.54 -0.1 -0.009 0.96 0.80
Values represent Pearson correlation coefficients. Boldfaced values show significant correlations at p < 0.001. LAI = leaf
area index at a zenith angle of 0°-60° -LAI 4-, and at 0°-75° -LAI 5-, Trans direct = transmitted direct light, Trans diffuse =
transmitted diffuse light, Trans total = transmitted total light.
8Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e2025456, enero-diciembre 2025 (Publicado Set. 17, 2025)
Predispersal fruit predation: There was a
positive relationship between fruit weight, seed
weight, and seed number (Fig. 3), indicating that
larger fruits contain more and heavier seeds. Of
the 39 fruits examined, six were infested by
moth larvae from the Family Tortricidae (the
only seed predator found), with one fruit hav-
ing all its seeds consumed. The percentage of
fruit predation was 15.38 %, although this likely
fluctuated throughout fruit development since
the last crop. Our observations were limited to
fruits that remained until September, but many
more were likely damaged earlier in the season.
DISCUSSION
The population structure, dominated by
adults, suggests that seedlings are rare, likely
due to multiple stressors. For instance, the high
energy demand required to store reserves for
surviving in the shade during the rainy season
may increase seedling mortality. Additionally,
seedlings are more susceptible to drought-
induced mortality, including cavitation and
hydraulic failure (Werden et al., 2023). Their
small size further increases vulnerability to
herbivory and pathogen damage, as they may
be unable to regenerate tissue or compen-
sate for losses effectively. In addition, seed-
lings are especially vulnerable to mechanical
damage from falling branches. Competition
with vines and other understory vegetation
may further limit their survival. Our previous
observations indicate that seedlings tend to
aggregate around adult plants, consistent with
the dispersion pattern typical of many tropi-
cal dry forest species (Hubbell, 1979), which
may increase their exposure to herbivores and
pathogens (Bhadouria et al., 2016). These com-
bined pressures suggest that the seedling stage
acts as a critical ecological filter influencing the
habitat preferences of B. nervosa. Long-term,
Fig. 3. A. Relationship between fruit weight and seed weight. B. Relationship between fruit weight and number of seeds in
B. nervosa, SRNP, Costa Rica.
Table 3
Coefficients of the eigenvalues and eigenvectors of the
PCA from seven variables obtained from the hemispherical
photograph analysis in the Indio Desnudo trail, SRNP.
Eigenvalue Variation
explained (%)
PC1 3.54 50.61
PC2 2.21 31.66
Cumulative variation 82.27
PC1 PC2
Percentage sky area 0.109 -0.27
Percentage canopy openness 0.50 -0.11
LAI 4 -0.38 0.40
LAI 5 -0.35 0.46
Percentage trans direct 0.27 0.54
Percentage trans diffuse 0.50 0.14
Percentage trans total 0.38 0.46
Boldfaced values represent dominant loadings of the
eigenvectors on each PC.
9
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multi-season monitoring studies are necessary
to accurately estimate seedling abundance and
recruitment dynamics. A long-term popula-
tion growth study, projected over several years,
may be ambitious considering that B. nervosa
appears to grow slowly. The Chapman-Rich-
ards model indicates an inflection point at
approximately 70.6 cm in height, suggesting a
transition from slow to even slower growth. We
observed reproductive structures in an indi-
vidual of 1.5 m in height, indicating that B. ner-
vosa may begin reproducing at relatively small
sizes and possibly early in its life cycle, which
could shift resource allocation toward repro-
duction rather than growth and maintenance.
Since leaves are produced only during the dry
season, there may be minimal differences in
leaf quality and function between seedlings
and adults, although this hypothesis requires
further investigation.
Bonellia nervosa is not an abundant species
in the dry forests of SRNP. While it is capable of
colonizing open areas such as forest edges (Jan-
zen, 1970) and has occasionally been observed
in pastures, it is more frequently found in old
secondary forests within SRNP. Notably, it is
absent from the parks only patch of primary
forest, which remains evergreen during the dry
season. This distribution suggests that B. ner-
vosa prefers intermediate light conditions and
avoids both the most open and the most shaded
environments. This pattern was also supported
by observations from A. Sánchez-Azofeifa, who
did not find B. nervosa in forests younger than
50 years and found only three individuals in an
80-year-old plot, further indicating its affin-
ity for late-successional stages (A. Sánchez-
Azofeifa, personal communication, 2024). Our
findings (five individuals/ha) are consistent
with those of Glander and Nisbett (1996), who
reported a very low density in Cañas, Costa
Rica (0.06 individuals/ha). These observations
suggest that B. nervosa may function as a late-
successional species and a potential indicator of
forest regeneration, especially in dry forest eco-
systems where successional dynamics are slow
and strongly shaped by water availability and
disturbance regimes (Griscom & Ashton, 2011;
Quesada et al., 2014). Its presence could there-
fore reflect structural and microclimatic condi-
tions associated with more advanced stages of
secondary succession.
