co-evolution of offspring antipredator competence and parental
TRANSCRIPT
ADVANCES IN CICHLID RESEARCH
Co-evolution of offspring antipredator competenceand parental brood defense in convict cichlids
Brian D. Wisenden • Anthony D. Stumbo • Patrick A. Self •
Jennifer L. Snekser • Daniel C. McEwen • Patricia A. Wisenden •
Miles H. A. Keenleyside • Murray Itzkowitz • Ellen Brisch
Received: 23 December 2013 / Accepted: 19 May 2014 / Published online: 14 July 2014
� Springer International Publishing Switzerland 2014
Abstract Convict cichlids are Neotropical freshwa-
ter fish with biparental brood defense of their free-
swimming young. In this study, we correlate ontoge-
netic changes in swimming performance measured by
maximum velocity and burst speeds with skeletal
ossification of larvae and consider how these data
provide insights into the proximate mechanisms for
the evolution of parental care. In lab tests, swimming
velocity and acceleration of the young increased
nonlinearly with body length with a rapid improve-
ment at 7 mm in standard length (SL). The timing of
abrupt improvement in swimming velocity and accel-
eration coincided with the timing of skeletal ossifica-
tion from cartilage to bone. Radii of defended broods
in the field reflected the interaction of parental defense
competence and offspring antipredator competence. In
the Rıo Cabuyo, Costa Rica, brood radii increased
steadily until the young were 6.45 mm SL, and then
plateaued. Taken together, these data indicate inter-
dependent and co-evolved traits that encompass larval
ontogenetic development, antipredator performance,
habitat-specific predation regime, and parental care.
Keywords Skeletal ossification � Swimming speed �Antipredator behavior � Parental care
Introduction
The link between morphology and performance has
long been of interest to evolutionary ecologists
because natural selection acts on variation in perfor-
mance (Arnold, 1983; Kingsolver & Huey, 2003). For
example, sprint speed of hatchling and juvenile
Urosaurus ornatus lizards is correlated to stride length
(not body size per se) and also to survival (Miles,
2004). Similarly, burst speed increases with snout-
vent length in neonate garter snakes, (Thamnophis
sirtalis fitchii), and both absolute burst speed and burst
speed corrected for length (residuals of burst speed on
snout-vent length) are correlated with survival (Jayne
& Bennett, 1990). Garter snake consumption rate of
size-matched tadpoles of Pacific tree frogs, Pseudacris
regilla, is inversely correlated with burst swimming
speed of the tadpoles (Watkins, 1996).
Guest editors: S. Koblmuller, R. C. Albertson, M. J. Genner, K.
M. Sefc & T. Takahashi / Advances in Cichlid Research:
Behavior, Ecology and Evolutionary Biology
B. D. Wisenden (&) � A. D. Stumbo � P. A. Self �D. C. McEwen � P. A. Wisenden � E. Brisch
Biosciences Department, Minnesota State University
Moorhead, 1104 7th Avenue South, Moorhead,
MN 56563, USA
e-mail: [email protected]
J. L. Snekser � M. H. A. Keenleyside
Zoology Department, University of Western Ontario,
London, ON, Canada
M. Itzkowitz
Biological Sciences Department, Lehigh University,
Bethlehem, PA, USA
123
Hydrobiologia (2015) 748:259–272
DOI 10.1007/s10750-014-1917-2
In this paper, we consider the links between
morphology and antipredator performance in larval
convict cichlids, a cichlid fish with biparental care of
its young. The convict cichlid (Amatitlania siquia
Schmitter-Soto, 2007) is a small fish endemic to
Central America (Bussing, 2002). They are substrate
spawners that deposit their eggs on the roof of a cavity
formed under a solid object on the substratum. They
have biparental care of their eggs and free-swimming
young over a period of four to six weeks (Wisenden,
1995). During this time, parents defend their young
against a range of brood predators (Wisenden, 1994a).
Young convict cichlids are about 4.5 mm in standard
length (SL) when they first emerge from their lair.
Both parents contribute to brood defense, although
there is some division of labor between the sexes in the
pre-hatch period, where males patrol the territory
perimeter repelling intruders while females do most of
the egg-directed care such as fanning and cleaning
(Itzkowitz et al., 2001). Once the young are free-
swimming, both parents guard a mobile territory
around the young as the family roams about during the
day. This allows the young to forage on a large area of
the substrate. In the field, convict cichlid broods form a
cohesive two-dimensional disk hovering above the
substrate. Thus, brood radius is an important variable
of both parental defense and predation risk to the
young. Families return to their lair each night for
refuge from nocturnal predators. Parental protection of
the young at study sites in Costa Rican streams
continues until the young reach a SL of 10–12 mm
(4–6 weeks post-hatch) (Wisenden, 1995).
Reproductive success in convict cichlids is deter-
mined by success against brood predators (Wisenden
1994a, 1995). Evolution of parental brood defense by
convict cichlids is therefore a problem of antipredator
behavior that is shared by the adults repelling brood
intruders, and the larvae that must evade direct attacks
when brood predators inevitably penetrate parental
defenses. Thus, offspring survival exerts selection both
on parental defense behavior and morphological
development that contributes to swimming perfor-
mance of the young. Supporting evidence comes from
three lines of data. First, large parents are more
successful than small ones at preventing fry mortality
(Wisenden, 1994a; Gagliardi-Seeley & Itzkowitz,
2006). Second, despite widely varying starting num-
bers, the number of young in guarded broods at four
different field sites in Costa Rican streams all
converged on a mean number of 27 young at indepen-
dence (Wisenden, 1994a). This suggests that there is a
limit to the radius that parents can effectively defend
and that 27 large, fully-developed young is the number
of young that fully occupy that area. Moreover,
experimentally augmented broods sustain compensa-
tory predation mortality (Wisenden & Keenleyside,
1995). The third piece of evidence is that the growth
rate of fry is inversely proportional to the number of
young in a brood (Wisenden, 1994a, 2001). The likely
mechanism for inhibited growth rates in large broods is
crowding when large numbers of young are forced to
remain within the small area that parents can effec-
tively defend. Taken together, these data suggest that
efficiency of brood defense declines rapidly with brood
radius. We predict that brood radius should reflect the
equilibrium between predator density and the ability of
parents to defend an area and the ability of the young to
evade an attack. In this study, we quantify this dynamic
process for natural populations in Costa Rican streams.
