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AQUACULTURE ENVIRONMENT INTERACTIONS
Aquacult Environ Interact
Vol. 12: 61–66, 2020
https://doi.org/10.3354/aei00347 Published February 13
1. INTRODUCTION
Biological control utilizes living organisms (control
agents) to suppress the population density and subse-
quent impact of a specific pest organism by leveraging
ecological interactions through predation, parasitism,
herbivory, or other natural mechanisms (Eilenberg et
al. 2001). Biological controls are used extensively in
agriculture, where the tactical release of parasites or
predators is used to reduce insect pest species of eco-
nomic importance (Smith & Basinger 1947, Simmonds
et al. 1976, Greathead 1994, Eilenberg et al. 2001). In
aquaculture, high stocking densities of cultured or-
ganisms can facilitate transmission of pathogens and
parasites, requiring analogous approaches for disease
management (Deady et al. 1995, Tully et al. 1996,
Maeda et al. 1997, Powell et al. 2018). In the northern
hemisphere, cleaner fishes (e.g. ballan wrasse Labrus
bergylta Ascanius, 1767 and, more recently, lumpfish
Cyclopterus lumpus Linnaeus, 1758) are bred in cap-
tivity and subsequently cohabited with farmed salmon
(primarily Salmo salar Linnaeus, 1758) to remove ec-
toparasitic copepods (e.g. Lepeophtheirus salmonis
[Krøyer, 1837]; Tully et al. 1996). This non-chemical
© The authors 2020. Open Access under Creative Commons by
Attribution Licence. Use, distribution and reproduction are un -
restricted. Authors and original publication must be credited.
Publisher: Inter-Research · www.int-res.com
*Corresponding author: jonathan.barton1@my.jcu.edu.au
NOTE
Biological controls to manage Acropora-eating
flatworms in coral aquaculture
Jonathan A. Barton1, 2, 3,*, Craig Humphrey2, 3, David G. Bourne1, 2, Kate S. Hutson1, 4
1College of Science and Engineering, James Cook University, Douglas, QLD 4814, Australia
2Australian Institute of Marine Science, Cape Cleveland, QLD 4816, Australia
3AIMS@JCU, James Cook University, DB17-148, Townsville, QLD 4811, Australia
4Cawthron Institute, 98 Halifax Street East, Nelson 7010, New Zealand
ABSTRACT: Coral aquaculture is expanding to supply the marine ornamental trade and active
coral reef restoration. A common pest of Acropora corals is the Acropora-eating flatworm Prosthio -
stomum acroporae, which can cause colonial mortality at high infestation densities on Acropora
spp. We investigated the potential of 2 biological control organisms in marine aquaria for the con-
trol of P. acroporae infestations. A. millepora fragments infested with adult polyclad flatworms (5
flatworms fragment−1) or single egg clusters laid on Acropora skeleton were cohabited with either
sixline wrasse Pseudocheilinus hexataenia or the peppermint shrimp Lysmata vittata and com-
pared to a control (i.e. no predator) to assess their ability to consume P. acroporae at different life
stages over 24 h. P. hexataenia consumed 100% of adult flatworms from A. millepora fragments
(n = 9; 5 flatworms fragment−1), while L. vittata consumed 82.0 ± 26.76% of adult flatworms (mean
± SD; n = 20). Pseudocheilinus hexataenia did not consume any Prosthiostomum acroporae egg cap-
sules, while L. vittata consumed 63.67 ± 43.48% (n = 20) of egg capsules on the Acropora skeletons.
Mean handling losses in controls were 5.83 % (shrimp system) and 7.50% (fish system) of flatworms
and 2.39% (fish system) and 7.50 % (shrimp system) of egg capsules. Encounters be tween L. vittata
and P. hexataenia result in predation of P. acroporae on an Acro pora coral host and represent viable
biological controls for reducing infestations of P. acroporae in aquaculture systems.
