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Evolutionary Ecology of Fish Venom: Adaptations and Consequences of Evolving a Venom System


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Research on venomous animals has mainly focused on the molecular, biochemical, and pharmacological aspects of venom toxins. However, it is the relatively neglected broader study of evolutionary ecology that is crucial for understanding the biological relevance of venom systems. As fish have convergently evolved venom systems multiple times, it makes them ideal organisms to investigate the evolutionary ecology of venom on a broader scale. This review outlines what is known about how fish venom systems evolved as a result of natural enemy interactions and about the ecological consequences of evolving a venom system. This review will show how research on the evolutionary ecology of venom in fish can aid in understanding the evolutionary ecology of animal venoms more generally. Further, understanding these broad ecological questions can shed more light on the other areas of toxinology, with applications across multiple disciplinary fields.
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Toxins 2019, 11, 60; doi:10.3390/toxins11020060
Evolutionary Ecology of Fish Venom: Adaptations
and Consequences of Evolving a Venom System
Richard J. Harris 1,* and Ronald A. Jenner 2,*
1 Venom Evolution Lab, School of Biological Sciences, The University of Queensland, St Lucia, Brisbane,
Queensland 4072, Australia
2 Department of Life Sciences, the Natural History Museum, Cromwell Road, SW7 5BD London, UK
* Correspondence: (R.J.H.); (R.A.J.)
Received: 14 December 2018; Accepted: 18 January 2019; Published: 22 January 2019
Abstract: Research on venomous animals has mainly focused on the molecular, biochemical, and
pharmacological aspects of venom toxins. However, it is the relatively neglected broader study of
evolutionary ecology that is crucial for understanding the biological relevance of venom systems.
As fish have convergently evolved venom systems multiple times, it makes them ideal organisms
to investigate the evolutionary ecology of venom on a broader scale. This review outlines what is
known about how fish venom systems evolved as a result of natural enemy interactions and about
the ecological consequences of evolving a venom system. This review will show how research on
the evolutionary ecology of venom in fish can aid in understanding the evolutionary ecology of
animal venoms more generally. Further, understanding these broad ecological questions can shed
more light on the other areas of toxinology, with applications across multiple disciplinary fields.
Keywords: evolution; ecology; fish; venom; evolutionary ecology; coevolution; natural enemy
interactions; ecological niche; aposematism; mimicry
Key Contribution: This is a comprehensive review of the evolutionary ecology of venomous fish. It
discusses the consequences and adaptations associated with the evolution of venom systems in fish.
1. Introduction
Animal venoms have been the subject of much research, particularly in reptiles, arachnids,
insects, and cone snails [1–6]. The biological activity of venom components and their characterisation
have been at the forefront of toxinology for many years. This has led to some ground-breaking
biochemical, genetic, evolutionary, and pharmacological discoveries [7–10]. In contrast, the
evolutionary aspects of venom, particularly their evolutionary ecology, remain poorly studied.
Investigating the evolution of venomous traits in the context of their ecology can answer many
questions about how and why venom systems have evolved and shed light on the adaptive value
and ecological implications of evolving a venom system. Venom systems play a vital role as key
fitness components that facilitate survival and reproductive success. Yet, traits relevant to
understanding the evolutionary ecology of venom systems, including their morphology, the
behaviour of venomous organisms, the presence and nature of aposematic, and mimetic traits, as well
as the niche spaces and life histories of venomous species all deserve more detailed investigations
across a broader range of venomous species.
Venomous fish have been relatively poorly studied, both with respect to the composition and
evolution of their venoms [11–13]. The focus of this review is to summarize what is known about the
evolution of fish venoms considered from an ecological perspective and, where possible, to place it
in the context of the evolutionary ecology of other venomous/toxic taxa.
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A Brief Introduction to Venomous Fish: Morphology and Biochemistry
Fish venom systems are thought to have convergently evolved 19 times (we include the toxic
buccal secretions of lamprey as venom) (Figure 1), with more than 2900 species utilising venom as a
form of defence, while a few species use venom for predation/competition [12–15]. Venom evolution
has had a particularly large impact in the lineages Scorpaeniformes (scorpionfish and relatives) and
Siluriformes (catfish), which together comprise the majority of venomous fish species [12] (Figure 1).
Fish deliver venom through a range of structures, such as spines, barbs, and teeth/fangs [12,13]
(Figure 2). Venom spines can be part of dorsal, pectoral, pelvic, and anal fins, as well associated with
or positioned close to the operculum, whilst stingray barbs are found on the tail. Morphological
analyses of fish venom systems indicate that spines are usually associated with some form of venom
gland/secretory cells located near or surrounding the spines. Spines usually contain an anterolateral
groove that allows venom to move from the base of the spine to the tip in a hypodermic fashion
[12,13], allowing the toxins entry into the envenomated target via a wound. Although this is the
general morphology of venom spines, there are differences between species (Figure 2) as would be
expected for convergently evolved systems (see Smith et al. [12] for a more in-depth review).
Figure 1. A phylogenetic tree of fish families (excluding cyclostomes) highlighting all known
venomous families in orange. The exact number of venomous fish families lies between 58 and 63
[12]. The phylogenies of Chondrichthyes and Actinopterygii were obtained from the Time Tree web
project ( and merged using R package phytools [16].
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Figure 2. Examples of the different morphological structures used by fish to deliver venom. This
figure is reproduced from Ziegman and Alewood [11], 2015, MDPI. The venom apparatuses are
highlighted in red: (A) Serrated dorsal spine of chimera; (B) serrated caudal spine of stingray; (C)
serrated pectoral spine of catfish; (D) canine tooth of fangblenny; (E) dorsal and opercular spines of
toadfish; (F) dorsal and opercular spines of weeverfish; (G) dorsal, pectoral, and pelvic spines of
gurnard perch; and (H) dorsal and anal spines with venom gland in stonefish.
Fish venoms contain a plethora of compounds, the majority of which are defensive in nature,
with the sole purpose of causing discomfort and pain to any potential predator. Bioactive toxins from
fish venoms cause a range of neuromuscular, cardiovascular, cytotoxic, and nociceptive effects [11].
The biochemistry of toxins also differs between and within lineages. Large pore-forming toxins, such
as stonustoxin and verrucotoxin can be found in many scorpaenid fish (e.g., Synanceia horrida and S.
verrucosa). Whilst there are many other protein/peptide toxins (dracotoxin, trachinine, and nattectin,
etc.) that have been isolated from different species (e.g., Echiichthys vipera, Trachinus draco, and
Thalassophryne nattereri), they are generally poorly studied [11]. Toxins with unusual and unique
effects have also recently been discovered in some species (Meiacanthus grammistes) [17]. The
proteomic analysis of fish venom is challenging due to the difficulty of collecting them as well as their
lability and the problems of avoiding contamination of the venom samples with mucus from the body
surface [18,19]. Therefore, efforts have been made to develop better methods of proteomic analysis of
these delicate venom molecules for characterisation and functional analysis [20,21].
2. Evolving A Venom System
2.1. The Basics of Antagonistic Coevolution: The Classic “Arms Race”
Before discussing the evolutionary ecology of fish venom systems, we need to clarify some of
the main concepts in this field. Antagonistic coevolution is arguably the main driver in the evolution
of defensive systems [22,23]. Three main ecological functions of venom have been identified: defence,
predation, and competition [2]. Antagonistic coevolution is the key to understanding how predator–
prey and host–parasite interactions have led to the defensive function of venom, and it provides the
Toxins 2019, 11, 60 4 of 21
context within which reciprocal selection pressures create a constant evolutionary “arms race” [22–
25]. Venom is one of the most conspicuous and most frequently evolved adaptations thought to have
evolved via such arms races. Despite this, there is still little empirical evidence supporting the impacts
of these arms races on venom evolution. Moreover, recent studies have indicated the existence of
other kinds of coevolutionary dynamics, such as phenotype matching between venomous predator
and prey or local adaptation of predatory venom eliciting no detectable coevolutionary response in
prey [26,27].
Prey can respond in two ways to these predatory pressures; they can evolve avoidance strategies
and/or evolve antipredator defences [28]. Thus, defensive venoms can evolve in response to intense
predator interactions with prey. It is useful to think of these strategies in terms of Endler’s (1986) five
stages of predation: detection, identification, approach, subjugation, and consumption. Antipredator
defences have evolved to disrupt each of these stages of predation. The primary stages of prey
detection, identification, and predator approach have led to such evolutionary defences as
camouflage and crypsis. The secondary stages of predation, prey subjugation and consumption, have
led to the evolution of chemical defences, such as toxungens, poisons, and venoms [29]. The evolution
of defensive squirting or spitting of venom in several lineages, such as snakes, scorpions,
hymenopterans, and assassin bugs, also plays a role in deterring predator approach once the animal
has been detected. The possession of these powerful chemical weapons consequently led to the
evolution of aposematism and mimicry. Once evolved, aposematism and mimicry could then disrupt
the earlier stages of predation and help minimise the use of metabolically costly venom toxins.
However, aposematism and mimicry would not evolve without effective defensive mechanisms,
such as venom, being in place. These toxic defences are commonly a last resort strategy, with
chemically defended organisms usually having some other and cheaper form of defence to deter the
early stages of predation, e.g., camouflage or aposematic warnings [22,30–32]. Defensive venoms,
particularly in fish, have evolved to cause immediate and intense pain to the predator, which creates
a window of escape time [2]. Defensive venoms have therefore been shaped by selective pressures
exerted by predators.
Conversely, venoms used for predation have a benefit of a high energy reward for a successful
predatory hunt. Predation is a common driver for venom evolution [2], one that has been studied the
most. Predatory venoms have evolved primarily to subdue prey rather than to outright kill them.
This is probably because the energetic demands of using venom to kill prey would outweigh the
fitness benefits gained over just subduing prey [33,34]. Predatory venoms, unlike defensive venoms,
have generally not evolved to cause pain but to immobilise prey [2]. They target neuromuscular
pathways to cause paralysis or disrupt hemostasis and the coagulation/anticoagulation of blood [2].
It is the need of evolving toxins to efficiently immobilise prey and the evolution of toxin resistance in
prey that drives predatory venom evolution [35].
It should be noted that venoms, in particular predatory venoms, can have both predatory and
defensive roles [36,37]. This has led to the evolution of dual purpose venoms [5,38,39]. This would
suggest these have arisen despite different, or possibly competing, selective pressures acting on them.
2.1.1. Evolving Venom for Defense in Fish
Many species of fish utilise spines as a form of defence from predatory attacks [12,13]. However,
not all spine defences contain venom [13], and having non-venomous spines may not be as effective
against predators [40]. Non-venomous spines differ in their defensive strength depending on shape,
size, and stoutness, etc., and adding venom increases this defensive strength [40,41]. Thus,
antagonistic interactions have led to the evolution of spines and then secondarily to the evolution of
venom or to both simultaneously. Yet, if and how spines and venom have evolved in conjunction,
which has recently been demonstrated for the venom and venom apparatus of rattlesnakes [42,43], is
a topic that needs more investigation.
It has been hypothesised that venom glands in fish evolved by the thickening and aggregation
of epidermal cells that produced antiparasitic toxins near defensive spines [44]. Skin secretions in fish
contain ichthyocrinotoxins, which are known for having antimicrobial, antiparasitic, and antifouling
Toxins 2019, 11, 60 5 of 21
activities [44–48]. Moreover, experiments on gobies suggest that ichthyocrinotoxins can play an
important role in predator avoidance [49,50]. Compounds that are thought to be primarily involved
in host–parasite and antimicrobial interactions may therefore have played a role in the evolution of
fish venoms, as skin mucus toxins contribute to envenomation effects [20,51–53]. Further, evidence
suggests that the stonustoxin (SNTX) gene family has evolved from an ancient antiviral protein
superfamily [48]. A secondary use of venom for antiparasitic defence has evolved in other taxa as
well, such as social Hymenoptera [54] and slow loris [55]. Toxins are spread over the body in slow
loris and nests in hymenopterans, reducing parasitic infection [54,55]. This hypothesis of fish venom
evolving from skin secretions is plausible, as crinotoxic gobies are more effective at avoiding
predation than closely related non-toxic species that are protected solely by spines and tough scales
[49], and species of porchthyine toadfish can cause envenomations, yet there is no macroscopic
evidence of any form of venom gland associated with spines [12,13,56]. This suggests the toxins may
be on the epidermal surface of the spines or located in primitive secretory cells. Similar spine
functions can also be seen in other taxa, such as recently discovered venomous frogs (Corythomantis
greeningi and Aparasphenodon brunoi) [57]. They have small skull spines, located near epidermal skin
glands filled with toxins. The spines are used to deliver the toxins into the predator’s system through
a wound [57]. Frogs, like fish, also have antimicrobial skin toxins [58,59], and it is possible that these
venomous frogs have convergently evolved a venom system reminiscent of that found in venomous
fish. A recent study has confirmed that mucosal skin secretions and venom extracts in Scorpaena
plumieri share similar proteins and that these are found across multiple species as well, even in non-
venomous fish [20]. However, the authors only attempted to show that skin mucus proteins do not
produce any physiological effects different from venom gland envenomations. Their assays did not
consider whether skin mucus proteins may be for parasitic defense or might have different biological
activities compared to venom gland proteins.
There is little research into predator–prey interactions as drivers of defensive venom evolution
in fish. The only available investigations of predator responses to venomous fish prey are focused on
catfish [41], and studies of the pharmacological effects of fish venom toxins are restricted to mammal
species that are not natural fish predators. One major difficulty is that venomous fish tend to have
multiple predators, e.g., stonefish (Synancea spp.) are predated on by sharks, rays, and sea snakes [60],
whilst (in their natural habitat range) lionfish (Pterois spp.) are predated on by sharks, eels, and
groupers [60,61]. These different predators may have different susceptibilities to the defensive venom
of their prey. Another problem is that defensive venoms are effective against a wide range of
organisms, even non-natural predators. Therefore, it is uncertain that a single predator species would
drive the evolution of a defensive venom. This taxonomic diversity of predators could explain why
many defensive venoms are non-target specific in both venom composition and delivering systems
[11–13]. Although interactions between predators and venomous fish prey have not been thoroughly
investigated, there is strong evidence that such interactions have led to the evolution of defensive
spines [62], which are a necessary apparatus for delivering venom.