Interacting with effectiveness of parental defense is
the ability of the young to escape a direct attack. Larval
convict cichlids are poorly developed and swim weakly
at the time of emergence from the lair but become better
at evading attack as they grow and develop (Wisenden
& Keenleyside, 1992, 1994). So pronounced is this rate
of change in antipredator competence that it is exploited
by parents engaging in alloparental care. Convict
cichlids preferentially adopt young from other broods
that are similar in size or smaller than their own broods
(Wisenden & Keenleyside, 1992). When predators
attack, the relatively weak-swimming adopted fry are
the preferred targets of brood predators, thereby
deflecting predation pressure away from the young
genetically related to the adults providing the care
(Wisenden & Keenleyside, 1994).
In the current study, we build on these earlier data to
examine the relationship among parental defense behav-
ior and ontogeny of antipredator competence of larvae
through a series of field and laboratory experiments.
Morphology and the ontogeny of swimming
performance of larval convict cichlids
In Costa Rican streams, the rate of brood reduction due
to predation is much greater during early development
(5–7 mm SL) than in later development (8–10 mm SL)
(Wisenden, 1994a). Experimentally contrived groups
260 Hydrobiologia (2015) 748:259–272
123
of young of mixed sizes comprising young of 5, 6, 7,
and 8 mm SL showed that 5 and 6 mm young were
eaten significantly more often than 7 and 8 mm young
when exposed in lab aquaria to juvenile convict
cichlids or juveniles of the sympatric piscivore
Parachromis dovii (Wisenden & Keenleyside, 1992).
Differential predation on small versus large sizes of
young was demonstrated again in a field manipulation
experiment (Wisenden & Keenleyside, 1994). That
study demonstrated fitness benefits of adopting unre-
lated young that are smaller than the genetically related
young, and that this difference seems to be maximal
between young that are smaller and larger than 7.5 mm
SL. Swimming performance of larval convict cichlids
as a function of length has not been quantified and was
the first goal of this study. We quantified swimming
performance in terms of maximum velocity and
maximum acceleration of rapid starts. Previously
published empirical data from the lab and field led us
to anticipate a rapid improvement in antipredator
escape performance starting at about 7 mm SL (Wi-
senden & Keenleyside, 1992, 1994, 1995).
Proximate anatomic structures that contribute to
rapid starts in larval fish include neurologic, muscular,
and skeletal changes (Fuiman & Magurran, 1994). We
quantified the timing of skeletal ossification because
the techniques for doing so are well established (Song
& Parenti, 1995), and because ossification of the axial
and appendicular skeleton is necessary to translate the
forces of muscular contraction into propulsive forces
generated by fins (Hale, 1999). By scoring the timing
of cartilage-bone transition of individual skeletal
elements, we could then test for a correlation between
skeletal ontogeny and changes in swimming perfor-
mance. Because swimming performance was pre-
dicted to improve non-monotonically, we predicted
that if skeletal ossification is indeed a major contrib-
utor to swimming performance then ossification
should also proceed nonlinearly and coincide with
marked improvement in swimming ability.
Parental brood defense in response to the ontogeny
of larval antipredator competence
Swimming performance of larvae has a direct effect on
the parental brood defense required for their protec-
tion. Shoals of convict cichlids take the shape of a
shallow disk hovering above the substratum. Larvae
with very poor swimming ability (i.e., limited skeletal
ossification) must remain in a small shoal directly
below the parents, where parents are most effective at
repelling intruders. When attacked, the young dart
toward the brood center and downward into the
substratum. As larval swimming performance
improves, or in habitats where density of brood
predators is low, the young can afford to stray from
the brood center where foraging opportunities are
better (i.e., increase brood radius). To develop a model
of brood defense, we looked to previously unpublished
parental defense data from field sites in Costa Rica to
define the problem of defending a brood as a series of
concentric zones of increasing risk of predation
around centrally located parents. We then used field
data from the Rıo Cabuyo to test predictions about the
rate of expansion of brood radius with respect to the
timing of skeletal ossification. We predicted that brood
radii in Rıo Cabuyo would correlate with skeletal
ossification and swimming performance of larvae.
Methods
Antipredator competence
A breeding colony of convict cichlids at the aquatic
research facility at Minnesota State University Moor-
head (MSUM) was established with wild-caught fish
from Quebrada Amores, which is a tributary of the Rıo
Cabuyo, and from the Rıo Potrero, which is the
adjacent river to the Rıo Cabuyo in the same
watershed. The Rıo Potrero and Rıo Cabuyo both
flow into the Rıo Tempisque, Guanacaste, Costa Rica.
Fish used in the first part of this experiment were F3
offspring from a random mixture of these fish.
Individual young convict cichlids were placed in a
circular plastic arena (diam = 25.5 cm) containing
dechlorinated tap water to a depth of about 2 cm. We
tested young at 1-mm intervals of SL. Sample sizes
were: 5 mm (n = 23), 6 mm (n = 17), 7 mm
(n = 28), 8 mm (n = 13), and 9 mm (n = 12). Startle
responses were induced using a standardized mechan-
ical stimulus created by dropping a weight on the
bench surface outside but adjacent to the arena and
recorded by an overhead digital camcorder at 30
frames per second. Frame-by-frame video play-back
of swimming behavior was analyzed for maximum
velocity (m/s) and acceleration (m/s/s) of the startle
Hydrobiologia (2015) 748:259–272 261
123
response using LoggerPro� software. Arena diameter
was used as the size reference to calibrate mm/pixel
ratios for calculating velocity and acceleration.
Skeletal ossification
Fish from MSUM Costa Rican lab stock were bred in
five separate breeder tanks. Five offspring from each
brood were euthanized and preserved in formalin at
1-mm size intervals from 5-9 mm SL. Offspring were
cleared and stained with Alcian Blue to reveal
cartilaginous tissues and Alizarin Red to reveal
ossified skeletal structures (Song & Parenti, 1995).