KEY WORDS: Prosthiostomum acroporae · Acropora-eating flatworm · Lysmata vittata ·
Pseudocheilinus hexataenia · Biological control · Coral aquaculture
O
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Aquacult Environ Interact 12: 61– 66, 2020
approach to pest management is preferable to costly
treatments, which stress cultured fish and reduce ap-
petite (Skiftesvik et al. 2013, Powell et al. 2018).
Within coral aquaculture and the marine ornamental
trade, the peppermint shrimps Lysmata wurdemanni
(Gibbes, 1850), L. seti caudata (Risso, 1816), L. bog -
gessi, and L. ankeri Rhyne & Lin, 2005, as well as the
nudibranch Berghia sp. are used for biological control
of anemones Aiptasia spp. (Rhyne et al. 2004, Calado
et al. 2005, Rhyne & Lin 2006). The reef fishes Thalas-
soma duperrey (Quoy & Gaimard, 1824) and Chaeto -
don auriga Forsskål, 1775 are also potential candi-
dates to mitigate infestations of the corallivorous
nudibranch Phestilla sibogae Begh, 1905 in captivity
(Gochfeld & Aeby 1997).
Control of pests of Acropora spp. coral is highly
desired, given that it is the most represented genus
imported into many countries globally (Rhyne et al.
2014), and Acropora spp. are commonly used for reef
restoration efforts (Barton et al. 2017). A problematic
coral pest, Prosthiostomum acroporae (Rawlinson,
Gillis, Billings, & Borneman, 2011), commonly known
as the Acropora-eating flatworm, has plagued hob-
byist aquaria for many years (Delbeek & Sprung
2005). P. acroporae is an obligate associate of Acrop-
ora spp. and actively consumes coral tissue, which
results in characteristic ~1 mm circular pale feeding
scars, often resulting in coral tissue necrosis. Infesta-
tions are associated with colonial mortality at high
densities in captivity (Nosratpour 2008). P. acroporae
infestations are challenging to detect because of their
highly cryptic nature, which facilitates their spread
into new systems undetected. Infestations impact
coral health through reduction of host coral fluores-
cence over time and hinder the coral’s ability to photo-
acclimate to changes in lighting conditions (Hume et
al. 2014). Infestations are often not de tected until
compromised host health is observed through visual
signs, at which point flatworm population density is
high and colonial mortality of the coral may occur.
There is no current empirical evidence to support
effective treatment or prevention measures for P.
acroporae infestations, although Barton et al. (2019)
examined the life cycle under a range of temperature
conditions and suggested timed intervention to dis-
rupt the life cycle.
The aim of the present study was to evaluate the
potential of 2 biological controls to reduce infestation
by the Acropora-eating flatworm P. acroporae on
coral. Biocontrol candidates included the peppermint
shrimp L. vittata (Stimpson, 1860), which has been
previously reported to remove parasites on fish and
in the environment (Vaughan et al. 2017, 2018a,b),
and the wrasse Pseudocheilinus hexataenia (Bleeker,
1857), based on anecdotal evidence that it may
reduce P. acroporae populations in aquaria through
active foraging (Delbeek & Sprung 2005). This study
examined the efficacy of potential biocontrols on
adults and eggs of Prosthiostomum acroporae in
captive systems over a 24 h period in vivo.
2. MATERIALS AND METHODS
2.1. Species selection, husbandry, and culture
Twenty Lysmata vittata and 10 Pseudocheilinus
hexataenia were purchased from Cairns Marine,
Cairns, Australia, and maintained for 1 mo before
any experimentation. Because of space limitations,
shrimps were housed together in one 50 l flow-
through aquarium system (10 turnovers d−1) with
approximately 5 kg of ‘live’ rock for hiding and pro-
tection between molts. P. hexataenia were housed
individually in 50 l flow-through aquarium systems
(10 turnovers d−1) with a 60 mm PVC tee (3-way junc-
tion) each for shelter. Filtered seawater (0.04 µm
nominal pore size) at 27°C was used to supply the
system. Shrimps and fish were fed twice daily to sati-
ation with a mixture of thawed Tasmanian mysid
shrimp, Ocean Nutrition®Marine Fish Eggs, Ocean
Nutrition®Cyclopods, and Vitalis®Platinum formu-
lated feed. Animals were fed the morning prior to the
commencement of each experimental trial but not
during their trial period.