Based on these ideas it is possible that in some species of fish, host–parasite or antimicrobial
interactions may have set the stage for skin toxins to evolve whilst predator–prey interactions have
led to the evolution of spines. Selection pressures for increased antipredator defenses then allowed
for the recruitment of skin toxins into spine-associated venom. Gene duplication is already thought
to have been involved in the evolution of venom in Scorpaeniformes [48,63]. These are hypotheses
that need further testing and although antagonistic coevolution may have played a role in evolving
spine defenses, the number of convergent origins of fish venom systems suggests that there are strong
selection pressures for the evolution of venom in fish.
In contrast to venomous spines, Meiacanthus blennies utilise unique venom fangs that are located
on the lower jaw [17]. In most fanged venom systems, defense is used as a secondary function after
predation. Meiacanthus’ diets mostly consist of coral polyps, zooplankton, and small invertebrates
[64]. Catching this food does not require venom and therefore the venomous fangs suggest a
defensive role. However, some research tested the defensive pain inducing toxins of Meiacanthus
venom with regard to mammalian subjects, which produced no significant reaction [17]. Yet, it is
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unlikely their venom has evolved to target mammals, and thus pain inducing toxins could still be
present but rather target predatory fish. This same study also highlights other toxins for defense
causing hypotensive and inflammatory effects. Further, these biochemical assays suggest a defensive
role may not be the only ecological function of the venom [17]. Competition is a possible evolutionary
driver of fangblenny venom as well (see Section 2.1.3).
2.1.2. Evolving Venom for Predation in Fish
Predation is a strong driver of venom evolution. As previously mentioned, selection pressures
acting on venom specificity to prey are thought to arise in many predator–prey interactions. A
constant battle between increasing efficiency for subduing prey and toxin resistance of prey lead to
these coevolutionary cycles, yet this is an area of little research and may be more complex than simple
antagonistic coevolution [26,35].
The use of venom for predation is mostly associated with delivery apparatuses located close to
the mouth of an organism, e.g., fangs, pincers, beaks, and probosces [2]. Only two fish taxa utilise
fangs/teeth for venom-based feeding, Monognathus (jawed eels) and lampreys (Petromyzonidae)
[12,17,65]. In jawed eels, the fixed rostral fang is located on the upper jaw [12] (Figure 2). This is highly
indicative of the fang playing a role in subduing prey, like in snakes, although the diet of Monognathus
eels is not well studied. Due to the scarcity of prey items in deep-sea habitats, most deep-sea
organisms are opportunistic hunters of many prey types [66]. Consequently, venom for predation
would be highly adaptive in desolate environments to ensure prey do not escape. Research on the
composition and bioactivity of Monognathus venom is needed, as well as observations of how they
use their venom.
Lampreys are an ancient lineage of jawless fish that utilise a toothed sucking-buccal cavity. Most
species of lamprey engage in parasitic micropredation, attaching their mouth parts to larger hosts in
order to blood feed for a prolonged period [65]. This kind of predation has evolved frequently in
hematophagous organisms such as leeches, ticks, mosquitos, and bats [67–69]. Some studies have
highlighted key components of their venom secretions, including anticoagulants, and their
nociceptor and immune response inhibitors [14,70,71]. Lampreys are known for their wide dispersal
and habitat ranges, being carried to new areas by attaching to migrating hosts [72–75]. The use of
host attachment and blood feeding toxins might have evolved in parallel. The longer a lamprey can
attach to a host to reach a specific destination whilst being able to feed, the better its chances of
survival throughout the journey. This unique lifestyle may have driven the evolution of this venom
system, firstly, by evolving numbing toxins to avoid detection by their hosts and, secondly, by
evolving anticoagulants to keep blood flowing over long migration ranges [14,71,74]. Very little
research has been conducted on how these micropredatory venoms have evolved, be it before or after
the evolution of host-attachment. Lampreys are an ideal model for these investigations as they are
the only fish to utilise this strategy.
2.1.3. Evolving Venom for Competition in Fish
Venom used for competition is a rare occurrence with few animals, such as the platypus
(Ornithorhynchus anatinus) and slow loris (Nycticebus spp.) utilising this function. It is worth noting
that there is a fine distinction between defensive and competitive venom, as both are interchangeable
in function. The distinction between them is based on the selective pressures that elicit the venom
evolution and how they are used, be it toward conspecifics or predators.
In fish, it is possible that competition has driven the evolution of one venom system associated
with Meiacanthus fangblennies. The biological activity of Meiacanthus grammistes venom is unique.
The venom causes hypotensive, neurotoxic, and proinflammatory effects. These functions act to
disorient attackers, rendering coordination and swimming difficult [17]. Yet, their venom may also
play an important role in intra- and interspecific competition. Blennies are known for their intense
competition for territory and aggressive combat with competitors [76–78]. The biological activity of
their venom would be advantageous against competitors as disorientation and hinderance in
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coordination would increase the probability of the competitor becoming an easy target for predators,
permanently removing the competition from the environment.
This intense competition for territory may have increased selection pressures on blennies to
evolve fangs and venom. The evolution of venom has led to an increasing evolution of mimicry in
blennies (see Section 3.2), further suggesting that the function of this trait is highly successful with
many mimetic adaptations arising as a consequence [17].
It is uncertain if other fish species also utilise venom in this way. However, it has been suggested
that the venom apparatus of stingrays has evolved primarily for a role in intraspecific aggressive
encounters [79]. The reasons for this hypothesis are the relatively low toxicity and low metabolic cost
of the venom, the use of the sting on conspecific individuals, and observations that the sting is not
used on attacking predators. Although defensive stingray barbs injure many people worldwide every
year, it has been noted that when handling them, they generally sting very reluctantly [79,80]. The
primary role of the relatively non-damaging venom may therefore be in social interactions. However,
further research investigating the evolutionary ecology of stingray and fangblenny venoms is clearly
needed. This can help us understand the selection pressures arising from competitive and non-
predatory aggressive interactions and their possible role in the evolution of these venom systems.
3. Consequences of Evolving A Venom System
3.1. Aposematism
Aposematic warning signals are prominent in many chemically defended organisms [81]. They
display warning signals as bright contrasting and conspicuous patterns, warning predators of their
chemical arsenal [62,81]. This kind of defence goes hand-in-hand with defensive venom evolution,
and this is no exception for venomous fish. These aposematic patterns have evolved to deter
predators in the primary stages of predation (see Section 2) [22]. Evolving warning colouration allows
predators to learn avoidance of specific colour patterns, preventing them from being envenomed
Since venom has convergently evolved in fish, aposematic colouration has also convergently
evolved, as some examples will show. The lesser weever fish (Echiichthys vipera) has a dark dorsal fin
with yellow spines that stands out in stark contrast to the white/silver colouration of the body (Figure
3A). Contrastingly, dark spine defences highlight to any predator the consequence of attack [62,81].
Weever fish often flare their dorsal spines as a response to nearby movement [82]. This is consistent
with the behaviour observed in many other taxa with defensive spines [83]. E. vipera also has a yellow
and black banding pattern on its caudal fin (Figure 3A): alternating black and yellow colouration is
an aposematic pattern that has evolved convergently in a range of venomous and poisonous taxa,
including snakes, amphibians, myriapods, spiders, and many hymenopteran species [31,84–88].
Banding patterns may simultaneously act as dazzle camouflage, causing disruptive blurring of the
body outline whilst in motion [87]. This causes predators to misjudge the distance and movement of
prey, increasing the probability of missing their intended target [89,90]. Lionfish (Pterois volitans) are
known for their banding pattern (Figure 3B). Because they hunt in the open water, their pattern may
not only act as an aposematic warning but also provide active camouflage when hunting and being
hunted [81,87]. Plotosus catfish and Meiacanthus blennies exhibit these banding patterns for both
warning and camouflage. (Figure 3D,E). The bluespotted ribbontail ray (Taeniura lymma) has a
distinctive aposematic spot pattern with iridescent blue colours (Figure 3C). Spot patterns are highly
effective in warning predators of a chemical arsenal [91]. Blue spot patterns are efficient in the aquatic
environment and are similarly found in such species as blue-ringed octopus (Hapalochlaena lunulata)
[92]. Many marine predators, such as fish, crustaceans, cetaceans, pinnipeds, and marine birds have
visual systems that are sensitive to blue-green wavelength colourations (~400–500nm) [93–96].
Species of the Inimicus genus of scorpionfish have contrasting coloured pectoral and caudal fins in
comparison to their body (Figure 3F). These warning fins are flared out when a predator is close,
advertising its venom defence.
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Figure 3. Examples of aposematic colouration adopted by venomous fish species: (A) Lesser weever
fish (Echiichthys vipera); (B) Lionfish (Pterois volitans); (C) Bluespotted ribbontail ray (Taeniura lymma);
(D) Striped eel catfish (Plotosus lineatus); (E) Striped fang blenny (Meiacanthus grammistes); and (F)
Devil scorpionfish (Inimicus didactylus). Image copyrights ©: Rachel Scott, Niels Sloth via , Jens Petersen via CC BY 2.5, Elias Levy via CC BY 2.0, Neil Hepworth—Bauer Media via, David Harasti via
Because aposematism deters predators at the primary stages of predation, its evolution may be
driven by the energetic demands of venom production and replenishment (see Section 4). Venom is
energetically costly and many organisms opt to use as little as possible [34,97]. Warning colouration
allows organisms to conserve venom by warning predators of their toxins. However, aposematism
can evolve in species with non-venomous spines. Thus, energy costs of toxin production may not be
the only driver of aposematism.
Aposematic signalling tends to be rare. Data from amphibians suggest that one explanation for
this is that over evolutionary time, aposematism is often short lived in lineages with cryptic
colouration frequently replacing it [98]. Transition rates from aposematic lineages to either
polymorphic or cryptic lineages are substantially higher than in the reverse direction. However,
selection for crypsis over aposematism might depend on the strength of the secondary defense [99].
In this case, highly effective venom toxins may allow for aposematism to be maintained, yet weak
venom may allow selection pressures to favour crypsis.
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Although aposematism is well studied, there are large gaps in the literature that need to be
investigated. The selection pressures that act to maintain aposematism or push toward crypsis is an
area that should be investigated more. Fish are excellent models as many venomous species exhibit
crypsis and/or aposematic patterns, as shown by the above examples. Furthermore, most research
has focussed on the implications of prey evolving aposematism. Although there has been much
research on the effects of aposematism on predators, more research is needed. Firstly, not much is
known about how predators make adaptive decisions in learning avoidance of aposematic signals
[100]. Secondly, there are few ideas about how these avoidance behaviours are adopted socially
throughout a predator community and how individual predators make adaptive decisions when
targeting prey. Much of the work conducted focuses on terrestrial organisms. Venomous fish provide
a great platform for comparison between terrestrial and marine taxa. Focussing on the ecology and
macroevolution of aposematism in venomous fish may aid in understanding aposematic evolution
and how predators learn avoidance.
3.2. Mimicry
Mimicry is the evolution of analogous appearances, behaviour, or scent that predators or prey
associate with species they either try to lure or avoid, respectively [62]. The purpose of a mimic is to
cheat a predator/prey via means of deception, by causing them to be perceived as either a harmful
species (Batesian and Müllerian) or a harmless species (aggressive and Mertensian) [62,101,102].
Mimicry can be deemed as parasitic toward the model or mutualistic with both benefitting
simultaneously [62]. Many venomous species that are aposematic tend to serve as desirable mimetic
models for non-venomous species [17,30,103,104].
3.2.1. Batesian
Batesian mimicry is when an unpalatable species (model) displays aposematic signals which are
copied by a palatable species (mimic). In the case of fish, we refer to venom as being the unpalatable
Batesian mimicry has been demonstrated for both poisonous [105] and venomous fish [17]. A
recent study found strong evidence for Batesian and aggressive (gaining access to an otherwise non-
approachable prey) mimetic phenotypes in fangblennies (Nemophini). There are five genera in
Nemophini: one venomous genus (Meiacanthus) and four non-venomous genera (Petroscirtes,
Cheilodiperus, Plagiotremus, and Escenius) [17]. It was found that all non-venomous genera were
Batesian mimics of Meiacanthus. This Batesian mimicry allows for mimics to appear harmful to
predators, falsely warning of their supposed “venom” [17]. It may also act to deceive even closely
related species in territorial competition. The Plagiotremus genus also shows aggressive mimicry, in
that they utilise these colour patterns to gain access to skin feeding in larger fish that only allow
specific cleaner species to skin feed [17,106,107]. The phenotypic convergence of colouration between
Meiacanthus and Plagiotremus is one of very few examples of Batesian-aggressive mimicry. It seems
that both defence and micropredation may have facilitated this unique convergence [17].
Under normal circumstances, both mimicry systems allow advantage to be taken of the model
(Meiacanthus). For Batesian mimicry, the model bears all the pressure in educating predators, whilst
the mimic gains the benefit of an increased fitness when the mimic population numbers are less than
the model [62]. In aggressive mimicry, if the frequency of attacks by the mimic is increased, then the
model suffers an increased intolerance by the larger fish and attack rates are increased for the model
too [108]. However, when both mimicry systems work in tandem, they are beneficial for both the
model and mimic. For example, aggressive attacks on predators by the mimic may strengthen learned
avoidance for the model–mimic colouration by predators [106]. When these mimetic systems work
together, they may even be categorised as Müllerian with both species being unpalatable or as quasi-
Batesian where both species are unpalatable, but the model is more so [109–111].