Cleared and stained offspring were stored in glycerol
with phenol crystals as a preservative. High-resolution
images of stained offspring were taken with a digital
camera (Olympus Q-color3) mounted on a compound
microscope (Olympus CX31). We assessed calcifica-
tion of the following skeletal structures: caudal fin,
hypourals (bones that connect the caudal fin to the
posterior tip of the vertebral column), dorsal fin rays
and their pterygiophores (small bones at base of fin
that support and anchor fin), and the anal fin rays and
their pterygiophores. We focused on these structures
because we hypothesized that calcification of fin
support would confer greater swimming force. A scale
of 0–4 was used to assess the level of ossification for
each skeletal element: 0 = all blue, i.e., completely
cartilage; 1 = mostly blue; 2 = approximately equal
amounts of blue and red; 3 = mostly red; 4 = all red,
i.e., completely bone. A total of 111 different skeletal
elements and an additional 17 fin groupings (=128
skeletal data) were scored for each of 115 fish. Thus,
the resulting data matrix contained 14,720 observa-
tions on skeletal calcification; however, fish that
showed no variance in ossification scores, i.e., fish of
5 mm SL that had not yet begun the ossification
process, were removed from the analysis. This left 92
total fish and (11,776 data) to analyze and to test for
changes in ossification as a function of fish length. We
used two complementary procedures to describe
ossification. First, we calculated the average ossifica-
tion score for each size class and then subtracted the
ossification for the proceeding size class. For example,
we found the average ossification to be 3.95 for the
7 mm fish for the Cbase element and 3.91 for the same
element in the 6 mm fish. The change (D) in ossifi-
cation score then would be 0.04 (i.e., 3.95–3.91) in
transitioning between 6 and 7 mm. Given all 5 mm
fish had no ossification, the change from 5 to 6 mm
reflects the average ossification score in 6 mm fish.
Second, we used nonmetric multidimensional scaling
(NMDS) to reduce the matrix of skeletal elements
(124) by fish (87) to two dimensions. We were
required to further trim our data matrix from 92 to 87
fish because ossification scores were identical for five
separate pairs of fish and NMDS cannot operate on
identical rows in matrices. These redundant records
were collapsed into five single records given fish were
the same size. After reducing the ossification matrix,
we then used an ANOVA to test the two reduced axes
against fish length while controlling for a brood effect.
We utilized a modified Gower’s similarity coefficient
appropriate for ordinal type data to generate our
distance matrix for the NMDS (Podani, 1999). Where
the ANOVA showed fish size to be significant, we
used a Tukey test for post-hoc pair-wise comparisons.
Attack radius by parental fish in Rıo Cabuyo, Costa
Rica
Attack radius is the distance from the brood center
(where parents typically reside) to the position of an
intruder. Because attacks occurred in all 360�, radius is
a useful descriptor of both risk to larvae and parental
defense effort. Parental convict cichlids directed their
attacks mainly against juvenile and adult conspecifics,
the substrate sifter Amphilophus longimanus, and the
piscivorous Parachromis dovii. Incidental attacks also
occurred against the characin Astyanax fasciatus and
the poeciliid Poecilia gillii. Baseline data on attack
frequency and attack radii come from unpublished
data collected from four study sites during the dry
seasons (December to May) of 1989–1990 and
1990–1991. The study sites were located in and near
Lomas Barbudal Biological Reserve, Guanacaste,
Costa Rica (10�30021.5600N, 85�22014.6400W, elev.
43 m), and described by Wisenden & Keenleyside
(1995) and Wisenden (1995). Each study site was a
defined section of stream in the Rıo Cabuyo or its
tributary Quebrada Amores. Within each stream, there
was one site that was a large deep pool (pool habitat)
and another site that was a series of small intercon-
nected shallow pools (stream habitat). Habitat affects
predation pressure (pools [ streams), male mate
desertion (streams [ pools), and overall brood suc-
cess (streams [ pools) (Wisenden, 1994a, b). Streams
were shallow and water transparency was excellent;
262 Hydrobiologia (2015) 748:259–272
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thus, parental defense behaviors were recorded from
above the surface with the aid of polarized sun-
glasses after calibrating distance estimates against a
meter stick. Parental defense behavior was recorded
from a distance of several meters for 10 min for the
one parent, followed immediately by 10 min of
parental behavior of the other parent. We conducted
840 focal follows on 198 different broods, typically
with one parental male and female per brood. Some
brood pairs were observed on more than one occasion.
We further separated our focal follows into two
separate responses: (1) attacks against cichlids and (2)
attacks against non-cichlid fishes. This effectively
doubled our records from 840 to 1,680 entries. Some
of these records were incomplete (e.g., estimates for
parent lengths, brood radii, etc., were not made).
Records without a full complement of data were
eliminated prior to analysis. Lengths and counts of
young were conducted at 5-day intervals for each
brood. Entire broods were encircled with a seine net,
the male was captured with a hand net, all of the
offspring were captured by hand net with the aid of a
scuba mask and the female was then captured by
chasing her into the seine net. On shore, a subsample
of 15 young was measured to the nearest 0.5 mm SL
with a ruler, the remaining young counted, and two
dorsal spines were excised from each parent in a
unique combination such that individuals could be
recognized if they respawned later that season (Wi-
senden 1994a, 1995). We also sketched the markings
of each parent to allow for convenient identification of
the breeding pair on subsequent samplings within the
same brood cycle. The family was carefully released
back into the stream at the site of capture by first
releasing the parents (the usually male fled and hid, but
the female always searched for her young and
defended the area; see Wisenden et al. 2008). The
young were returned via a clear plastic tube fashioned
from two 2-L pop bottles with the tops and bottoms
removed and stacked together. The young settled to
the bottom and made eye contact with the searching
female. When the female approached the tube we
raised the tube upward to allow the family to reunite.
Brood radii in the Rıo Cabuyo 2008
Brood radius is the distance from the brood center to
the outer limit of the area occupied by the brood. These
data were collected from the Rıo Cabuyo in January
2008. We surveyed about 1 km of river starting at the
deep pool below the road crossing (Cabuyo Pool site
used in 1990 and 1991) up to the pool with the
waterfall near the upstream boundary of Lomas
Barbudal Biological Reserve. For each brood, we
measured brood depth and brood diameter to the
nearest cm with a meter stick, SL of a subsample of 10
captured young to the nearest 0.5 mm using a ruler and
counted the total number of young in the brood. To
ensure accurate brood counts, we caught all but
several of the young with hand nets and brought them
on shore to measure and count. The remaining few
young in the water could be counted with certainty
with the aid of a SCUBA mask. Young were returned
to their parents immediately after sampling using the
transparent plastic tube described above.