Adult Prosthiostomum acroporae were collected
from a culture of infested captive Acropora spp. colo -
nies. Flatworms were maintained in culture using
established methods (see Barton et al. 2019).
2.2. Coral fragment preparation, infestation, and
egg collection
To provide A. millepora for biological control trials,
96 A. millepora fragments (approximately 50 mm
height; 30 mm width) were generated from donor
colo nies harvested from 2 colonies sourced from
Davies Reef, Australia (harvested September 2017;
GBRMPA Permit: G12/35236.1), and 5 captive colo -
nies originating from Orpheus Island, Australia (har-
vested May 2016; G14/36802.1). A combination of
bone cutters and a band saw (Gyrphon®Aquasaw
XL) was used to prune A. millepora fragments, which
were then fixed onto aragonite coral plugs (32 mm
diameter) with cyanoacrylate glue.
62
Barton et al.: Biological control of Prosthiostomum acroporae
To infest A. millepora fragments with P. acroporae,
fragments were housed temporarily in individual 5 l
containers. Before the start of each experimental
trial, 5 P. acroporae individuals, approximately 3 mm
in size, were directly pipetted onto each A. millepora
fragment. After 60 s, each fragment was gently
shaken to ensure P. acroporae had laterally ap -
pressed themselves to the host coral’s tissue and
were not stuck in the coral mucus (flatworms can dis-
lodge if stuck in mucus). Any worms that detached
were attempted to be reattached once and then dis-
carded for another specimen if unsuccessful.
Egg capsules were naturally laid on Acropora
skeleton in the P. acroporae culture and then har-
vested using bone cutters to remove the section of
skeleton with these eggs. The underside of each sub-
sequent skeletal fragment was glued onto clean
aragonite disks or ‘frag plugs’ with cyanoacrylate
glue. The number of eggs per cluster was determined
by counting them under a dissecting microscope
(Leica EZ4, 10−40× magnification) while immersed in
seawater to prevent desiccation. Only fragments of
coral skeleton bearing unhatched and undamaged
egg capsules were selected for experimentation.
2.3. L. vittata experiments
Experiments with L. vittata were conducted on 4
separate trial days (i.e. 6 control and 6 treatment
replicates per trial; n = 24 control; 24 treatment). On
the day before each L. vittata trial, a random number
generator was used to designate treatments and con-
trols to aquaria. PVC blocks (80 × 80 × 25 mm; 32 mm
diameter depression with central 10 × 15 mm hole to
hold 32 mm diameter aragonite plugs in all repli-
cates) were placed in each aquarium (3.5 l) before
each trial. After their morning feeding, 6 L. vittata
were haphazardly caught from their holding system
using a 500 ml wide−mouth container and placed
into their respective experimental tanks. L. vittata
were given a minimum of 2 h to acclimate to their
surroundings in the replicate experimental flow-
through aquaria (5 l h−1) maintained at 27 ± 0.1°C. L.
vittata were considered acclimated once they settled
on the bottom of each aquarium.
A. millepora fragments (1 per aquarium) infested
with 5 P. acroporae each were introduced to each of
the 3.5 l aquaria (treatment and control) for 24 h to
determine if the presence of L. vittata (treatment)
influenced the number of remaining flatworms on
each coral fragment. The number of flatworms
remaining was determined using a seawater screen-
ing method (Barton et al. 2019). In addition, the PVC
blocks and clear tanks were inspected for flatworms
with the naked eye after each trial, with any flat-
worms found added to the remaining total of flat-
worms. Experiments examining the influence of L.
vittata on P. acroporae egg capsules were conducted
using the same approach, with the exception of egg
capsules being counted before and after the trial
under a stereo microscope (Leica EZ4, 10−40× mag-
nification). Skeletal fragments (n = 48) were divided
equally across treatments and controls (i.e. n = 24
control, 24 treatment) in L. vittata trials with 47.27 ±
19.09 (mean ± SD) egg capsules per fragment. L. vit-
tata do not forage immediately before or after molt-
ing (D. Vaughan pers. comm.), therefore any shrimps
that molted during the 24 h trial were excluded (i.e.