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3.2.2. Müllerian
Müllerian mimicry occurs when two or more chemically defended species share similar
colouration [62]. Müllerian mimics share predator education and thus can mutually coexist as a single
community structure [62,109], and their aposematism can be maintained over evolutionary time
through coevolution of the Müllerian mimics [112]. The abundance of multiple Müllerian mimics in
a community can lead to the complex divergence of “mimicry rings” [113,114]. These structures have
been observed in venomous Corydoradinae catfish [103]. Corydoras mimicry rings are unique in that
species within them differ in colouration from related species in distant communities, whilst
unrelated species share similar colourations [103] (Figure 4). Alexandrou et al. [103] observed 52
species that adopted 24 mimicry ring communities, with multiple unrelated species all coexisting in
stable communities. This has allowed the existence of co-mimics that would be competing for trophic
resources without mimicry [103]. Although their patterns are similar, they differ in other
morphological features, such as snout length, which lessens competition for resources [103,112].
Figure 4. Examples of Müllerian mimetic patterns in venomous Corydoras catfish mimicry ring
communities. (A) Corydoras multimaculatus, C. araguaiaensis and C. sp. (left to right) and (B) C. imitator
(left) and C. sp. (right). Images courtesy of © Martin Taylor via
Research has mostly focussed on the negative aspects of Batesian mimicry, such as how the
mimic benefits whilst the model is burdened with predator education. In contrast, positive
interactions (e.g., mutualisms) of Müllerian mimicry and even Batesian-aggressive mimicry, which
facilitate the longevity and coexistence of multiple species, have been relatively overlooked. Research
into multiple mimetic systems acting in conjunction is also lacking. There is an absence of data
regarding these systems, whereby two distinct selection pressures act upon multiple species that
exhibit mimetic colouration. Research concerning mimicry ring formations is also essential.
Understanding how these ring communities diverge and change and the factors influencing the
longevity of these systems are poorly understood. Further, investigating venom variation or strength
in Corydoradinae mimicry rings will help us understand more complex phenomena such as super-
Müllerian mimicry, when two chemically defended mimics have differing toxin strengths, and how
these lead to greater learned avoidance by predators [115].
Better understanding of mimetic relationships in fish could highlight key facets of how evolving
a venom may affect the ecology in a community structure. This may also help us to understand other
mimetic systems, both terrestrial and marine.
Toxins 2019, 11, 60 11 of 21
4. Energetic Implications of Evolving A Venom System
The utilisation of a defensive venom can be costly to an organism’s fitness when the predatory
presence is low. This is because the production of toxins is energetically demanding, competing with
the energetic demands of growth and reproduction [62]. Therefore, the selective pressures on venom
must be balanced by sufficient predatory presence and energy harmonising.
Replenishment of toxins after use can be energetically demanding to an organism [33,97],
although not all venoms are metabolically costly [79]. The energy used on replenishment can reduce
fitness and survivability, as it can take up to several days [116,117], leaving them chemically
undefended. It was shown that venom replenishment of key toxins in Synanceia horrida can take 28
days, with full venom yield taking longer depending on feeding conditions [118]. These energetic
constraints may potentially explain why many venomous organisms adopt other forms of defence,
such as crypsis and aposematism (see Section 3.1) [62]. In venomous fish, although aposematism and
crypsis are common, the adoption of a sedentary lifestyle is also prevalent [44]. This is seen in species
such as stonefish, scorpionfish, waspfish, and weeverfish. Sedentary fish have low metabolic rates
and decreased locomotory functions after feeding, in comparison to active fish [119]. This
sedentary/sit-and-wait lifestyle may have evolved in venomous fish for energy conservation,
balancing the energetic demands of venom with growth and reproduction. There are certainly many
venomous taxa with a sit-and-wait lifestyle, such as viperid snakes and spiders. It is possible that
energetic demands of venom have led to the evolution of sedentary lifestyles, as well as aposematic
and cryptic colourations.
Venomous taxa can employ other strategies that reduce the energetic costs of venom use, such
as venom metering and dry-bites/stings [34]. Venom metering controls the amount of venom injected
per bite or sting, gauged by factors such as prey size or predator threat [34,120,121]. Although venom
metering has not been investigated in fish, it is unlikely for their defensive venoms. This is based on
the morphology of venom structures [12,13]. Venomous spines/barbs lack structures that allow
behavioural venom metering provided by fangs or stingers in other venomous taxa. Venoms from
spines are released via a pressure mechanism [12,13], whereby the venom gland/tissue is deformed
or ruptured upon pressure. It would be difficult for this mechanism to allow control of the venom
volume released. However, it is entirely possible that fish that utilise venomous fangs, e.g.,
Meiacanthus and Monognathus, could control venom output.
The evidence that venomous taxa can control the volume of venom delivered, along with a
sedentary lifestyle in many venomous species, suggests that the energetic cost of venom production
is an important constraint both evolutionarily and ecologically. More research is required to assess
the energy demands of evolving venom, particularly the ecological constraints that it poses and the
adaptations that might help to balance the energy budget.
5. Intersexual Variation in Venom
Sexual variation of venom composition has been documented for a few taxa, principally spiders,
scorpions, snakes, and a species of fish [122–125]. Research on Thalassophyrne maculosa (cano toadfish)
showed that male venom had double the protein content of that of females and differing bioactivities,
with males having a greater target affinity to nociceptors whilst females had greater proteolytic
activity [123]. From an ecological perspective, one may speculate that these differences could relate
to reproduction and brooding. A lower protein concentration in females may be linked to energetic
balancing of venom and reproduction. Having a lower yield means energy on venom maintenance
can be reallocated to other needs, such as reproduction. Conversely males may have a higher protein
yield and potency for guarding of the eggs from predators and conspecifics [126,127]. Similar
observations have been made in other species, such as spiders. One study found that females that
were carrying eggs had a lower venom yield and fewer proteins present than females without eggs
[128]. Yet, venom may not be sex specific but related to other factors such as diet, health, and size.
Certainly, sexual dimorphism of size is common in nature, and it could be argued that size is a major
factor in explaining why venom potency and yield are different between sexes. However, this does
not explain the variance in protein content and bioactivities between sexes.
Toxins 2019, 11, 60 12 of 21
More research is needed on interspecific venom variation and how this relates to ecology. These
differences may be vital in understanding how energy is balanced between venom production and
other ecological demands.
6. Ecological Niches, Life History, and Venom Evolution
As antipredator defences evolve to reduce predation, it would logically suggest that evolving
venom would reduce ecological constraints. For example, an increase in niche space may occur, as
less predators would allow for a greater freedom of movement [129].
Research conducted on chemically defended musteloid mammals (they secrete repellent
compounds) suggests that chemical defence increases niche space, increasing foraging times, diet
diversity, and activity periods [130]. However, no investigations regarding niche space of venomous
organisms have been conducted. Since the overarching function of fish venom is for defence, they
may similarly increase niche space. A study on butterflyfish (Chaetodontidae) showed that robust
and longer dorsal spines led to an increase in riskier foraging behaviour [131]. Although it is
unknown if butterflyfish are venomous, their spine morphology has the characteristics of venom
spines. Still, it is interesting that defensive spines can alter foraging strategies regardless of whether
they deliver venom or not.
Lionfish, Pterois miles and P. volitans, are known for having broad niches on native reefs,
particularly regarding foraging ranges and diet [132–134]. This broad niche range is possibly
attributable to their venomous spines, with few predators to limit foraging strategies. This might be
why they have caused invasive devastation across reefs in the Caribbean and Gulf of Mexico [132–
134]. Studies comparing the behaviour of native and invasive lionfish populations indicate no
difference between foraging strategies and niche ranges, although invaders capture larger sized prey
[134]. Is their broad niche range and wide variety of prey items a consequence of their possession of
venom on both native and invaded reefs? With little research investigating the ecological implications
of venom on foraging ranges and diet, it is difficult to determine. Yet, chemical defence is one aspect
in which foraging in new areas without natural predators has led to widespread upheaval of
communities [132,133,135]. Lionfish and their invasive behaviour would be an ideal model to
understand how niches are affected by the evolution of a defensive venom.
This niche alteration may also occur with predatory venoms. Hematophagous lampreys have a
large range of habitats, wide reproductive dispersal and low selectivity of host–prey [74]. It is their
lifestyle of host attachment in combination with anticoagulant venom (see Section 2.1.2) that may
have allowed for long migrations and dispersal. The evolution of venom certainly allows for lamprey
to attach to hosts longer, increasing migration and dispersal, whilst finding new breeding grounds
and hosts when resources change. Therefore, it is plausible the evolution of a predatory venom may
have aided their successful increase in niche space, range, and host prey. Certainly, more research
needs to be conducted investigating how the evolution of both defensive and predatory venoms may
alter niche characteristics.
Although much research has shown how venom can vary with changes in prey type [36,136,137],
there are fewer investigations about how specific diets may put evolutionary constraints on venom.
For example, a shift in diet may allow for constraints of venom evolution to be removed. This concept
might fit with the evolution of venom in Meiacanthus fangblennies. The evolution of elongated
canines evolved at the base of the Nemophini clade; however, venom evolution did not occur until
much later with the origin of the Meiacanthus genus [17]. Interestingly, Meiacanthus is the only genus
within Nemophini that has a different diet, tending to feed on small invertebrates [138], rather than
opting for scales/skin feeding of larger fish. This is a very interesting facet, as defensive venom might
not evolve in skin feeders as the larger fish would feel the effects of venom and therefore learn
avoidance of these fish. It has been observed that a dietary shift can lead to the loss of a venom trait
as well [139,140]. Therefore, the reverse should also occur, where a change in diet either frees
constraints or initiates positive selection pressure for evolving a venom. It is interesting that other
factors such as specific diet may play an important role in restricting the evolution of venom when a
potential delivery system has already evolved.
Toxins 2019, 11, 60 13 of 21
Some research has suggested that the evolution of aposematism with regards to a toxic arsenal
can also have similar effects on niche [130,141]. Yet, there is a fine divide between discerning if these
changes in behaviour occur due to the evolution of the toxins or the warning colouration as both
evolve in conjunction with each other. Thus, experiments may be difficult to conduct regarding this
It is not just the ecological niche that can be affected by the evolution of a chemical defence, life
history traits are prone to alteration as well. Chemical defences have evolved to increase longevity
by reducing predatory mortality rates [142]. They have been shown to lead to slower life histories
and increased longevity in amphibians [143], with venomous fish also corroborating this [144]. Yet,
some research contradicts this positive relationship, with findings of a negative correlation in
chemically defended musteloid mammals [130]. The authors suggest that physiological mechanisms
of chemical defence may reduce life span due to oxidative stress damaging vital tissues shortening
life span [145]. They also note that this negative relationship may be due to variables affecting both
chemical defence and longevity making them appear correlated [130]. It should be noted the possible
contradictions may be due to the difference in chemical defence type and utilisation. It is possible
that the chemical defences of musteloid animals (secretions from anal glands) have different
ecological consequences for longevity than skin secretions or venoms and this may cause these
contrasting patterns.
Future investigations should aim to compare how venom affects the longevity of an organism.
Venomous fish can be a perfect model to investigate this, as within families, there are closely related
venomous and non-venomous species that can provide a comparison of longevity and venom.
Further, investigations into how different functions of chemical defences can lead to differences in
longevity, e.g., venom vs. poison or defensive vs. predatory venom functions.
7. Diversification Rates and Venom Evolution
The study of ecological factors may illuminate how diversification works and can help us
understand how these factors may lead to phenotypic diversity and speciation. The “escape and
radiate” hypothesis [129] identifies chemical defences as a factor increasing diversification and
speciation. However, very little research has been conducted on this concerning venom [146].
The only study regarding venom diversification in fish showed that venom gland evolution has
increased diversification in Meiacanthus blennies [147]. Further studies investigating
macroevolutionary diversification showed that evolving venom in reptiles and mammals has
increased diversification rates as well [3]. Despite this, other research has shown a negative
association between diversification and venomous stings in ants [148]. With these differing trends
between taxa, the association of diversification and defensive toxins might not be based on the
chemical arsenal but the delivery system involved, with some delivery systems being more effective
than others. This may be a key area for future investigations.
A study of amphibian chemical defense showed that lineages that were chemically defended
had increased speciation rates yet also increased extinction rates [98]. This extinction risk may also
play an ecological role in venomous fish lineages. It is noteworthy that most toxic amphibians utilise
defensive toxins as poisons rather than venom like fish; however the functional strategy remains the
Understanding diversification across lineages using phylogenetic comparative methods such as
ancestral state estimations, trait evolution models, convergent evolution and dynamic diversification
analyses may provide substantial evidence about the ecological relevance of evolving toxic traits
[146]. Fish may provide an excellent model to study these due to the wide array of convergently
evolved venoms and large phylogenetic diversity within fishes [12,13]. Further research should aim
to demonstrate if diversification rates differ based on the type of venom apparatus evolved. Fish have
adopted an array of different apparatus across lineages and thus provide a solid basis for the
comparison of diversification. It remains unclear if this increased extinction risk also applies to
species that primarily utilise defensive venoms. Fish would be good candidates to investigate this as
many venomous taxa are considered threatened species.
Toxins 2019, 11, 60 14 of 21
8. Conclusions and Future Directions
Research regarding the evolutionary ecology of venom systems is scarce, not just in fish but
across animals in general. As fish represent the largest group of vertebrates, coupled with their vast
convergence of venom, it stands to reason that exploring the evolutionary ecology of venom in fish
has great potential to shed light on unanswered questions regarding venom evolution.
Exploring the evolution of defensive fish venom, including its role in interactions with
predators, could shed more light on the relationship between skin mucus ichthyocrinotoxins and
venom components, as well as illuminate how venom systems have evolved as integrated
phenotypes in fish. This could help improve our understanding of how venom systems evolve from
systems with other systemic functions, and how predator–prey/host–parasite interactions influence
venom evolution.