Results
Antipredator swimming performance
Size of young had a significant effect on maximum
swimming velocity (ANOVA F4,88 = 36.96, P\0.001) and acceleration (ANOVA F4,88 = 48.85,
P\ 0.001) of the startle response (Fig. 1). Post-hoc
pair-wise comparisons (Tukey test) among size groups
showed that 5 mm = 6 mm \7 mm \8 mm =
9 mm for both velocity and acceleration (P\0.05).
Skeletal ossification
The skeleton of larvae ossified from cartilage (blue) to
bone (red) at 1-mm intervals from 5 mm SL to 9 mm
SL (Fig. 2A). Magnified images of cleared and stained
embryos allowed for unambiguous scoring of individ-
ual skeletal elements (Fig. 2B). The ANOVA per-
formed on the scores generated by the NMDS showed
the first axis to have significant groups for both size
(F3.79 = 25.14, P \ 0.001) and brood (F4,79 = 37.77,
P \ 0.001), but that variance partitioned from the
sums of squares indicated that the majority of variance
for the first axis could be attributed to brood source
(49%). Fish size explained 24% with the remaining
variance left unexplained (26%). The second axis also
showed fish size (F3.79 = 199.12, P \ 0.001) and
brood (F3.79 = 15.19, P \ 0.001) were both signifi-
cant, but here the primary factor associated with
structuring variance was fish size (81%). Brood
Hydrobiologia (2015) 748:259–272 263
123
explained only a minor proportion (8%) with 11%
unexplained. The NMDS ordination plot showed good
discrimination of cichlid young of different lengths on
the basis of skeletal ossification data (Fig. 3). Post-hoc
pair-wise comparisons (Tukey test) among size groups
showed that 6 mm \ 7 mm \ 8 mm \ 9 mm for
scores along the second NMDS axis (P \ 0.001),
where the largest change in skeletal ossification
occurred between sizes 6 and 7 mm SL (Fig. 3).
Individual skeletal elements that ossified the most
between 5 and 6 mm SL were the skeleton of the
caudal fin and supporting elements of the hypourals
that anchor the caudal fins to the caudal tip of the
vertebral column (Table 1). Between 6 and 7 mm SL,
where the most pronounced improvements in swim-
ming performance occurred, the medial pterygio-
phores (middle rays that support the fin membrane) of
the dorsal and anal fin showed the greatest change.
Over the interval from 7 to 8 mm SL, skeletal
ossification continued on various elements without
any cluster of bones ossifying as a group. Between 8
and 9 mm SL, the distal pterygiophores that support
the outer edges of the dorsal and anal fins showed the
greatest change, indicating completion of the ossifi-
cation process (Table 1).
Brood defense radii in Costa Rican streams
A total of 840, 10-min recordings were made on 198
different broods, representing a comprehensive sam-
ple of all four sites (two in pool habitat, two in stream
habitat), and all brood ages and sizes (Table 2). Mean
attack radius over two breeding seasons in four sites by
males and females against six types of intruders was
33.56 ± 0.48 cm (Fig. 4). Attacks occurred on aver-
age 6.93 ± 0.24 times per 10-min observation period
(Fig. 4). Attack frequency and distance varied with
0
0.1
0.2
0.3
0.4
0.5
Max
imum
Vel
ocity
(m
/s)
Young SL (mm)
a
0
1
2
3
4
5 6 7 8 9
5 6 7 8 9
Max
imum
Acc
eler
atio
n (m
•s-2
)
Young SL (mm)
a
b
c c
a a
b
c
c
Fig. 1 Maximum velocity (upper panel) and maximum accel-
eration (lower panel) for young Costa Rican fish sized 5, 6, 7, 8
and 9 mm in standard length. Letters above bars indicate the
results of post-hoc pair-wise Bonferroni tests. Shared letters
indicate no significant difference (P [ 0.05)
5 mm 8 mm
6mm 9 mm
7 mm
(B)
Hypourals
Prox Med Dist
Anal pterygiophores
Prox Med Dist
Dorsal pterygiophores
Dorsal fin rays
Anal fin rays
Caudal fin rays
(A)
Fig. 2 Color images of cleared and stained embryos A at 1-mm
intervals of development and B showing individual skeletal
elements composed of cartilage in blue and bone in red
264 Hydrobiologia (2015) 748:259–272
123
species of intruder (Table 3). The characin Astyanax
fasciatus and the poeciliid Poecilia gillii were attacked
only when they intruded directly into the mobile
territory of the brood. Brood radius within 10 cm is
physically occupied by the parents, therefore, mini-
mum parental attack distance was 10 cm. Because
attack frequencies were counts, we used a generalized
linear model to test for environmental effects on the
number of attacks. We had no a priori reason to
suspect overdispersion and used Akaikie Information
Criteria (AIC) model selection to choose the better
fitting of a Poisson model or a negative binomial
model for the case of overdispersion (Burnham &
Anderson, 2002). AIC indicated that the negative
binomial distribution fit much better than did the
Poisson distribution (DAIC = 1,104, w = 0). The
DAIC gives the difference in AIC score for a particular
model relative to the most parsimonious model and
generally a DAIC \ 2 indicates comparable models.
The AIC weight (w) gives the probability that upon
resampling, a particular model would end up being
ranked as the most parsimonious. Our result indicates
it is virtually impossible that the Poisson model would
ever be supported over the negative binomial. Conse-
quently, this indicates that there is overdispersion
associated with the counts. We used a set of predictor
variables that included random effects of year and
brood along with a covariate for time. After
controlling for these variables, our model resulted in
all terms we included were significant except for size
of the young. In order of importance of generating
high frequency of attacks were sex of the parent,
taxonomy of the target fish, brood depth, site, number
of young, and parent size. Males had 2.7 times as many
attacks as females did, and cichlids were attacked 1.8
times more than noncichlids (P \ 0.05). Effects for
the other predictors were significant, but weak with
higher attack frequencies for deeper broods, pool sites
as opposed to stream sites, larger as opposed to smaller
broods, and larger rather than smaller parents. The
coefficient of determination for the global model
estimated on 1,308 complete records using null and
residual deviance indicated our model explained a
significant proportion of variation (v62 = 179, R2 =
0.30, P \ 0.001).