4 replicates were removed due to molting; n = 20).
2.4. P. hexataenia experiments
P. hexataenia (n = 9) were acclimated for approxi-
mately 2 wk to their randomly allocated flow-through
aquaria at 27 ± 0.1°C with PVC blocks in place. The
50 l aquaria (n = 9 with wrasse, 9 without) were sep-
arated by black plastic because of the acute eyesight
and territorial behavior of P. hexataenia. After accli-
mation, each fish regularly accepted food and did not
exhibit signs of physical or behavioral stress.
Following morning feeding of P. hexataenia, in -
fested A. millepora fragments (5 flatworms each) were
introduced to each 50 l aquarium and left for a dura-
tion of 24 h to assess if the presence of the wrasse in-
fluenced the number of flatworms remaining on each
coral fragment. Flatworms were recovered using an
established screening method (Barton et al. 2019).
The surfaces of the aquaria and the PVC blocks hold-
ing the fragment plugs were inspected visually for
any remaining worms, which were added to the total
remaining flatworms if present. Experiments examin-
ing the influence of P. hexataenia on P. acroporae egg
capsules were conducted similarly, but egg capsules
were counted before and after in spection with a
stereo microscope (Leica EZ4, 10−40× magnification).
The 18 skeletal fragments used in P. hexataenia trials
(n = 9 treatment, 9 controls) had 42.33 ± 16.95 (mean ±
SD) egg capsules per skeletal fragment.
2.5. Statistical analysis
Binomial generalized linear mixed models (GLMMs)
and generalized linear models (GLMs) were gener-
63
Aquacult Environ Interact 12: 61– 66, 2020
ated in RStudio (Version 1.0.143; R packages ‘car,’
Fox & Weisberg 2019, and ‘lme4,’ Bates et al. 2015) to
assess the effect of L. vittata treatments on P. acropo-
rae egg capsules and individual flatworms. Treat-
ment was considered a random effect and trial iden-
tity a fixed effect in the model to ensure that there
were no effects that changed the results significantly
(p < 0.05) between L. vittata trials. Lacking any sig-
nificant effects from trial identity in both experiments
testing L. vittata egg and individual consumption, the
GLM with pooled data denoted any significant
effects (p < 0.05) of treatment on consumption for
each experiment. Four replicates were removed from
statistical analysis of the L. vittata vs. egg capsule
experiment because these replicates molted during
the experimental trial. Kruskal-Wallis tests were
used to assess the results of P. hexataenia experi-
ments with a significance threshold of α= 0.05.
3. RESULTS AND DISCUSSION
The peppermint shrimp Lysmata vittata consumed
both settled flatworm individuals and egg capsules
laid on coral skeleton. The presence of L. vittata
significantly reduced (GLM; p < 0.001) Prosthiosto-
mum acroporae infestations over 24 h, with 82.0 ±
26.76% of the flatworms consumed (mean ± SD; n =
20; Fig. 1). Control tanks (n = 24)
showed a loss of 5.83 ± 10.77% (n =
24; Fig. 1). This indicates that approx-
imately 94% of flatworms were re-
covered using the screening method,
which is consistent with previous use
(Barton et al. 2019). L. vittata also sig-
nificantly reduced P. acroporae egg
capsules (GLM; p < 0.05), with 63.7 ±
43.48% (n = 20) of the egg capsules
removed compared to only 1.0 ±
2.99% (n = 24) in the control (Fig. 1).