More studies on how defensive fish venom systems interact with predators are needed to shed
more light on the ecological drivers in venom evolution and the mechanisms acting as selection
pressures in fish communities. Further investigations on the coevolutionary interactions between
venomous fish and their predators can illuminate the relative importance and frequency of different
types of ecological and evolutionary dynamics, such as arms races or phenotype matching between
predators and prey, in the shaping of venom systems more generally. The convergent evolution of
defensive fish venom systems is especially useful for studies that aim to understand how these
interactions act to increase divergence and speciation.
Aposematism and mimicry are prevalent consequences of evolving a venom system. Fish
highlight these strategies in myriad ways not only from the perspective of phenotypes but also from
that of the complex community interactions that arise with mimetic relationships. This makes
venomous fish a solid model for the study of these systems.
Applying phylogenetic comparative methods to venomous fish taxa has the potential to
highlight how important evolving this system is from an ecological perspective. Understanding how
a trait is evolved on a broad scale may further lead to the recognition of how and why these complex
systems evolve across longer evolutionary timescales. Furthermore, the link between diversification
and extinction [98] urgently needs more research.
By studying the evolutionary ecology of venom, we can begin to cross disciplinary lines within
toxinology more confidently. Understanding how venom has evolved on an ecological scale will
allow us to better understand the purpose and function of venom on a biochemical and genetic level.
Venom systems are integrated phenotypes that comprise many components with interrelated
functions across different levels of organisation, from individual toxic molecules to complex
morphological delivery systems and from behavioural adaptations to aposematic and mimetic
colours and patterns. The study of such systems in large groups such as fish is a promising avenue
to advance our understanding of venomous taxa and their evolution.
Author Contributions: R.J.H. conceived and designed the review topic and wrote the first draft of the
manuscript, contributing to subsequent drafts and changes thereafter. R.A.J. edited, amended, and added further
research and insights to the manuscript. Both authors revised the final manuscript after editor feedback and
gave the final approval for publication.
Funding: This research received no external funding.
Acknowledgments: Although there was no direct funding for this work, R.J.H was logistically supported by the
University of Queensland International PhD research scholarship award. The authors would like to give a big
thanks to all image copyright owners; Rachel Scott, Niels Sloth, Neil Hepworth, David Harasti, and Martin
Taylor who gave permission to use their excellent photography in this review. We would also like to thank Kevin
Arbuckle for editing this special issue and the reviewers for their comments to further improve the manuscript.
Conflicts of Interest: The authors declare no conflict of interest.
Toxins 2019, 11, 60 15 of 21
1. Fry, B.G.; Roelants, K.; Champagne, D.E.; Scheib, H.; Tyndall, J.D.; King, G.F.; Nevalainen, T.J.; Norman,
J.A.; Lewis, R.J.; Norton, R.S. The toxicogenomic multiverse: Convergent recruitment of proteins into
animal venoms. Ann. Rev. Genom. Human Genet. 2009, 10, 483–511.
2. Casewell, N.R.; Wüster, W.; Vonk, F.J.; Harrison, R.A.; Fry, B.G. Complex cocktails: The evolutionary
novelty of venoms. Trends Ecol. Evol. 2013, 28, 219–229.
3. Harris, R.J.; Arbuckle, K. Tempo and mode of the evolution of venom and poison in tetrapods. Toxins 2016,
8, 193.
4. Dutertre, S.; Jin, A.-h.; Kaas, Q.; Jones, A.; Alewood, P.F.; Lewis, R.J. Deep venomics reveals the mechanism
for expanded peptide diversity in cone snail venom. Mol. Cell. Proteom. 2013, 12, 312–329.
5. Dutertre, S.; Jin, A.-H.; Vetter, I.; Hamilton, B.; Sunagar, K.; Lavergne, V.; Dutertre, V.; Fry, B.G.; Antunes,
A.; Venter, D.J. Evolution of separate predation-and defence-evoked venoms in carnivorous cone snails.
Nat. Commun. 2014, 5, 3521.
6. Vetter, I.; J Lewis, R. Therapeutic potential of cone snail venom peptides (conopeptides). Curr. Top. Med.
Chem. 2012, 12, 1546–1552.
7. Fry, B.G.; Vidal, N.; Norman, J.A.; Vonk, F.J.; Scheib, H.; Ramjan, S.F.R.; Kuruppu, S.; Fung, K.; Blair
Hedges, S.; Richardson, M.K.; et al. Early evolution of the venom system in lizards and snakes. Nature 2005,
439, 584.
8. Clark, A.M. Natural Products as a Resource for New Drugs. Pharm. Res. 1996, 13, 1133–1141.
9. Fernandez, J.H.; Neshich, G.; Camargo, A.C.M. Using bradykinin-potentiating peptide structures to
develop new antihypertensive drugs. Genet. Mol. Res. 2004, 3, 554–563.
10. Triplitt, C.; Chiquette, E. Exenatide: From the Gila monster to the pharmacy. J. Am. Pharm. Assoc. 2006, 46,
11. Ziegman, R.; Alewood, P. Bioactive components in fish venoms. Toxins 2015, 7, 1497–1531.
12. Smith, W.L.; Stern, J.H.; Girard, M.G.; Davis, M.P. Evolution of Venomous Cartilaginous and Ray-Finned Fishes;
Oxford University Press: Oxford, UK, 2016.
13. Smith, W.L.; Wheeler, W.C. Venom evolution widespread in fishes: A phylogenetic road map for the
bioprospecting of piscine venoms. J. Hered. 2006, 97, 206–217.
14. Li, B.; Gou, M.; Han, J.; Yuan, X.; Li, Y.; Li, T.; Jiang, Q.; Xiao, R.; Li, Q. Proteomic analysis of buccal gland
secretion from fasting and feeding lampreys (Lampetra morii). Proteome Sci. 2018, 16, 9.
15. Wright, J.J. Diversity, phylogenetic distribution, and origins of venomous catfishes. BMC Evol. Biol. 2009,
9, 282.
16. Revell, L.J. phytools: An R package for phylogenetic comparative biology (and other things). Methods Ecol.
Evol. 2012, 3, 217–223.
17. Casewell, N.R.; Visser, J.C.; Baumann, K.; Dobson, J.; Han, H.; Kuruppu, S.; Morgan, M.; Romilio, A.;
Weisbecker, V.; Mardon, K. The evolution of fangs, venom, and mimicry systems in blenny fishes. Curr.
Biol. 2017, 27, 1184–1191.
18. Baumann, K.; Casewell, N.R.; Ali, S.A.; Jackson, T.N.; Vetter, I.; Dobson, J.S.; Cutmore, S.C.; Nouwens, A.;
Lavergne, V.; Fry, B.G. A ray of venom: Combined proteomic and transcriptomic investigation of fish
venom composition using barb tissue from the blue-spotted stingray (Neotrygon kuhlii). J. Proteom. 2014,
109, 188–198.
19. Han, H.; Baumann, K.; Casewell, N.R.; Ali, S.A.; Dobson, J.; Koludarov, I.; Debono, J.; Cutmore, S.C.;
Rajapakse, N.W.; Jackson, T.N. The cardiovascular and neurotoxic effects of the venoms of six bony and
cartilaginous fish species. Toxins 2017, 9, 67.
20. Borges, M.H.; Andrich, F.; Lemos, P.H.; Soares, T.G.; Menezes, T.N.; Campos, F.V.; Neves, L.X.; Castro-
Borges, W.; Figueiredo, S.G. Combined proteomic and functional analysis reveals rich sources of protein
diversity in skin mucus and venom from the Scorpaena plumieri fish. J. Proteom. 2018, 187, 200–211.
21. Malacarne, P.F.; Menezes, T.N.; Martins, C.W.; Naumann, G.B.; Gomes, H.L.; Pires, R.G.; Figueiredo, S.G.;
Campos, F.V. Advances in the characterization of the Scorpaena plumieri cytolytic toxin (Sp-CTx). Toxicon
22. Endler, J.A. Defense against predators. In Predator-Prey Relationships: Perspectives and Approaches from the
Study in Lower Vertebrates; Feder, M.E., Lauder, G.V., Ed.; University of Chicago Press: Chicago, IL, USA,
23. Endler, J.A. Interactions between predator and prey. Behav. Ecol. 1991, 169–196.
Toxins 2019, 11, 60 16 of 21
24. Dawkins, R.; Krebs, J.R. Arms races between and within species. Proc. R. Soc. Lond. B 1979, 205, 489–511.
25. Van Valen, L. A new evolutionary law. Evol. Theory 1973, 1, 1–30.
26. Holding, M.L.; Biardi, J.E.; Gibbs, H.L. Coevolution of venom function and venom resistance in a
rattlesnake predator and its squirrel prey. Proc. R. Soc. B 2016, 283, 20152841.
27. Margres, M.J.; Wray, K.P.; Hassinger, A.T.B.; Ward, M.J.; McGivern, J.J.; Moriarty Lemmon, E.; Lemmon,
A.R.; Rokyta, D.R. Quantity, Not Quality: Rapid Adaptation in a Polygenic Trait Proceeded Exclusively
through Expression Differentiation. Mol. Biol. Evol. 2017, 34, 3099–3110, doi:10.1093/molbev/msx231.
28. Brodie Jr, E.; Formanowicz Jr, D.; Brodie, E., III. Predator avoidance and antipredator mechanisms: Distinct
pathways to survival. Ethol. Ecol. Evol. 1991, 3, 73–77.
29. Nelsen, D.R.; Nisani, Z.; Cooper, A.M.; Fox, G.A.; Gren, E.C.; Corbit, A.G.; Hayes, W.K. Poisons, toxungens,
and venoms: Redefining and classifying toxic biological secretions and the organisms that employ them.
Biol. Rev. 2014, 89, 450–465.
30. Wüster, W.; Allum, C.S.; Bjargardóttir, I.B.; Bailey, K.L.; Dawson, K.J.; Guenioui, J.; Lewis, J.; McGurk, J.;
Moore, A.G.; Niskanen, M. Do aposematism and Batesian mimicry require bright colours? A test, using
European viper markings. Proc. R. Soc. Lond. B: Biol. Sci. 2004, 271, 2495–2499.
31. Mappes, J.; Marples, N.; Endler, J.A. The complex business of survival by aposematism. Trends Ecol. Evol.
2005, 20, 598–603.
32. Speed, M.P.; Ruxton, G.D. Warning displays in spiny animals: One (more) evolutionary route to
aposematism. Evolution 2005, 59, 2499–2508.
33. McCue, M.D. Cost of producing venom in three North American pitviper species. Copeia 2006, 2006, 818–
34. Morgenstern, D.; King, G.F. The venom optimization hypothesis revisited. Toxicon 2013, 63, 120–128.
35. Arbuckle, K.; de la Vega, R.C.R.; Casewell, N.R. Coevolution takes the sting out of it: Evolutionary biology
and mechanisms of toxin resistance in animals. Toxicon 2017, 140, 118–131.
36. Barlow, A.; Pook, C.E.; Harrison, R.A.; Wüster, W. Coevolution of diet and prey-specific venom activity
supports the role of selection in snake venom evolution. Proc. R. Soc. Lond. B: Biol. Sci. 2009, 276, 2443–2449.
37. Boyer, L.; Alagón, A.; Fry, B.; Jackson, T.; Sunagar, K.; Chippaux, J. Signs, symptoms and treatment of
envenomation. Venom. Reptil. Their Toxins: Evol. Pathophysiol. Biodiscovery 2015, 32–60.
38. Inceoglu, B.; Lango, J.; Jing, J.; Chen, L.; Doymaz, F.; Pessah, I.N.; Hammock, B.D. One scorpion, two
venoms: Prevenom of Parabuthus transvaalicus acts as an alternative type of venom with distinct
mechanism of action. Proc. Natl. Acad. Sci. USA 2003, 100, 922–927.
39. Whittington, C.M.; Papenfuss, A.T.; Bansal, P.; Torres, A.M.; Wong, E.S.; Deakin, J.E.; Graves, T.; Alsop, A.;
Schatzkamer, K.; Kremitzki, C. Defensins and the convergent evolution of platypus and reptile venom
genes. Genome Res. 2008, 18, 986–994.
40. Sismour, E.N.; Nellis, S.C.; Newton, S.H.; Mays, D.A.; Fine, M.L. An experimental study of consumption of
channel catfish Ictalurus punctatus by largemouth bass Micropterus salmoides when alternative prey are
available. Copeia 2013, 2013, 277–283.
41. Wright, J.J. Adaptive significance of venom glands in the tadpole madtom Noturus gyrinus (Siluriformes:
Ictaluridae). J. Exp. Biol. 2012, 215, 1816–1823.
42. Margres, M.J.; Wray, K.P.; Seavy, M.; McGivern, J.J.; Sanader, D.; Rokyta, D.R. Phenotypic integration in
the feeding system of the eastern diamondback rattlesnake (Crotalus adamanteus). Mol. Ecol. 2015, 24,
43. Strickland, J.L.; Smith, C.F.; Mason, A.J.; Schield, D.R.; Borja, M.; Castañeda-Gaytán, G.; Spencer, C.L.;
Smith, L.L.; Trápaga, A.; Bouzid, N.M. Evidence for divergent patterns of local selection driving venom
variation in Mojave Rattlesnakes (Crotalus scutulatus). Sci. Rep. 2018, 8, 17622.
44. Cameron, A.M.; Endean, R. Epidermal secretions and the evolution of venom glands in fishes. Toxicon 1973,
11, 401–410.
45. Colorni, A.; Ullal, A.; Heinisch, G.; Noga, E. Activity of the antimicrobial polypeptide piscidin 2 against
fish ectoparasites. J. Fish Dis. 2008, 31, 423–432.
46. Rajanbabu, V.; Chen, J.-Y. Applications of antimicrobial peptides from fish and perspectives for the future.
Peptides 2011, 32, 415–420.