We were able to use the same set of predictors to test
attack radius, but because the response was a continuous
variable, we were able to use a linear modeling
framework. The global model, generated on 943 focal
follows, explained a significant portion of the variance
in measured attack radius (F169,773 = 4.25, R2 = 0.368,
P \ 0.001). After controlling for year, time, and brood,
attack radius responded strongly with taxonomic group
(cichlids = 38.7 ± 0.56 cm; noncichlids = 22.2 ±
0.57 cm), which captured[35% of variability remain-
ing after controlling for covariates. Parent size, young
number, and brood depth also were statistically signif-
icant model terms (P \ 0.05) but accounted for a very
small proportion of the observed variance in attack radii,
explaining 0.1, 1.4, and 0.7% of the variance, respec-
tively, (None of sex, site, or size of the young were
significant (P [ 0.05)).
Taken together, parental attack radius data indicate
a zonal pattern of parental defense (Fig. 4). Very few
attacks occurred in the area immediately below the
parents, with a radius of less than 10 cm, because the
parents physically occupy this whole area. The next
concentric zone, with a radius between 10 and 20 cm,
is of intermediate exposure to brood predators. To
evade predator attack in this zone, young must be able
to dart 10–20 cm to the brood center. Relatively few
attacks occur within 10–20 cm likely because of
parental intimidation. The next zone, with radii
between 20 and 30 cm, is where attack frequency
begins to increase rapidly. To attack a potential brood
predator at this radius parents must momentarily
vacate the brood center leaving the brood vulnerable to
Fig. 3 Plot of NMDS1 versus NMDS 2 reveals major patterns
of variation in skeletal ossification for larval convict cichlids
ranging in size from 6 to 9 mm in SL. Minimum convex
polygons are drawn around points for fish of similar size. The
average score for each size group along NMDS 2 is shown along
with the 95% confidence intervals. Tukey HSD post-hoc test
showed each group to be significantly different (P \ 0.001)
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Table 1 Change in mean calcification score for each 1-mm interval for larval convict cichlids for each of 129 skeletal elements in
larval convict cichlids over 1-mm intervals
5–6 mm SL 6–7 mm SL 7–8 mm SL 8–9 mm SL
Bone D Bone D Bone D Bone D
Cbase 3.91 DMED1 2.28 APROX3 0.91 ADIST10 1.50
Cmed 3.86 DMED4 2.21 H4 dist 0.91 ADIST11 1.31
H2 prox 3.14 DMED2 2.20 HL2prox 0.87 ADIST7 1.24
H3 prox 2.91 DMED3 2.16 APROX2 0.83 ADIST8 1.19
Dspiny rays 2.73 AMED7 2.03 H6 prox 0.83 DMED14 1.19
H4 prox 2.64 DMED5 2.03 DDIST3 0.78 ADIST5 1.18
H5 prox 2.59 AMED6 2.03 APROX4 0.78 ADIST9 1.13
Aspiny 2.50 DMED6 1.95 APROX1 0.78 ADIST6 1.10
H5 med 2.36 AMED1 1.95 AMED2 0.78 ADIST4 1.08
H4 med 2.32 AMED5 1.93 AMED4 0.78 DDIST2 1.08
Cdist 2.32 AMED3 1.91 H1 prox 0.74 DDIST4 1.05
H6 med 2.27 AMED8 1.91 H1 dist 0.74 DMED13 1.03
Dsoft rays 2.27 AMED4 1.88 APROX5 0.74 DMED11 0.99
H3 med 2.23 HU 3prox 1.88 AMED3 0.74 DDIST5 0.98
H6 prox 2.18 AMED2 1.86 AMED9 0.74 DDIST3 0.97
H2 med 2.09 Asoft 1.74 DDIST2 0.74 DDIST9 0.95
Asoft 1.91 DMED7 1.69 DDIST6 0.74 DDIST1 0.95
H6 dist 1.73 ADIST2 1.64 APROX9 0.74 DDIST11 0.93
HL 2med 1.68 DDIST1 1.64 AMED11 0.74 DDIST7 0.93
H1 prox 1.64 ADIST1 1.64 AMED14 0.74 DMED12 0.92
H5 dist 1.59 AMED9 1.61 AMED5 0.74 DMED9 0.91
H1 med 1.55 DMED8 1.61 DDIST1 0.70 DMED10 0.90
H4 dist 1.50 ADIST3 1.52 H1 med 0.70 DDIST6 0.89
H2 dist 1.45 Aspiny 1.50 H5 dist 0.70 DDIST12 0.86
H3 dist 1.32 DDIST2 1.47 APROX7 0.70 DDIST8 0.83
AMED1 1.23 H1 prox 1.45 APROX8 0.70 DMED8 0.80
ADIST1 1.23 ADIST4 1.44 DMED2 0.65 ADIST3 0.79
HL 2prox 1.18 DDIST3 1.43 AMED1 0.65 DDIST10 0.77
APROX1 1.18 DDIST4 1.43 AMED6 0.65 ADIST12 0.75
APROX2 1.18 ADIST7 1.42 AMED7 0.65 DMED7 0.74
AMED2 1.18 ADIST6 1.38 HU 3dist 0.65 DMED6 0.70
ADIST2 1.18 AMED10 1.35 HL 2dist 0.65 DMED15 0.63
AMED3 1.05 DMED9 1.35 DDIST5 0.65 DMED3 0.62
ADIST3 1.05 HL 2prox 1.34 APROX6 0.65 ADIST14 0.59
H1 dist 0.91 HU 3med 1.28 AMED10 0.65 AMED10 0.58
APROX3 0.91 ADIST5 1.28 DMED3 0.65 DMED4 0.57
ADIST4 0.77 APROX1 1.21 AMED8 0.65 DDIST14 0.56
APROX4 0.73 Dsoft rays 1.21 AMED13 0.61 DPROX11 0.56
AMED4 0.73 Dspiny rays 1.14 H3 med 0.61 DPROX12 0.56
HL 2dist 0.68 DDIST5 1.12 H3 dist 0.61 DMED5 0.55
HU 3med 0.64 APROX2 1.12 HL 2med 0.61 DMED1 0.54
APROX5 0.64 DMED10 1.09 H4 med 0.57 DMED2 0.54
ADIST5 0.64 H3 prox 1.00 H2 dist 0.57 ADIST1 0.53
266 Hydrobiologia (2015) 748:259–272
123
Table 1 continued
5–6 mm SL 6–7 mm SL 7–8 mm SL 8–9 mm SL
Bone D Bone D Bone D Bone D