A related species, B. macrocarpa, in Oaxa-
ca, Mexico, was classified as a late-successional
species by Romero et al. (2023). It typically
occurs in tropical dry forests aged 50 to 70 years
but has also been observed in early succes-
sional forests as young as two years old, but
in low numbers. Bonellia nervosa employs a
“long-lived pioneer” regeneration strategy,
enabling it to associate with old secondary for-
ests but limiting its abundance in early succes-
sional stages and primary tropical dry forests
(Rüger et al., 2023).
Hemispherical photographs show that B.
nervosa tends to occupy microsites with mod-
erate canopy cover, suggesting a preference for
intermediate light environments. The average
canopy openness at sites where B. nervosa
occurs was 14.16 %, with a LAI of 2.17. These
values fall between those of cloud forests (Syl-
vester & Avalos, 2013) and mature lowland
tropical rainforests, the latter typically exhibit-
ing canopy openness below 10 % and LAI val-
ues approaching six (Bakar et al., 2023; Clark et
al., 2008; Clark et al., 2021; Pfeifer et al., 2018).
During the dry season, the mature forest patch
at SRNP showed a canopy openness of 10.31 %
and an LAI of 2.78 (pers. obs.). These values
show that B. nervosa avoids dense shade and
full exposure and is instead associated with
intermediate light levels.
We consider our findings to be preliminary,
highlighting the need for further research dur-
ing the dry season, including a more through
seedling census and a detailed comparison
of leaf structure and function between seed-
lings and adults. The apparent restriction of
B. nervosa to older secondary forests, and its
absence from a broader range of habitats, sug-
gests limited phenotypic plasticity in coping
with environmental variation. This constraint
may significantly affect the species’ capacity to
adapt to climate change. For instance, Sánchez
et al. (2020) attempted to alter the species’ leaf
phenology through dry-season irrigation, but
10 Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e2025456, enero-diciembre 2025 (Publicado Set. 17, 2025)
observed no significant changes, pointing to
a potentially low level of genetic variation in
response to water availability, although their
results were inconclusive. The unique inverted
phenology of B. nervosa underscores the need
for further investigation into the physiological
mechanisms determining its ecological strate-
gy, particularly in the face of increasing climate
variability (Schwinning & Kelly, 2013).
Bonellia nervosa shows a pulse in vegetative
and reproductive growth during the dry season.
The plants energy reserves must support the
production of a new canopy and the develop-
ment of flowers and fruits. The fruits continue
to expand and mature for at least five additional
months during the rainy season, further deplet-
ing the plants reserves. Additionally, the young
leaves of B. nervosa are exposed to a relatively
diverse array of herbivores during the dry sea-
son, which consume an average of 36.77 % of
their area (Chaves & Avalos, 2007). While the
fruit damage percentage observed in our study
may seem low, the level of infestation by Tor-
tricidae larvae should be monitored throughout
the fruit’s development. Adult moths likely lay
their eggs in the immature ovaries, with the
larvae developing as the fruit expands.
Chaves and Avalos (2008) reported that
only 3 % of the flowers became fruits. This low
reproductive success was associated with low
levels of flower synchrony. B. nervosa is thought
to be dispersed by rodents (Sumichrasts vesper
rat, Nyctomys sumichrasti, Ceballos, 1990), as
well as by the White-tailed deer, Odocoileus vir-
ginianus, Jara-Guerrero et al., 2018). During the
2024 dry season, white-faced monkeys (Cebus
imitator) were also observed eating their ripe
fruits in SRNP and in Taboga Forest Reserve,
Guanacaste. Horses also have been seen eating
B. nervosa fruits in SRNP (O. Chaves, personal
communication, 2024). Possibly, there is no
shortage of seed dispersers, but the species still
shows low abundance.
Our study shows that B. nervosa has a popu-
lation structure dominated by adults. Seedlings
are scarce, likely because of the high energy
demands for reserve accumulation, vulnerabil-
ity to drought, and herbivory and mechanical
damages. The species occurs in microsites with
moderate canopy openness (~14 %), indicating
a preference for intermediate light conditions
and suggesting it functions as an indicator
of late-successional forest stages. Its absence
from very young and mature forests supports
this interpretation. Although predispersal fruit
predation was relatively low (~16 %), further
monitoring is needed to assess fruit losses over
the entire reproductive period. The species
slow growth, narrow habitat preferences, and
distinctive reverse phenology point to lim-
ited phenotypic plasticity, justifying the need
for long-term, multi-seasonal studies to better
understand the recruitment dynamics and the
resilience of this species to climate change.
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.
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