47. Ángeles Esteban, M. An overview of the immunological defenses in fish skin. ISRN Immunol. 2012,
Toxins 2019, 11, 60 17 of 21
48. Ellisdon, A.M.; Reboul, C.F.; Panjikar, S.; Huynh, K.; Oellig, C.A.; Winter, K.L.; Dunstone, M.A.; Hodgson,
W.C.; Seymour, J.; Dearden, P.K. Stonefish toxin defines an ancient branch of the perforin-like superfamily.
Proc. Natl. Acad. Sci. USA 2015, 112, 15360–15365.
49. Gratzer, B.; Millesi, E.; Walzl, M.; Herler, J. Skin toxins in coral-associated G obiodon species (T eleostei: G
obiidae) affect predator preference and prey survival. Mar. Ecol. 2015, 36, 67–76.
50. Schubert, M.; Munday, P.L.; Caley, M.J.; Jones, G.P.; Llewellyn, L.E. The toxicity of skin secretions from
coral-dwelling gobies and their potential role as a predator deterrent. Environ. Biol. Fishes 2003, 67, 359–367.
51. Junqueira, M.E.P.; Grund, L.Z.; Orii, N.M.; Saraiva, T.C.; de Magalhães Lopes, C.A.; Lima, C.; Lopes-
Ferreira, M. Analysis of the inflammatory reaction induced by the catfish (Cathorops spixii) venoms.
Toxicon 2007, 49, 909–919.
52. Monteiro-dos-Santos, J.; Conceição, K.; Seibert, C.S.; Marques, E.E.; Silva Jr, P.I.; Soares, A.B.; Lima, C.;
Lopes-Ferreira, M. Studies on pharmacological properties of mucus and sting venom of Potamotrygon cf.
henlei. Int. Immunopharmacol. 2011, 11, 1368–1377.
53. Ramos, A.D.; Conceição, K.; Silva, P.I., Jr.; Richardson, M.; Lima, C.; Lopes-Ferreira, M. Specialization of
the sting venom and skin mucus of Cathorops spixii reveals functional diversification of the toxins. Toxicon
2012, 59, 651–665.
54. Baracchi, D.; Francese, S.; Turillazzi, S. Beyond the antipredatory defence: Honey bee venom function as a
component of social immunity. Toxicon 2011, 58, 550–557.
55. Grow, N.B.; Nekaris, K. Does toxic defence in Nycticebus spp. relate to ectoparasites? The lethal effects of
slow loris venom on arthropods. Toxicon 2015, 95, 1–5.
56. Lopes-Ferreira, M.; Ramos, A.D.; Martins, I.A.; Lima, C.; Conceição, K.; Haddad, V., Jr. Clinical
manifestations and experimental studies on the spine extract of the toadfish Porichthys porosissimus.
Toxicon 2014, 86, 28–39.
57. Jared, C.; Mailho-Fontana, Pedro L.; Antoniazzi, Marta M.; Mendes, Vanessa A.; Barbaro, Katia C.;
Rodrigues, Miguel T.; Brodie, Edmund D. Venomous Frogs Use Heads as Weapons. Curr. Biol. 2015, 25,
58. Mangoni, M.L.; Rinaldi, A.C.; Di Giulio, A.; Mignogna, G.; Bozzi, A.; Barra, D.; Simmaco, M. Structure–
function relationships of temporins, small antimicrobialpeptides from amphibian skin. Eur. J. Biochem.
2000, 267, 1447–1454.
59. Rinaldi, A.C. Antimicrobial peptides from amphibian skin: An expanding scenario: Commentary. Curr.
Opin. Chem. Biol. 2002, 6, 799–804.
60. Paxton, J.R.; Eschmeyer, W.N.; Kirshner, D. Encyclopedia of Fishes; Academic Press: San Diego, CA, USA,
61. Mumby, P.J.; Harborne, A.R.; Brumbaugh, D.R. Grouper as a natural biocontrol of invasive lionfish. PLoS
ONE 2011, 6, e21510.
62. Ruxton, G.D.; Sherratt, T.N.; Speed, M.P.; Speed, M.P.; Speed, M. Avoiding Attack: The Evolutionary Ecology
of Crypsis, Warning Signals and Mimicry; Oxford University Press: Oxford, UK, 2004.
63. Chuang, P.-S.; Shiao, J.-C. Toxin gene determination and evolution in scorpaenoid fish. Toxicon 2014, 88,
64. Hundt, P.J.; Nakamura, Y.; Yamaoka, K. Diet of combtooth blennies (Blenniidae) in Kochi and Okinawa,
Japan. Ichthyol. Res. 2014, 61, 76–82.
65. Baxter, E.W. Observations on the Buccal Glands of Lampreys (Petromyzonidae). Proc. Zool. Soc. Lond. 1956,
127, 95–118.
66. Dayton, P.; Hessler, R. In Role of Biological Disturbance in Maintaining Diversity in the Deep Sea; Deep Sea
Research and Oceanographic Abstracts; Elsevier: Amsterdam, The Netherlands, 1972; pp. 199–208.
67. Ribeiro, J. Role of saliva in blood-feeding by arthropods. Ann. Rev. Entomol. 1987, 32, 463–478.
68. Apitz-Castro, R.; Beguin, S.; Tablante, A.; Bartoli, F.; Holt, J.C.; Hemker, H.C. Purification and partial
characterization of draculin, the anticoagulant factor present in the saliva of vampire bats (Desmodus
rotundus). Thromb. Haemost. 1995, 73, 094–100.
69. Francischetti, I.M. Platelet aggregation inhibitors from hematophagous animals. Toxicon 2010, 56, 1130–
70. Gage, S.H.; Gage-Day, M. The anti-coagulating action of the secretion of the buccal glands of the lampreys
(Petromyzon, Lampetra and Entosphenus). Science 1927, 66, 282–284.
Toxins 2019, 11, 60 18 of 21
71. Ito, N.; Mita, M.; Takahashi, Y.; Matsushima, A.; Watanabe, Y.G.; Hirano, S.; Odani, S. Novel cysteine-rich
secretory protein in the buccal gland secretion of the parasitic lamprey, Lethenteron japonicum. Biochem.
Biophys. Res. Commun. 2007, 358, 35–40.
72. Meckley, T.D.; Wagner, C.M.; Gurarie, E. Coastal movements of migrating sea lamprey (Petromyzon
marinus) in response to a partial pheromone added to river water: Implications for management of invasive
populations. Can. J. Fish. Aquat. Sci. 2014, 71, 533–544.
73. Waldman, J.; Grunwald, C.; Wirgin, I. Sea lamprey Petromyzon marinus: An exception to the rule of
homing in anadromous fishes. Biol. Lett. 2008, 4, 659–662.
74. Silva, S.; Araújo, M.J.; Bao, M.; Mucientes, G.; Cobo, F. The haematophagous feeding stage of anadromous
populations of sea lamprey Petromyzon marinus: Low host selectivity and wide range of habitats.
Hydrobiologia 2014, 734, 187–199.
75. Bergstedt, R.A.; Seelye, J.G. Evidence for Lack of Homing by Sea Lampreys. Trans. Am. Fish. Soc. 1995, 124,
76. Buchheim, J.R.; Hixon, M.A. Competition for shelter holes in the coral-reef fish Acanthemblemaria spinosa
Metzelaar. J. Exp. Mar. Biol. Ecol. 1992, 164, 45–54.
77. Koppel, V.H. Habitat selection and space partitioning among two Mediterranean blenniid species. Mar.
Ecol. 1988, 9, 329–346.
78. Stephens Jr, J.S.; Johnson, R.K.; Key, G.S.; McCosker, J.E. The comparative ecology of three sympatric
species of California blennies of the genus Hypsoblennius Gill (Teleostomi, Blenniidae). Ecol. Monogr. 1970,
40, 213–233.
79. Enzor, L.; Wilborn, R.; Bennett, W. Toxicity and metabolic costs of the Atlantic stingray (Dasyatis sabina)
venom delivery system in relation to its role in life history. J. Exp. Mar. Biol. Ecol. 2011, 409, 235–239.
80. Hughes, R.; Pedersen, K.; Huskey, S. The kinematics of envenomation by the yellow stingray, Urobatis
jamaicensis. Zoomorphology 2018, 1–10.
81. Cott, H.B. Adaptive Coloration in Animals; Methuen: London, UK, 1940.
82. Lewis, D.B. Studies of the biology of the lesser weever fish Trachinus vipera Cuvier: I. Adaptations to a
benthic habit. J. Fish Biol. 1976, 8, 127–138.
83. Inbar, M.; Lev-Yadun, S. Conspicuous and aposematic spines in the animal kingdom. Naturwissenschaften
2005, 92, 170–172.
84. Kauppinen, J.; Mappes, J. Why are wasps so intimidating: Field experiments on hunting dragonflies
(Odonata: Aeshna grandis). Anim. Behav. 2003, 66, 505–511.
85. Schuler, W.; Hesse, E. On the function of warning coloration: A black and yellow pattern inhibits prey-
attack by naive domestic chicks. Behav. Ecol. Sociobiol. 1985, 16, 249–255.
86. Noonan, B.P.; Comeault, A.A. The role of predator selection on polymorphic aposematic poison frogs. Biol.
Lett. 2009, 5, 51–54.
87. Hoese, F.; Law, E.; Rao, D.; Herberstein, M. Distinctive yellow bands on a sit-and-wait predator: Prey
attractant or camouflage? Behaviour 2006, 143, 763–781.
88. Iniesta, L.F.; Ratton, P.; Guerra, T.J. Avian predators avoid attacking artificial aposematic millipedes in
Brazilian Atlantic Forest. J. Trop. Ecol. 2017, 33, 89–93.
89. Hughes, A.E.; Troscianko, J.; Stevens, M. Motion dazzle and the effects of target patterning on capture
success. BMC Evol. Biol. 2014, 14, 201.
90. Stevens, M.; Searle, W.T.L.; Seymour, J.E.; Marshall, K.L.; Ruxton, G.D. Motion dazzle and camouflage as
distinct anti-predator defenses. BMC Biol. 2011, 9, 81.
91. Dolenska, M.; Nedved, O.; Vesely, P.; Tesarova, M.; Fuchs, R. What constitutes optical warning signals of
ladybirds (Coleoptera: Coccinellidae) towards bird predators: Colour, pattern or general look? Biol. J. Linn.
Soc. 2009, 98, 234–242.
92. Mäthger, L.M.; Bell, G.R.; Kuzirian, A.M.; Allen, J.J.; Hanlon, R.T. How does the blue-ringed octopus
(Hapalochlaena lunulata) flash its blue rings? J. Exp. Biol. 2012, 215, 3752–3757.
93. Cronin, T.W.; Marshall, N.J.; Caldwell, R.L. Spectral tuning and the visual ecology of mantis shrimps.
Philos. Trans. R. Soc. Lond. B Biol. Sci. 2000, 355, 1263–1267.
94. Gačić, Z.; Damjanović, I.; Mićković, B.; Hegediš, A.; Nikčević, M. Spectral sensitivity of the dogfish shark
(Scyliorhinus canicula). Fish Physiol. Biochem. 2007, 33, 21.
Toxins 2019, 11, 60 19 of 21
95. Hart, N.S. Microspectrophotometry of visual pigments and oil droplets in a marine bird, the wedge-tailed
shearwater Puffinus pacificus: Topographic variations in photoreceptor spectral characteristics. J. Exp. Biol.
2004, 207, 1229–1240.
96. Levenson, D.H.; Ponganis, P.J.; Crognale, M.A.; Deegan, J.F.; Dizon, A.; Jacobs, G.H. Visual pigments of
marine carnivores: Pinnipeds, polar bear, and sea otter. J. Comp. Physiolo. A 2006, 192, 833–843.
97. Nisani, Z.; Dunbar, S.G.; Hayes, W.K. Cost of venom regeneration in Parabuthus transvaalicus (Arachnida:
Buthidae). Comp. Biochem. Physiol. Part A Mol. Integr. Physiol. 2007, 147, 509–513.
98. Arbuckle, K.; Speed, M.P. Antipredator defenses predict diversification rates. Proc. Natl. Acad. Sci. USA
2015, 112, 13597–13602.
99. Speed, M.P.; Franks, D.W. Antagonistic evolution in an aposematic predator–prey signaling system.
Evolution 2014, 68, 2996–3007.
100. Skelhorn, J.; Halpin, C.G.; Rowe, C. Learning about aposematic prey. Behav. Ecol. 2016, 27, 955–964.
101. Pasteur, G. A classificatory review of mimicry systems. Ann. Rev. Ecol. Syst. 1982, 13, 169–199.
102. Sheppard, P. The Evolution of Mimicry; a Problem in Ecology and Genetics; Cold Spring Harbor Symposia on
Quantitative Biology; Cold Spring Harbor Laboratory Press: Woodbury, NY, USA,1959; pp. 131–140.
103. Alexandrou, M.A.; Oliveira, C.; Maillard, M.; McGill, R.A.; Newton, J.; Creer, S.; Taylor, M.I. Competition
and phylogeny determine community structure in Müllerian co-mimics. Nature 2011, 469, 84.
104. Greene, H.W.; McDiarmid, R.W. Coral snake mimicry: Does it occur? Science 1981, 213, 1207–1212.
105. Caley, J.M.; Schluter, D. Predators favour mimicry in a tropical reef fish. Proc. R. Soc. Lond. Ser. B Biol. Sci.
2003, 270, 667–672.
106. Cheney, K.L. Multiple selective pressures apply to a coral reef fish mimic: A case of Batesian–aggressive
mimicry. Proc. R. Soc. Lond. Ser. B Biol. Sci. 2010, 277, 1849–1855.
107. Fujisawa, M.; Sakai, Y.; Kuwamura, T. Aggressive mimicry of the cleaner wrasse by Aspidontus taeniatus
functions mainly for small blennies. Ethology 2018, 124, 432–439.