AMED5 0.59 APROX3 1.00 ADIST8 0.57 ADIST2 0.53
DMED1 0.45 AMED11 1.00 APROXS10 0.57 AMED15 0.51
DMED2 0.45 ADIST8 1.00 H6 med 0.57 ADIST13 0.51
APROX6 0.41 H5 prox 0.97 DMED1 0.57 AMED8 0.46
HU 3prox 0.36 DMED11 0.96 DMED5 0.57 AMED9 0.44
DMED3 0.36 AMED12 0.96 HI 3prox 0.54 APROX13 0.42
AMED6 0.36 H6 prox 0.95 H2 med 0.52 AMED7 0.40
ADIST6 0.36 APROX4 0.92 H5 med 0.52 DPROX9 0.40
DMED4 0.27 DDIST6 0.91 D PROX 1 0.52 DPROX10 0.39
DMED5 0.27 H5 med 0.90 D PROX2 0.52 DDIST13 0.39
AMED7 0.23 H4 prox 0.89 H6 dist 0.52 APROX12 0.37
ADIST7 0.23 DMED12 0.87 ADIST6 0.48 DPROX13 0.36
DDIST1 0.18 ADIST9 0.87 ADIST9 0.48 ADIST15 0.36
DDIST2 0.18 D PROX 1 0.87 H4 prox 0.48 DPROX8 0.33
APROX7 0.18 D PROX2 0.87 DMED4 0.48 APROX14 0.33
DMED6 0.14 D PROX3 0.87 DMED6 0.48 H1 med 0.32
DDIST3 0.14 D PROX4 0.87 DMED7 0.48 DDIST15 0.32
DDIST4 0.14 H6 med 0.86 H5 prox 0.43 H1 dist 0.30
DDIST5 0.14 H4 med 0.86 DMED10 0.43 H5 dist 0.30
AMED8 0.14 APROX5 0.84 ADIST3 0.43 AMED12 0.28
HU 3dist 0.09 D PROX5 0.83 ADIST5 0.43 AMED14 0.27
DMED7 0.09 H1 med 0.80 D PROX3 0.43 DPROX14 0.27
DDIST6 0.09 H1 dist 0.79 AMED15 0.43 AMED6 0.27
DDIST7 0.09 HU 3dist 0.78 D PROX 6 0.43 HU 3dist 0.27
ADIST8 0.09 APROX7 0.77 DPROX7 0.43 AMED11 0.26
D PROX 1 0.05 HL 2dist 0.75 DMED9 0.43 AMED3 0.25
D PROX2 0.05 DDIST8 0.74 DDIST4 0.43 APROXS10 0.24
D PROX3 0.05 APROX8 0.74 APROX11 0.43 AMED4 0.24
D PROX4 0.05 APROX6 0.72 ADIST2 0.43 HL 2dist 0.23
DMED8 0.05 D PROX 6 0.70 ADIST4 0.43 H2 dist 0.22
DMED9 0.05 ADIST10 0.70 DMED8 0.39 APROX11 0.21
D PROX5 0.00 H2 med 0.69 DDIST7 0.39 APROX15 0.19
D PROX 6 0.00 DDIST7 0.69 HU 3med 0.39 AMED13 0.19
DPROX7 0.00 HL 2med 0.67 Dsoft rays 0.39 H4 dist 0.18
DPROX8 0.00 H2 prox 0.65 DMED13 0.39 H6 dist 0.18
DPROX9 0.00 H3 med 0.64 AMED12 0.39 DPROX7 0.17
DPROX10 0.00 H5 dist 0.63 ADIST1 0.39 AMED5 0.16
DPROX11 0.00 H6 dist 0.62 D PROX4 0.35 ADIST16 0.16
DPROX12 0.00 DPROX7 0.61 D PROX5 0.35 H3 med 0.15
DPROX13 0.00 APROX9 0.61 DPROX8 0.35 H3 dist 0.15
DPROX14 0.00 DDIST9 0.57 DDIST12 0.35 APROX1 0.14
DPROX15 0.00 AMED13 0.57 DDIST13 0.35 D PROX5 0.14
DMED10 0.00 H3 dist 0.55 APROX13 0.35 APROX7 0.14
Hydrobiologia (2015) 748:259–272 267
123
attack from the opposite direction. For this reason,
parents generally orient at 180� to each other to be
ready to defend against intruders approaching from
any direction. The next zone, with radii between 30
and 50 cm, is where most parental attacks occurred.
These attacks require parents to vacate the brood,
Table 1 continued
5–6 mm SL 6–7 mm SL 7–8 mm SL 8–9 mm SL
Bone D Bone D Bone D Bone D
DMED11 0.00 DMED13 0.52 ADIST12 0.35 D PROX 6 0.13
DMED12 0.00 H2 dist 0.50 ADIST13 0.35 AMED1 0.12
DMED13 0.00 DPROX8 0.48 DPROX9 0.30 AMED2 0.12
DMED14 0.00 ADIST11 0.48 APROX12 0.30 HU 3prox 0.11
DMED15 0.00 H4 dist 0.46 ADIST14 0.30 H5 med 0.11
DDIST8 0.00 DDIST10 0.39 Asoft 0.26 D PROX4 0.11
DDIST9 0.00 DPROX9 0.35 DPROX10 0.26 H6 med 0.09
DDIST10 0.00 DPROX10 0.35 DMED11 0.26 Cdist 0.08
DDIST11 0.00 DMED14 0.35 ADIST7 0.26 APROX2 0.08
DDIST12 0.00 APROXS10 0.35 DDIST10 0.26 AMED16 0.07
DDIST13 0.00 DMED15 0.30 DDIST11 0.26 H2 med 0.06
DDIST14 0.00 APROX11 0.30 DMED12 0.26 HU 3med 0.06
DDIST15 0.00 AMED14 0.30 ADIST11 0.26 DPROX15 0.06
APROX8 0.00 DPROX11 0.26 DDIST8 0.22 APROX6 0.06
APROX9 0.00 DPROX12 0.26 DDIST9 0.22 APROX16 0.05
APROXS10 0.00 AMED15 0.26 ADIST15 0.22 H4 med 0.05
APROX11 0.00 AMED16 0.26 Cdist 0.22 HL 2prox 0.03
APROX12 0.00 DPROX13 0.22 APROX14 0.17 Dsoft rays 0.03
APROX13 0.00 APROX12 0.22 DDIST14 0.17 D PROX3 0.02
APROX14 0.00 ADIST12 0.22 ADIST10 0.17 H1 prox 0.02
APROX15 0.00 DPROX14 0.17 H2 prox 0.17 APROX3 0.02
APROX16 0.00 DPROX15 0.17 Dspiny rays 0.13 H4 prox 0.00
AMED9 0.00 DDIST11 0.17 DPROX11 0.13 H5 prox 0.00
AMED10 0.00 APROX13 0.13 DPROX12 0.13 Cbase 0.00
AMED11 0.00 APROX14 0.13 Cbase 0.04 Cmed 0.00
AMED12 0.00 APROX15 0.13 Cmed 0.04 Dspiny rays 0.00
AMED13 0.00 APROX16 0.13 DMED14 0.04 HL 2med -0.01
AMED14 0.00 Cdist 0.12 APROX15 0.04 APROX4 -0.01
AMED15 0.00 Cmed 0.09 H3 prox 0.04 Asoft -0.02
AMED16 0.00 ADIST13 0.09 DPROX13 0.00 Aspiny -0.05
ADIST9 0.00 Cbase 0.05 DDIST15 0.00 H6 prox -0.06
ADIST10 0.00 DDIST12 0 Aspiny 0.00 D PROX 1 -0.07
ADIST11 0.00 DDIST13 0 ADIST16 0.00 D PROX2 -0.07
ADIST12 0.00 DDIST14 0 DPROX14 -0.13 APROX8 -0.07
ADIST13 0.00 DDIST15 0 DPROX15 -0.13 APROX5 -0.11
ADIST14 0.00 ADIST14 0 APROX16 -0.13 H3 prox -0.11
ADIST15 0.00 ADIST15 0 AMED16 -0.17 APROX9 -0.14
ADIST16 0.00 ADIST16 0 DMED15 -0.30 H2 prox -0.17
Fin codes: C, caudal; A, anal; D, dorsal; H, hypourals; prox, proximate; med, medial; dist, distal; numbers indicate series number
268 Hydrobiologia (2015) 748:259–272
123
intercept and pursue intruders to drive them from the
vicinity before quickly retreating back to the brood
center. Parental reaction time at these distances is too
long to afford protection for the young. It seems that
for this reason, few young strayed more than 30 cm
from the brood center (Fig. 5).
Brood radii in Rıo Cabuyo 2008
Brood radius increased with Young SL independent of
the number of young in the brood (model
radius = SL ? Number ? SL * Number, F3,32 = 9.08,
P \ 0.001; test of coefficients SL: t = 2.19,
P = 0.036; Number t = 0.21, P = 0.834; SL * Num-
ber t = 0.428, P = 0.672; Fig. 5). The relationship
Table 2 Distribution of sample sizes for parental brood
defense behaviors in 1990, 1991
Study site No of
different
pairs
Size of young (mm) for
1990 ? 1991
1990 1991 Egg/
wriggler
\5 6–8 9–10 [10
Amores
Pool
45 20 52 61 85 51 18
Cabuyo
Pool
36 19 31 64 64 48 16
Amores
Stream
18 20 8 17 40 52 47
Cabuyo
Stream
17 23 8 29 55 49 41
0
20
40
60
80
100
120
140
160
180
0-9 10-19 20-29 30-39 40-49 50-59 60-69 70-79 80-89 90
Fre
quen
cy
Parental attack radius (cm)
JuvCC
AdCC
Long
Dovii
Average
Par
enta
l occ
upat
ion
Low
ris
k of
pre
datio
n
Sho
rt e
scap
e di
stan
ce
Inte
rmed
iate
ris
k
Long
esc
ape
dist
ance
H
igh
risk
Parental intercept and chase Very high risk
1.50
%
4.72
%
15.5
2%
30.2
8%
27.2
9%
10.4
2%
5.55
%
2.70
%
1.27
%
0.75
%
Fig. 4 A Parental attack
frequency as a function of
distance between predator
and brood center by species
of intruder and overall total
mean attack distance per
10-min observation period
(n = 840). Sample sizes and
mean values are given in
Table 2. JuvCC juvenile
convict cichlid, AdCC adult
convict cichlid, Long A.
longimanus, Dovii P. dovii.
Percentages above bars
represent the over
percentage of total attacks
by parents
Table 3 Mean (and standard error, SE) attack frequency per
10-min and attack radius (cm) for parental convict cichlids
defending broods in Rıo Cabuyo and Quebrada Amores, 1990
and 1991. Intruder species are Astyanax fasciatus, Poecilia
gillii, juvenile convict cichlids, adult convict cichlids, Am-
philophus longimanus, and Parachromis dovii
Total Astyanax P. gillii Juv CC Adult CC A. long. P. dovii
Attack frequency
X 6.93 1.75 0.50 1.50 2.02 0.2323 0.34
SE 0.24 0.12 0.05 0.12 0.09 0.02 0.027
Attack distance
X 33.56 17.00 21.39 36.40 40.30 31.17 40.62
SE 0.48 0.47 0.82 0.90 0.59 1.38 1.45
N 764 366 188 463 525 122 220
Hydrobiologia (2015) 748:259–272 269
123
between brood radius and Young SL was not linear. A
significant change point (Siegel & Castellan, 1988)
occurred in the slope of the trend line defining the effect
of SL the change point occurred at 6.45 mm SL
(z = 4.63, P \ 0.001). Individual regressions on pre-
and post-change point data showed a significant slope
of brood radius on Young SL only before 6.45 mm SL
(F1,13 = 7.3, P = 0.019) but not after 6.45 mm SL
(F1,13 = 0.05, P = 0.835). Non-linear increase in
maximum velocity, maximum acceleration, and brood
radius all coincided with the timing of larval ossifica-
tion (Fig. 6).
Discussion
Taken together, field and laboratory data show a
correlation among the morphological and functional
aspects of larval antipredator competence, and the
evolution and expression of biparental brood defense
behavior in convict cichlids.
The overall nonlinear pattern of burst speed with
respect to body length observed in convict cichlids is
similar to the pattern seen in zebrafish (Fuiman &
Webb, 1988). The main determinant of predator
evasion is ontogenetic changes (Wisenden & Keen-
leyside, 1992, 1994) because other aspects of predator
detection and evasion contribute little to escape
potential (Fuiman, 1994; Fuiman et al., 2006). Skeletal
ossification is a convenient and easily quantifiable
measure of ontogeny. The ossification of the skeleton
from cartilage to bone confers greater efficiency of the
forces of muscular contraction into forces of propul-
sion from the fin areas. However, skeletal ossification
is not the sole determinant of locomotory perfor-
mance. Muscle mass also increases dramatically over
the larva-juvenile transition as does fin area and
overall body form, all of which contribute to locomo-
tory performance (Fuiman & Magurran, 1994;
McHenry & Lauder, 2006). The abrupt improvement
in swimming performance of convict cichlid larvae
occurred shortly before 7 mm SL, which coincides
with an abrupt acceleration in, and completion of,
skeletal ossification. Note that ossification scores of
some 7 mm fish clustered with 6 mm fish and some
clustered with 8 mm fish (Fig. 3).