108. Cheney, K.L.; Côté, I.M. Frequency-dependent success of aggressive mimics in a cleaning symbiosis. Proc.
R. Soc. Lond. Ser. B Biol. Sci. 2005, 272, 2635–2639.
109. Rowland, H.M.; Ihalainen, E.; Lindström, L.; Mappes, J.; Speed, M.P. Co-mimics have a mutualistic
relationship despite unequal defences. Nature 2007, 448, 64.
110. Rowland, H.M.; Mappes, J.; Ruxton, G.D.; Speed, M.P. Mimicry between unequally defended prey can be
parasitic: Evidence for quasi-Batesian mimicry. Ecol. Lett. 2010, 13, 1494–1502.
111. Taylor, M.I. Evolution: Fangtastic Venoms Underpin Parasitic Mimicry. Curr. Biol. 2017, 27, R295–R298.
112. Wright, J.J. Conservative coevolution of Müllerian mimicry in a group of rift lake catfish. Evolution 2011,
65, 395–407.
113. Marek, P.E.; Bond, J.E. A Müllerian mimicry ring in Appalachian millipedes. Proc. Natl. Acad. Sci. USA
2009, 106, 9755–9760.
114. Symula, R.; Schulte, R.; Summers, K. Molecular phylogenetic evidence for a mimetic radiation in Peruvian
poison frogs supports a Müllerian mimicry hypothesis. Proc. R. Soc. Lond. Ser. B Biol. Sci. 2001, 268, 2415–
115. Balogh, A.C.; Gamberale-Stille, G.; Leimar, O. Learning and the mimicry spectrum: From quasi-Bates to
super-Müller. Anim. Behav. 2008, 76, 1591–1599.
116. Currier, R.B.; Calvete, J.J.; Sanz, L.; Harrison, R.A.; Rowley, P.D.; Wagstaff, S.C. Unusual stability of
messenger RNA in snake venom reveals gene expression dynamics of venom replenishment. PLoS ONE
2012, 7, e41888.
117. Nisani, Z.; Boskovic, D.S.; Dunbar, S.G.; Kelln, W.; Hayes, W.K. Investigating the chemical profile of
regenerated scorpion (Parabuthus transvaalicus) venom in relation to metabolic cost and toxicity. Toxicon
2012, 60, 315–323.
118. Saggiomo, S.L.; Zelenka, C.; Seymour, J. Relationship between food and venom production in the estuarine
stonefish Synanceia horrida. Toxicon 2017, 125, 19–23.
119. Fu, S.-J.; Zeng, L.-Q.; Li, X.-M.; Pang, X.; Cao, Z.-D.; Peng, J.-L.; Wang, Y.-X. The behavioural, digestive and
metabolic characteristics of fishes with different foraging strategies. J. Exp. Biol. 2009, 212, 2296–2302.
120. Nisani, Z.; Hayes, W.K. Defensive stinging by Parabuthus transvaalicus scorpions: Risk assessment and
venom metering. Anim. Behav. 2011, 81, 627–633.
121. Young, B.A.; Zahn, K. Venom flow in rattlesnakes: Mechanics and metering. J. Exp. Biol. 2001, 204, 4345–
Toxins 2019, 11, 60 20 of 21
122. Amorim, F.G.; Costa, T.R.; Baiwir, D.; De Pauw, E.; Quinton, L.; Sampaio, S.V. Proteopeptidomic,
Functional and Immunoreactivity Characterization of Bothrops moojeni Snake Venom: Influence of Snake
Gender on Venom Composition. Toxins 2018, 10, 177.
123. Lopes-Ferreira, M.; Sosa-Rosales, I.; Bruni, F.M.; Ramos, A.D.; Portaro, F.C.V.; Conceição, K.; Lima, C.
Analysis of the intersexual variation in Thalassophryne maculosa fish venoms. Toxicon 2016, 115, 70–80.
124. Ward, M.J.; Ellsworth, S.A.; Hogan, M.P.; Nystrom, G.S.; Martinez, P.; Budhdeo, A.; Zelaya, R.; Perez, A.;
Powell, B.; He, H. Female-biased population divergence in the venom of the Hentz striped scorpion
(Centruroides hentzi). Toxicon 2018, 152, 137–149.
125. Zobel-Thropp, P.A.; Bulger, E.A.; Cordes, M.H.; Binford, G.J.; Gillespie, R.G.; Brewer, M.S. Sexually
dimorphic venom proteins in long-jawed orb-weaving spiders (Tetragnatha) comprise novel gene families.
PeerJ 2018, 6, e4691.
126. Gross, M.R.; Sargent, R.C. The evolution of male and female parental care in fishes. Am. Zool. 1985, 25, 807–
127. Hoffman, S.G.; Robertson, D.R. Foraging and reproduction of two Caribbean reef toadfishes
(Batrachoididae). Bull. Mar. Sci. 1983, 33, 919–927.
128. Herzig, V.; Ward, R.J.; dos Santos, W.F. Intersexual variations in the venom of the Brazilian ‘armed’spider
Phoneutria nigriventer (Keyserling, 1891). Toxicon 2002, 40, 1399–1406.
129. Ehrlich, P.R.; Raven, P.H. Butterflies and plants: A study in coevolution. Evolution 1964, 18, 586–608.
130. Arbuckle, K.; Brockhurst, M.; Speed, M.P. Does chemical defence increase niche space? A phylogenetic
comparative analysis of the Musteloidea. Evol. Ecol. 2013, 27, 863–881.
131. Hodge, J.R.; Alim, C.; Bertrand, N.G.; Lee, W.; Price, S.A.; Tran, B.; Wainwright, P.C. Ecology shapes the
evolutionary trade-off between predator avoidance and defence in coral reef butterflyfishes. Ecol. Lett. 2018.
132. Layman, C.A.; Allgeier, J.E. Characterizing trophic ecology of generalist consumers: A case study of the
invasive lionfish in The Bahamas. Mar. Ecol. Prog. Ser. 2012, 448, 131–141.
133. Betancur-R, R.; Hines, A.; Acero P, A.; Ortí, G.; Wilbur, A.E.; Freshwater, D.W. Reconstructing the lionfish
invasion: Insights into Greater Caribbean biogeography. J. Biogeogr. 2011, 38, 1281–1293.
134. Cure, K.; Benkwitt, C.E.; Kindinger, T.L.; Pickering, E.A.; Pusack, T.J.; McIlwain, J.L.; Hixon, M.A.
Comparative behavior of red lionfish Pterois volitans on native Pacific versus invaded Atlantic coral reefs.
Mar. Ecol. Prog. Ser. 2012, 467, 181–192.
135. Phillips, B.L.; Brown, G.P.; Webb, J.K.; Shine, R. Invasion and the evolution of speed in toads. Nature 2006,
439, 803.
136. Daltry, J.C.; Wüster, W.; Thorpe, R.S. Diet and snake venom evolution. Nature 1996, 379, 537.
137. Prator, C.A.; Murayama, K.M.; Schulz, J.R. Venom variation during prey capture by the cone snail, Conus
textile. PLoS ONE 2014, 9, e98991.
138. Losey, G.S. Predation protection in the poison-fang blenny, Meiacanthus atrodorsalis, and its mimics,
Ecsenius bicolor and Runula laudandus (Blenniidae). Pac. Sci. 1972, 26, 129–139.
139. Li, M.; Fry, B.; Kini, R.M. Eggs-only diet: Its implications for the toxin profile changes and ecology of the
marbled sea snake (Aipysurus eydouxii). J. Mol. Evol. 2005, 60, 81–89.
140. Li, M.; Fry, B.G.; Kini, R.M. Putting the brakes on snake venom evolution: The unique molecular
evolutionary patterns of Aipysurus eydouxii (Marbled sea snake) phospholipase A2 toxins. Mol. Biol. Evol.
2005, 22, 934–941.
141. Santos, J.C.; Cannatella, D.C. Phenotypic integration emerges from aposematism and scale in poison frogs.
Proc. Natl. Acad. Sci. USA 2011, 108, 6175–6180.
142. Bosher, B.T.; Newton, S.H.; Fine, M.L. The spines of the channel catfish, Ictalurus punctatus, as an anti-
predator adaptation: An experimental study. Ethology 2006, 112, 188–195.
143. Hossie, T.; Hassall, C.; Knee, W.; Sherratt, T. Species with a chemical defence, but not chemical offence, live
longer. J. Evol. Biol. 2013, 26, 1598–1602.
144. Blanco, M.A.; Sherman, P.W. Maximum longevities of chemically protected and non-protected fishes,
reptiles, and amphibians support evolutionary hypotheses of aging. Mech. Ageing Dev. 2005, 126, 794–803.
145. Blount, J.D.; Speed, M.P.; Ruxton, G.D.; Stephens, P.A. Warning displays may function as honest signals of
toxicity. Proc. R. Soc. Lond. B Biol. Sci. 2009, 276, 871–877.
146. Arbuckle, K. Phylogenetic Comparative Methods can Provide Important Insights into the Evolution of
Toxic Weaponry. Toxins 2018, 10, 518.
Toxins 2019, 11, 60 21 of 21
147. Liu, S.-Y. V.; Frederich, B.; Lavoué, S.; Chang, J.; Erdmann, M.V.; Mahardika, G.N.; Barber, P.H. Buccal
venom gland associates with increased of diversification rate in the fang blenny fish Meiacanthus
(Blenniidae; Teleostei). Mol. Phylogenet. Evol. 2018, 125, 138–146.
148. Blanchard, B.D.; Moreau, C.S. Defensive traits exhibit an evolutionary trade-off and drive diversification
in ants. Evolution 2017, 71, 315–328.
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... Pre-vertebrates and jawless fishes (hagfishes, Myxinidae) deploy a noxious slime that smothers the gills and suffocates would-be predators (Zintzen et al., 2011). Venom is observed in at least 58 fish families and serves both predatory and anti-predatory functions (Smith et al., 2016;Harris and Jenner, 2019). In some species, modified fin and body spines form hypodermic needles capable of injecting venom into predators (Harris and Jenner, 2019). ...
... Venom is observed in at least 58 fish families and serves both predatory and anti-predatory functions (Smith et al., 2016;Harris and Jenner, 2019). In some species, modified fin and body spines form hypodermic needles capable of injecting venom into predators (Harris and Jenner, 2019). This defense is hypothesized to contribute to lionfishes' (Pterois miles and Pterois volitans) ( Figure 1G) wide niche breadth and P. volitan's expansive range and success as an invasive species (Harris and Jenner, 2019). ...
... In some species, modified fin and body spines form hypodermic needles capable of injecting venom into predators (Harris and Jenner, 2019). This defense is hypothesized to contribute to lionfishes' (Pterois miles and Pterois volitans) ( Figure 1G) wide niche breadth and P. volitan's expansive range and success as an invasive species (Harris and Jenner, 2019). Noxious chemical defenses can take the form of ichthyotoxins which are secreted from the skin and aid in escape. ...
Full-text available
In nature, many multicellular and unicellular organisms use constitutive defenses such as armor, spines, and noxious chemicals to keep predators at bay. These defenses render the prey difficult and/or dangerous to subdue and handle, which confers a strong deterrent for predators. The distinct benefit of this mode of defense is that prey can defend in place and continue activities such as foraging even under imminent threat of predation. The same qualitative types of armor-like, spine-like, and noxious defenses have evolved independently and repeatedly in nature, and we present evidence that cancer is no exception. Cancer cells exist in environments inundated with predator-like immune cells, so the ability of cancer cells to defend in place while foraging and proliferating would clearly be advantageous. We argue that these defenses repeatedly evolve in cancers and may be among the most advanced and important adaptations of cancers. By drawing parallels between several taxa exhibiting armor-like, spine-like, and noxious defenses, we present an overview of different ways these defenses can appear and emphasize how phenotypes that appear vastly different can nevertheless have the same essential functions. This cross-taxa comparison reveals how cancer phenotypes can be interpreted as anti-predator defenses, which can facilitate therapy approaches which aim to give the predators (the immune system) the upper hand. This cross-taxa comparison is also informative for evolutionary ecology. Cancer provides an opportunity to observe how prey evolve in the context of a unique predatory threat (the immune system) and varied environments.
... Notwithstanding the proposed influences on diversification rate above, the potential role of venom in contributing to the great diversity of fishes and insects has not yet been investigated. This is despite many fishes and insects being venomous and in both groups venom is thought to have arisen multiple times independently [13,[24][25][26]. Fish venoms have evolved, with few exceptions, in a defensive role and their venoms typically cause extreme pain resulting from both direct and indirect (via cytolytic effects) toxic actions [26,27]. ...
... This is despite many fishes and insects being venomous and in both groups venom is thought to have arisen multiple times independently [13,[24][25][26]. Fish venoms have evolved, with few exceptions, in a defensive role and their venoms typically cause extreme pain resulting from both direct and indirect (via cytolytic effects) toxic actions [26,27]. Insect venoms are also commonly defensive, including the painful envenomations from clinically important groups such as social hymenopterans and lepidopterans [28,29], but in many groups function primarily in feeding [13,25]. ...
... Results shown for diversification rate based on ε = 0.5, see Additional file 1: Table S2 for equivalent model outputs for ε = 0 and ε = 0.9 Diversification rates and standard errors are based on estimated parameters from a model accounting for clade age which found that the differences shown here are statistically significant despite the relatively wide confidence intervals (Table 2) cases; for instance Blanchard and Moreau [16] found no evidence for venomous stingers being associated with faster diversification in a family of insects (Formicidae). Despite suggestions in the literature that venom may be important in the diversification patterns of fishes overall [26], our study is the first to investigate the question across the whole lineage (and that of insects). Since work on individual genera or families have yielded conflicting results, the broad-scale approach we use here represents a key advance in determining general patterns concerning the diversification of these large lineages. ...
Full-text available
Background: Understanding drivers of animal biodiversity has been a longstanding aim in evolutionary biology. Insects and fishes represent the largest lineages of invertebrates and vertebrates respectively, and consequently many ideas have been proposed to explain this diversity. Natural enemy interactions are often important in diversification dynamics, and key traits that mediate such interactions may therefore have an important role in explaining organismal diversity. Venom is one such trait which is intricately bound in antagonistic coevolution and has recently been shown to be associated with increased diversification rates in tetrapods. Despite ~ 10% of fish families and ~ 16% of insect families containing venomous species, the role that venom may play in these two superradiations remains unknown. Results: In this paper we take a broad family-level phylogenetic perspective and show that variation in diversification rates are the main cause of variations in species richness in both insects and fishes, and that venomous families have diversification rates twice as high as non-venomous families. Furthermore, we estimate that venom was present in ~ 10% and ~ 14% of the evolutionary history of fishes and insects respectively. Conclusions: Consequently, we provide evidence that venom has played a role in generating the remarkable diversity in the largest vertebrate and invertebrate radiations.
... Fish venoms are often extracted from living or frozen specimens by dissecting their venom glands. Many fishes do not have distinct venom glands but clustered, venom-producing, secretory cells that end in a spine groove [37]. For those species, protocols Downloaded from by guest on 31 May 2022 were developed in which crude venoms are extracted through a syringe or by a forced sting into a sponge contained in a tube [38,39]. ...
Full-text available
Venoms have evolved >100 times in all major animal groups, and their components, known as toxins, have been fine-tuned over millions of years into highly effective biochemical weapons. There are many outstanding questions on the evolution of toxin arsenals, such as how venom genes originate, how venom contributes to the fitness of venomous species, and which modifications at the genomic, transcriptomic, and protein level drive their evolution. These questions have received particularly little attention outside of snakes, cone snails, spiders, and scorpions. Venom compounds have further become a source of inspiration for translational research using their diverse bioactivities for various applications. We highlight here recent advances and new strategies in modern venomics and discuss how recent technological innovations and multi-omic methods dramatically improve research on venomous animals. The study of genomes and their modifications through CRISPR and knockdown technologies will increase our understanding of how toxins evolve and which functions they have in the different ontogenetic stages during the development of venomous animals. Mass spectrometry imaging combined with spatial transcriptomics, in situ hybridization techniques, and modern computer tomography gives us further insights into the spatial distribution of toxins in the venom system and the function of the venom apparatus. All these evolutionary and biological insights contribute to more efficiently identify venom compounds, which can then be synthesized or produced in adapted expression systems to test their bioactivity. Finally, we critically discuss recent agrochemical, pharmaceutical, therapeutic, and diagnostic (so-called translational) aspects of venoms from which humans benefit.
... Indeed, the efficacy of these toxins in deterring predation may have contributed to the high toad densities (Lampo & De Leo, 1998) and pronounced intraspecific competition (Crossland, Hearnden, et al., 2011) that likely favored the evolution of cannibalistic behaviors within these invasive populations (DeVore, . Although the costs of toxic defenses are often calculated in terms of how energetically expensive they are to produce (Blennerhassett et al., 2019;Enzor et al., 2011;Harris & Jenner, 2019), here we demonstrate a strong, additional cost; the utilization of this predator defense comes at the expense of increased cannibalism risk. Whether the emergence of targeted cannibalism in the invasive range will ultimately favor reduced maternal investment in egg toxicity remains an open question for future research. ...
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In many species, cannibalism is uncommon and involves nonselective consumption of conspecifics as well as heterospecifics. However, within their invasive Australian range, cane toad larvae (Rhinella marina) specifically target and voraciously consume the eggs and hatchlings of conspecifics, often extirpating entire clutches. In contrast, toad larvae rarely consume the eggs and hatchlings of native frogs. Here, we use laboratory studies to demonstrate that this selective consumption is triggered by species-specific chemical cues: maternally-invested bufadienolide toxins that otherwise defend cane toad eggs and hatchlings against predators. We find that these cues stimulate feeding behaviors in toad tadpoles, such that the addition of bufadienolide toxins to the water column increases predation on eggs, not only of conspecifics, but also of native anuran species that are otherwise usually ignored. In contrast, we find that cannibalism rates on conspecific hatchlings are high and unaffected by the addition of bufadienolide cues. The maternally-invested toxins present in conspecific eggs may therefore be more easily detected post-hatching, at which point tadpole feeding behaviors are induced whether or not additional toxin cues are present. As bufadienolide cues have previously been found to attract toad tadpoles to vulnerable hatchlings, our present findings demonstrate that the same toxin cues that attract cannibalistic tadpoles also induce them to feed, thereby facilitating cannibalism through multiple behavioral effects. Because native fauna do not produce bufadienolide toxins, the species specificity of these chemical cues in the Australian landscape may have facilitated the evolution of targeted (species-specific) cannibalism in invasive cane toad populations. Thus, these bufadienolide toxins confer cost (increased vulnerability to cannibalism in early life-stages) as well as benefit (reduced vulnerability to predation by other taxa).
... Modern sample-friendly omics approaches can help to overcome these limitations, making venoms more accessible for drug discovery. More than 30% of venomous vertebrates are fish [1], with defensive venom systems (and diverse delivery structures) arising by convergent evolution at least 19 times among 2900 species [24,25]. However, the remote habitats of these species and the typical impurity of venom samples limit our ability to test venom composition and activity. ...
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Animal venoms offer a valuable source of potent new drug leads, but their mechanisms of action are largely unknown. We therefore developed a novel network pharmacology approach based on multi-omics functional data integration to predict how stingray venom disrupts the physiological systems of target animals. We integrated 10 million transcripts from five stingray venom transcriptomes and 848,640 records from three high-content venom bioactivity datasets into a large functional data network. The network featured 216 signaling pathways, 29 of which were shared and targeted by 70 transcripts and 70 bioactivity hits. The network revealed clusters for single en-venomation outcomes, such as pain, cardiotoxicity and hemorrhage. We carried out a detailed analysis of the pain cluster representing a primary envenomation symptom, revealing bibrotoxin and cholecystotoxin-like transcripts encoding pain-inducing candidate proteins in stingray venom. The cluster also suggested that such pain-inducing toxins primarily activate the inositol-3-phosphate receptor cascade, inducing intracellular calcium release. We also found strong evidence for syner-gistic activity among these candidates, with nerve growth factors cooperating with the most abundant translationally-controlled tumor proteins to activate pain signaling pathways. Our network pharmacology approach, here applied to stingray venom, can be used as a template for drug discovery in neglected venomous species.
... Fish use their venoms mostly for defensive purposes, and the molecular composition of these venoms-combined with the evolution of strategies, such as mimicry and aposematism-reflects this fact [16]. Several bioactive compounds, including enzymes, such as hyaluronidases and proteases, large proteinaceous toxins, lectins, and peptides, among others, have been identified in fish venoms [17,18]. ...
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The majority of the effects observed upon envenomation by scorpaenoid fish species can be reproduced by the cytolysins present in their venoms. Fish cytolysins are multifunctional proteins that elicit lethal, cytolytic, cardiovascular, inflammatory, nociceptive, and neuromuscular activities, representing a novel class of protein toxins. These large proteins (MW 150–320 kDa) are composed by two different subunits, termed α and β, with about 700 amino acid residues each, being usually active in oligomeric form. There is a high degree of similarity between the primary sequences of cytolysins from different fish species. This suggests these molecules share similar mechanisms of action, which, at least regarding the cytolytic activity, has been proved to involve pore formation. Although the remaining components of fish venoms have interesting biological activities, fish cytolysins stand out because of their multifunctional nature and their ability to reproduce the main events of envenomation on their own. Considerable knowledge about fish cytolysins has been accumulated over the years, although there remains much to be unveiled. In this review, we compiled and compared the current information on the biochemical aspects and pharmacological activities of fish cytolysins, going over their structures, activities, mechanisms of action, and perspectives for the future.
... The latter finding agrees with a similar study by [5], where it was reported that the proteaserelated activities of stonefish crude venoms are probably responsible for tissue necrosis and the spread of venom toxicity. It usually consists of depolarising action (stressinducing imbalance) of cell membrane on both nerve and muscle tissues, and that their effects differ only quantitatively [25,28,29]. Based on our findings, we hypothesized the role of stonefish venom in cell signaling (ROS dependent) that might interact with the biological consequences processes. ...
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The present study utilizes coastal and environmental engineering to investigate the histopathological effects of Synanceia verrucosa venom on Albino BALB/c mice. S. verrucosa is the most hazardous venomous marine fish that belong to the family Synanceiidae, generally known as the "Reef Stonefish". Crude venom was collected from venom glands of the dorsal spines of stonefish samples taken from the Jordanian coastline of the Gulf of Aqaba, Red Sea. The mice were given intramuscular injections of the venom. Consequently, the research evaluated the acute toxicity and influence on selected serum biomarker enzymes, as well as possible histological alterations of the soleus skeletal muscles. The mice 24 h LD50 was 0.107 µg toxin/kg mouse body weight. After the treatment using venom sublethal dose, the serum biomarkers, including Lactate dehydrogenase (LDH) and Alanine aminotransferase (ALT), were significantly improved (P≤0.05). In addition, Lipid Peroxidation (LPO) contents were significantly increased (P≤0.05) after venom treatment. Moreover, we combined routine medical procedures and artificial intelligence-assisted image analysis for a rapid qualitative and quantitative diagnosis of stonefish injury, based on the histophotography of mice tissue samples during the observation period (1, 2, and 3 hours respectively). The novelty of our method is that we could detect severe and mild damage with an accuracy of 93% and 91%, respectively. The most histological abnormalities in muscles were the great variety in diameters, content, and widespread among randomly distributed muscle fibres. In addition, loss of the tissue's striated appearance was noticed in toxin-treated groups compared with the control group. Consequently, our findings indicate the Stonefish's harmful influences that may endanger human life and highlight the need for appropriate measures to be considered. This, in turn, can ensure beach safety in the Gulf of Aqaba.
... Venom may have evolved due to other demands in different groups. Self-defense has been also proposed as driver of venom evolution in fishes and wasps [157,158], intraspecific competition in venomous mammals [81], possibly mating behavior in scorpions [128,159,160] and even for an antimicrobial function in bees [161]. ...
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Scorpions possess two systems of weapons: the pincers (chelae) and the stinger (telson). These are placed on anatomically and developmentally well separated parts of the body, that is, the oral appendages and at the end of the body axis. The otherwise conserved body plan of scorpions varies most in the shape and relative dimensions of these two weapon systems, both across species and in some cases between the sexes. We review the literature on the ecological function of these two weapon systems in each of three contexts of usage: (i) predation, (ii) defense and (iii) sexual contests. In the latter context, we will also discuss their usage in mating. We first provide a comparative background for each of these contexts of usage by giving examples of other weapon systems from across the animal kingdom. Then, we discuss the pertinent aspects of the anatomy of the weapon systems, particularly those aspects relevant to their functioning in their ecological roles. The literature on the functioning and ecological role of both the chelae and the telson is discussed in detail, again organized by context of usage. Particular emphasis is given on the differences in morphology or usage between species or higher taxonomic groups, or between genders, as such cases are most insightful to understand the roles of each of the two distinct weapon systems of the scorpions and their evolutionary interactions. We aimed to synthesize the literature while minimizing conjecture, but also to point out gaps in the literature and potential future research opportunities.
... Fish toxins have been poorly studied compared to venoms from other animals such as snakes, scorpions, spiders, and cone snails (Utkin, 2015). It is estimated that there are up to 2,900 venomous fishes (Xie et al., 2017) with venom systems convergently evolved 19 times (Harris and Jenner, 2019). Mandarin fish is one of those who can produce toxins in their hard spines to help them defense and prey, and cause pain and swelling at the site of the sting in human as well (Zhang F.-B. et al., 2019). ...
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The mandarin fish, Siniperca chuatsi , is an economically important perciform species with widespread aquaculture practices in China. Its special feeding habit, acceptance of only live prey fishes, contributes to its delicious meat. However, little is currently known about related genetic mechanisms. Here, we performed whole-genome sequencing and assembled a 758.78 Mb genome assembly of the mandarin fish, with the scaffold and contig N50 values reaching 2.64 Mb and 46.11 Kb, respectively. Approximately 92.8% of the scaffolds were ordered onto 24 chromosomes (Chrs) with the assistance of a previously established genetic linkage map. The chromosome-level genome contained 19,904 protein-coding genes, of which 19,059 (95.75%) genes were functionally annotated. The special feeding behavior of mandarin fish could be attributable to the interaction of a variety of sense organs (such as vision, smell, and endocrine organs). Through comparative genomics analysis, some interesting results were found. For example, olfactory receptor (OR) genes (especially the beta and delta types) underwent a significant expansion, and endocrinology/vision related npy , spexin , and opsin genes presented various functional mutations. These may contribute to the special feeding habit of the mandarin fish by strengthening the olfactory and visual systems. Meanwhile, previously identified sex-related genes and quantitative trait locis (QTLs) were localized on the Chr14 and Chr17, respectively. 155 toxin proteins were predicted from mandarin fish genome. In summary, the high-quality genome assembly of the mandarin fish provides novel insights into the feeding habit of live prey and offers a valuable genetic resource for the quality improvement of this freshwater fish.
The origin and biogenesis of tetrodotoxin (TTX) is one of the most interesting and perplexing questions remaining for TTX researchers. Newts can possess extreme quantities of TTX and are one of the most well-studied of all TTX-bearing organisms, yet seemingly conflicting results between studies on closely related species continues to generate debate. In this study, eggs from 12 female newts (Taricha granulosa) were reared in captivity and the metamorphosed juveniles were fed a TTX-free diet for 3 years. Using a non-lethal sampling technique, we collected skin samples from each individual each year. Wild-caught juveniles from the same population were also sampled for TTX. In lab-reared juveniles, mass increased rapidly, and after only 2 years individuals approached adult body mass. TTX levels increased slowly during the first two years and then jumped considerably in year three when fed a diet free of TTX. However, wild-caught juvenile newts of unknown age were more toxic than their lab-reared counterparts. These results, coupled with additional data on the long-term production and synthesis of TTX in adult newts suggest that TTX is unlikely to come through dietary acquisition, but rather newts may be able to synthesize their own toxin or acquire it from symbiotic bacteria.