Parental defense data from the field parsed the
young’s living space into zones of risk created by
0
10
20
30
4 6 8 10 12 14
Bro
od R
adiu
s (c
m)
Young SL
Low Risk
Intermediate Risk
High Risk
Fig. 5 Radius of natural broods in the Rıo Cabuyo as a function
of Young SL. The non-linear nature of this relationship is
highlighted by a switch-point in slope at 6.45 mm (solid symbols
and solid line, before 6.45 mm; open symbols and dashed line,
after 6.45 mm)
0
2
4
6
8
10
12
14
16
18
Bro
od r
adiu
s (c
m)
Max Velocity (m/s)
0
2
4
6
8
10
12
14
16
18
0.1 0.2 0.3 0.4 1.0 1.5 2.0 2.5 3.0
Bro
od r
adiu
s (c
m)
Max Acceleration (m/s2)
5 5
6 6
7 7 8 8 9
9
Fig. 6 Parental defense
attack radii as a function of
larval maximum velocity
(left panel) and maximum
acceleration (right panel)
270 Hydrobiologia (2015) 748:259–272
123
differential tolerance for each species of intruder.
Low-risk intruders such as Poecilia and Astyanax are
allowed closer to the brood while medium-risk
predators such as juvenile convict cichlids receive
little tolerance and high-risk predators such as the
piscivorous P. dovii receive none at all. Parental brood
defense behavior recorded in the Rıo Cabuyo system
was broadly similar to that observed by Alonzo et al.
(2001) in Laguna de Xiloa. Like fish in the Rıo
Cabuyo, fish in Laguna de Xiloa increased attack rates
for broods with high numbers of fry, and attack
intensity (in terms of frequency, not distance to
intruder) in accordance with the predation threat
different species of intruder posed to the young
(Alonzo et al., 2001). In contrast to the Xiloa system,
our data did not find an effect of size of young on
attack rates.
Detailed data on parental defense suggest that the
economy of brood defense imposes a limit on defense
radii. Secondly, defense radius is graded in accordance
with the degree of threat represented by each species
of intruder. Thirdly, attack radii are constrained by
parental body size and swimming ability, which in
turn constrains the ecological space in which young
evolved optimal solutions to the foraging/predation
risk trade-off. In sum, these data indicate that parental
care behavior co-evolved in a three-way interaction
with swimming performance of the young and habitat-
specific predation pressure on the young. We predict
that convict cichlids in other systems will have
evolved different equilibria for these traits.
Brood diameter increased as the free-swimming
young grew from 4.5 to approximately 6.45 mm SL.
Expansion of brood diameter during this interval was
most likely a reflection of foraging activity of the
young and not a response to changes in parental
defense because attack radius was determined by
number of young, not size (age) of young. Experi-
mentally enlarged broods show suppressed rates of
daily growth increments relative to unmanipulated
control broods (Wisenden & Keenleyside, 1995),
suggesting that brood radius is a function of the
trade-off between the benefit of foraging and the cost
of predation risk.
Parental defense behavior based on antipredator
competence of the young set the stage for alloparental
care by creating young that differ markedly in
antipredator competence. Convict cichlids routinely
adopt conspecific young from neighboring broods. In
Costa Rican streams, at least 29% of broods contains
unrelated young at some point during the period of
care based on the presence of different size groups
(Wisenden & Keenleyside, 1992) while genetic anal-
yses reveal the actual rate of brood mixing is well
above 50% (Lee-Jenkins et al. unpublished data).
While their young are less than 7 mm SL, parents
judiciously adopt only young that are similar in size or
smaller than their own young (Wisenden & Keenley-
side, 1992). When predators succeed in attacking the
brood, it is the relatively small and weak adopted
young that bear significantly greater predation mor-
tality, sparing the young related to the adopting
parents (Wisenden & Keenleyside, 1994). Moreover,
the antipredatory competence switch-point that we
identified matches the size at which parents no longer
discriminate adoptions on the basis of size, and also
the size at which differential predation occurs in
adopted broods (Wisenden & Keenleyside, 1992,
1994). In broods experimentally manipulated to
comprise large host young and small adopted young,
large young (related to the parents) had significantly
higher survival over 10 days if smaller young were
added to their brood, a rate significantly higher that
what would occur by dilution of predation alone
(Wisenden & Keenleyside, 1994).
These data have bearing on the egg size—egg
number trade-off. Selection for earlier onset of
antipredator competence should select for an increase
in egg size and either reduced fecundity or larger adult
body size. The current body size and egg size/egg
number in this species (or any cichlid) reflects an
evolutionary equilibrium between these competing
life history traits (Kolm et al., 2006a, b). While this
link has always been intuitive, these data empirically
demonstrate the linkage between the ontogeny of
antipredator competence and the evolution of parental
care in cichlids.
Acknowledgments The 1990–1991 field data were collected
with the able assistance of Jeff Christie, Gillian De Gannes, and
Randy Jimenez. Logistical support in 1990 and 1991 provided
by Gordon and Jutta Frankie and Amigos de Lomas Barbudal,
Stewart Family (Quebrada Amores), and el Servicios de las
Parques Nacionales, Costa Rica. 1990 and 1991 data were
funded by an NSERC operating grant to Miles Keenleyside.
Data in 2008 were collected under MINAE Pasaporte de
Investigaciones numero 00058. Special thanks to Celso
Alvarado and Henry Ramirez of the Ministerio del Ambiente
y Energıa, Sistema Nacional de Areas de Conservacion Arenal
Tempisque (ACT MINAE). Ossification and startle responses
Hydrobiologia (2015) 748:259–272 271
123
were enabled by research grants from the College of Social and
Natural Sciences, MSUM to Brian Wisenden, and the Dille
Fund for Excellence (MSUM) to Brian Wisenden and Ellen
Brisch.
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