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The literature on chemical weaponry of organisms is vast and provides a rich understanding of the composition and mechanisms of the toxins and other components involved. However, an ecological or evolutionary perspective has often been lacking and is largely limited to (1) molecular evolutionary studies of particular toxins (lacking an ecological view); (2) comparisons across different species that ignore phylogenetic relatedness (lacking an evolutionary view); or (3) descriptive studies of venom composition and toxicology that contain post hoc and untested ecological or evolutionary interpretations (a common event but essentially uninformative speculation). Conveniently, comparative biologists have prolifically been developing and using a wide range of phylogenetic comparative methods that allow us to explicitly address many ecological and evolutionary questions relating to venoms and poisons. Nevertheless, these analytical tools and approaches are rarely used and poorly known by biological toxinologists and toxicologists. In this review I aim to (1) introduce phylogenetic comparative methods to the latter audience; (2) highlight the range of questions that can be addressed using them; and (3) encourage biological toxinologists and toxicologists to either seek out adequate training in comparative biology or seek collaboration with comparative biologists to reap the fruits of a powerful interdisciplinary approach to the field.
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Snake venoms represent an enriched system for investigating the evolutionary processes that lead to complex and dynamic trophic adaptations. It has long been hypothesized that natural selection may drive geographic variation in venom composition, yet previous studies have lacked the population genetic context to examine these patterns. We leverage range-wide sampling of Mojave Rattlesnakes (Crotalus scutulatus) and use a combination of venom, morphological, phylogenetic, population genetic, and environmental data to characterize the striking dichotomy of neurotoxic (Type A) and hemorrhagic (Type B) venoms throughout the range of this species. We find that three of the four previously identified major lineages within C. scutulatus possess a combination of Type A, Type B, and a ‘mixed’ Type A + B venom phenotypes, and that fixation of the two main venom phenotypes occurs on a more fine geographic scale than previously appreciated. We also find that Type A + B individuals occur in regions of inferred introgression, and that this mixed phenotype is comparatively rare. Our results support strong directional local selection leading to fixation of alternative venom phenotypes on a fine geographic scale, and are inconsistent with balancing selection to maintain both phenotypes within a single population. Our comparisons to biotic and abiotic factors further indicate that venom phenotype correlates with fang morphology and climatic variables. We hypothesize that links to fang morphology may be indicative of co-evolution of venom and other trophic adaptations, and that climatic variables may be linked to prey distributions and/or physiology, which in turn impose selection pressures on snake venoms.
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Venom has been associated with the ecological success of many groups of organisms, most notably reptiles, gastropods, and arachnids. In some cases, diversification has been directly linked to tailoring of venoms for dietary specialization. Spiders in particular are known for their diverse venoms and wide range of predatory behaviors, although there is much to learn about scales of variation in venom composition and function. The current study focuses on venom characteristics in different sexes within a species of spider. We chose the genus Tetragnatha (Tetragnathidae) because of its unusual courtship behavior involving interlocking of the venom delivering chelicerae (i.e., the jaws), and several species in the genus are already known to have sexually dimorphic venoms. Here, we use transcriptome and proteome analyses to identify venom components that are dimorphic in Tetragnatha versicolor . We present cDNA sequences including unique, male-specific high molecular weight proteins that have remote, if any, detectable similarity to known venom components in spiders or other venomous lineages and have no detectable homologs in existing databases. While the function of these proteins is not known, their presence in association with the cheliceral locking mechanism during mating together with the presence of prolonged male-male mating attempts in a related, cheliceral-locking species ( Doryonychus raptor ) lacking the dimorphism suggests potential for a role in sexual communication.
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Background Previous studies have shown that lamprey buccal glands contain some regulators related to anticoagulation, nociception, and immune responses due to the blood sucking habit. Regrettably, the protein expression profile in the buccal glands of feeding lampreys has never been reported yet. The present study was performed in order to further identify more proteins which are closely associated with lamprey feeding process. Methods 2D-PAGE, NanoLC–MS/MS with higher resolution, Ensembl lamprey and NCBI protein databases, as well as western blot was used to compare the proteomics of buccal gland secretion from China northeast lampreys (Lampetra morii) which had been fed for 0, 10, and 60 min, respectively. Results In the present study, the number of identified protein species in the buccal glands of feeding groups (60 min) was increased significantly, nearly ten times of that in the fasting group. During the feeding stage, novel proteins emerged in the buccal gland secretion of lampreys. According to gene ontology (GO) analysis and function predictions, these proteins were summarized and discussed based on their potential roles during feeding process. Furthermore, some of the identified proteins were confirmed to express during the feeding time of lampreys. Conclusion When lampreys attack host fishes to suck blood and flesh, their buccal glands could secrete enough proteins to suppress blood coagulation, nociception, oxidative stress, immune response, as well as other adverse effects encountered during their parasitic lives. The present study would provide clues to clarify the feeding mechanism of the bloodsucking lampreys. Electronic supplementary material The online version of this article (10.1186/s12953-018-0137-5) contains supplementary material, which is available to authorized users.
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Venom composition varies across snakes from all taxonomic levels and is influenced by the snakes' age, habitat, diet, and sexual dimorphism. The present study reports the first in-depth investigation of venom composition in male and female Bothrops moojeni (B. moojeni) snakes (BmooM and BmooF, respectively) through three proteomics approaches associated with functional, cytotoxic, and immunoreactivity characterization. Compared with BmooM venom, BmooF venom exhibited weaker hyaluronidase, metalloproteinase, and phospholipase activity; stronger recognition by anti-bothropic serum; 1.4-fold stronger cytotoxicity; and greater number of peptides. The increased L-amino acid oxidase expression probably accounted for the stronger immunoreactivity and cytotoxicity of BmooF venom. BmooF and BmooM venom shared only 19% peptides. Some venom components were gender-specific, such as phospholipases B, phospholipase inhibitor, and hyaluronidases in BmooM, and cysteine-rich secretory proteins in BmooF. In conclusion, we describe herein the first proteomics study of B. moojeni snake venom and an in-depth characterization of gender-specific differences in venom composition. Altogether, our findings not only stress the importance of considering the snake's gender during antivenom production, but also help to identify new potential drugs and biotechnological tools. Key Contribution: We describe herein the first proteomics study of Bothrops moojeni snake venom and an in-depth characterization of gender-specific differences in venom composition, which will help to improve the antivenom production process and identify new potential drugs and biotechnological tools.
The biological activities observed upon envenomation by Scorpaena plumieri could be linked to both the venom and the skin mucus. Through a proteomic/functional approach we analyzed protein composition and biological activities of the venom and skin mucus. We identified 885 proteins: 722 in the Venomous Apparatus extracts (Sp-VAe) and 391 in the Skin Mucus extract (Sp-SMe), with 494 found exclusively in Sp-VAe, being named S. plumieri Venom Proteins (Sp-VP), while 228 were found in both extracts. The majority of the many proteins identified were not directly related to the biological activities reported here. Nevertheless, some were classified as toxins/potentially interesting molecules: lectins, proteases and protease inhibitors were detected in both extracts, while the pore-forming toxin and hyaluronidase were associated with Sp-VP. Proteolytic and anti-microbial activities were linked to both extracts, while the main toxic activities - cardiovascular, inflammatory, hemolytic and nociceptive - were elicited only by Sp-VAe. Our study provided a clear picture on the composition of the skin mucus and the venom. We also show that the classic effects observed upon envenomation are produced by molecules from the venomous gland. Our results add to the growing catalogue of scorpaeniform fish venoms and their skin mucus proteins. Significance: In this study a large number of proteins - including classical and non-classical toxins - were identified in the venomous apparatus and the skin mucus extracts of the Scorpaena plumieri fish through shotgun proteomic approach. It was shown that the toxic effects observed upon envenomation are elicited by molecules originated from the venomous gland. These results add to the growing catalogue of scorpaeniform fish venoms and their skin mucus proteins - so scarcely explored when compared to the venoms and bioactive components of terrestrial animals. Data are available via ProteomeXchange with identifier PXD009983.
Sex-biased genes are expressed at higher levels in one sex and contribute to phenotypic differences between males and females, as well as overall phenotypic variation within and among populations. Venom has evolved primarily for predation and defense, making venom expression a highly variable phenotype as a result of local adaptation. Several scorpion species have shown both intraspecific and intersexual venom variation, and males have been observed using venom in courtship and mating, suggesting the existence of venom-specific, sex-biased genes that may contribute to population divergence. We used reversed-phase high-performance liquid chromatography (RP-HPLC), Agilent protein bioanalyzer chips, nano-liquid chromatography mass spectrometry (nLC/MS/MS), and median lethal dose (LD50) assays in fruit flies (Drosophila melanogaster) and banded crickets (Gryllodes sigillatus) to investigate proteomic and functional venom variation within and among three Florida populations of the Hentz striped scorpion (Centruroides hentzi). We found significant venom variation among populations, with females, not males, being responsible for this divergence. We also found significant variation in venom expression within populations, with males contributing more to within population variation than females. Our results provide evidence that male and female scorpions experience different natural and sexual selective pressures that have led to the expression of sex-biased venom genes and that these genes may be consequential in population divergence.
Proteins that account for the hemolytic activity found in scorpaeniform fish venoms are responsible for the majority of the effects observed upon envenomation, for instance, neurotoxic, cardiotoxic and inflammatory effects. These multifunctional toxins, described as protein lethal factors and referred to as cytolysins, are known to be extremely labile molecules. In the present work, we endeavored to overcome this constraint by determining optimal storage conditions for Sp-CTx, the major bioactive component from the scorpionfish Scorpaena plumieri venom. This cardiotoxic hemolytic cytolysin is a large dimeric glycoprotein (subunits of ≈65 kDa) with pore-forming ability. We were able to establish storage conditions that allowed us to keep the toxin partially active for up to 60 days. Stability was achieved by storing Sp-CTx at -80 and -196 °C in the presence of glycerol 10% in a pH 7.4 solution. It was demonstrated that the hemolytic activity of Sp-CTx is calcium dependent, being abolished by EDTA and zinc ions. Furthermore, the toxin exhibited its maximal hemolytic activity at pH between 8 and 9, displaying typical N- and O- linked glycoconjugated residues (galactose (1-4) N-acetylglucosamine and sialic acid (2-3) galactose in N- and/or O-glycan complexes). The hemolytic activity of Sp-CTx was inhibited by phosphatidylglycerol and phosphatidylethanolamine, suggesting a direct electrostatic interaction lipid - toxin in the pore-formation mechanism of action of this toxin. In addition, we observed that the hemolytic activity was inhibited by increasing doses of cholesterol. Finally, we were able to show, for first time, that Sp-CTx is at least partially responsible for the pain and inflammation observed upon envenomation. However, while the edema induced by Sp-CTx was reduced by pre-treatment with aprotinin and HOE-140, pointing to the involvement of the kallikrein-kinin system in this response, these drugs had no significant effect in the toxin-induced nociception. Taken together, our results could suggest that, as has been already reported for other fish cytolysins, Sp-CTx acts mostly through lipid-dependent pore formation not only in erythrocytes but also in other cell types, which could account for the pain observed upon envenomation. We believe that the present work paves the way towards the complete characterization of fish cytolysins.
Antipredator defensive traits are thought to trade‐off evolutionarily with traits that facilitate predator avoidance. However, complexity and scale have precluded tests of this prediction in many groups, including fishes. Using a macroevolutionary approach, we test this prediction in butterflyfishes, an iconic group of coral reef inhabitants with diverse social behaviours, foraging strategies and antipredator adaptations. We find that several antipredator traits have evolved adaptively, dependent primarily on foraging strategy. We identify a previously unrecognised axis of diversity in butterflyfishes where species with robust morphological defences have riskier foraging strategies and lack sociality, while species with reduced morphological defences feed in familiar territories, have adaptations for quick escapes and benefit from the vigilance provided by sociality. Furthermore, we find evidence for the constrained evolution of fin spines among species that graze solely on corals, highlighting the importance of corals, as both prey and structural refuge, in shaping fish morphology.
The mimic blenny Aspidontus taeniatus Quoy & Gaimard is well known for its resemblance to the juvenile and adult cleaner wrasse Labroides dimidiatus (Valenciennes) in colour and shape. As various reef fishes including piscivores actively approach the cleaner wrasse to solicit cleaning by posing, two types of benefits have been suggested for this resemblance, that is, protective mimicry and aggressive mimicry. In aggressive mimicry, the mimic blenny is supposed to have considerable opportunities to bite the fin of deceived fishes when they pose, but some studies have confirmed that fin biting does not seem to be the main feeding tactic in the blenny in nature. Here, we examined the feeding tactics including fin biting by the mimic blenny in relation to its body size in a field observational survey in the coral reefs of Sesoko Island, Okinawa, Japan. The blenny was observed feeding mainly on four food items: the tentacles of Christmas tree worms, the mantle edges of boring clams, the demersal eggs in damselfishes’ nests and the fins of fishes. The feeding frequency by fin biting significantly decreased with body size, while that by egg predation significantly increased with body size of the blenny. When predating on eggs, the blenny was vigorously attacked by egg‐guarding fish, but often succeeded in raiding their nests by forming a feeding group. When feeding by fin biting, the blenny attacked prey fish without performing any cleaning. The ratio of fin biting was considerably higher in small‐sized blennies, suggesting reliance on this feeding tactic because of a difficulty in conducting a risky egg predation. Thus, our results suggest that the mimic blenny utilizes aggressive mimicry only when it is small as an alternative feeding tactic.