Lysmata shrimps use their setae-
covered antennules to detect chemi-
cal cues (via cuti cular sensilla) from
their environment and locate suitable
prey items (Zhu et al. 2011, Caves et
al. 2016). Because they do not use vi-
sual mechanisms to locate and cap-
ture prey, L. vittata predation on P.
acroporae is not hindered by the
camouflage of these flatworms. How-
ever, L. vittata must physically en -
counter P. acroporae eggs or individ-
uals while foraging to consume them,
thus potentially limiting their ability to control P. ac r o -
porae populations in larger aquaria (aquaria >3.5 l
were not tested in this study), where the probability of
a direct encounter would be limited by proximity and
the availability of alternate food sources (L. vittata
were not fed during the trials). Despite this possible
limitation, L. vittata remain useful as a potential treat-
ment of P. acroporae infestations because intimate co-
habitation with Acropora enables shrimp to scavenge
among coral branches and consume P. acroporae indi-
viduals and egg capsules. L. vittata are also an aggre-
gating species and can be kept in high numbers when
provided with sufficient food and shelter (Vaughan et
al. 2018b). Future research could examine diet prefer-
ences of L. vittata, which may contribute to their effi-
cacy in removing flatworms from Acropora colonies
(e.g. Grutter & Bshary 2004).
Experimental trials with Pseudocheilinus hexa -
taenia demonstrated that these fish are effective at
reducing the P. acroporae population, with their pres-
ence having a significant effect on flatworm abun -
dance remaining on A. millepora fragments (Kruskal-
Wallis; p < 0.001). All P. acroporae exposed to P.
hexataenia were removed over 24 h (100%; n = 9),
compared to a loss of 7.5 ± 13.92% of flatworms (mean
± SD; n = 9) in controls. In contrast, all egg capsules
were recovered intact in the experimental treatments
(100%; n = 9) when cohabited with P. hexataenia. In
64
Fig. 1. Proportion of Acropora-eating flatworm individuals and egg capsules
removed (error bars: ± SD) in the presence and absence of biocontrols. (A)
Lysmata vittata and flatworm individuals (n = 24), (B) L. vittata and flatworm
eggs (n = 20 egg clusters), (C) Pseudocheilinus hexataenia and flatworms (n =
9), and (D) P. hexataenia and flatworm eggs (n = 9 egg clusters). *: statistical
significance between treatments and controls. Photos: = L. vittata and P. hexa-
taenia. (P. hexataenia photo credit: creative commons license istockphoto.com
user: marrio31 id#471448553)
Barton et al.: Biological control of Prosthiostomum acroporae
the control, 2.39 ± 3.84% egg capsules (mean ± SD;
n = 9) were not recovered, resulting in significant dif-
ferences between treatment and control (Kruskal-
Wallis; p < 0.05), likely from incidental mechanical
damage to egg capsules through handling.
These results indicate that P. hexataenia is highly
efficient at eating flatworms using well-developed
eyesight (Gerlach et al. 2016) but does not interact
with the hard shell of flatworm egg capsules. The
implementation of P. hexataenia as biological con-
trols must consider their ecology and husbandry
requirements. In the wild, these fish actively forage
in their established territory (Geange & Stier 2009,
Geange 2010), generally only coming together for
mating purposes (Kuwamura 1981). While their for-
aging behavior appears similar in captivity, the soli-
tary and territorial nature of P. hexataenia renders
keeping more than 1 individual in smaller aquaria
(e.g. <1000 l) problematic. More than 1 individual
could be kept in aquaculture systems large enough
to avoid territorial confrontation, but the ‘patrol’
range of this territory may remain relatively constant.
It is for this reason, combined with the fact that this
fish does not interact with flatworm egg capsules,
that they may not be as suitable for treating acute
infestations of P. acroporae compared to L. vittata.
However, their performance in our trials suggests
that this colorful labrid is a useful tool for consuming
adult flatworms, thus mitigating the chronic impacts
of a given P. acroporae infestation by removing or
reducing the P. acroporae density to non-lethal levels
for the Acropora host.
P. hexataenia and L. vittata identify prey items in
different ways while foraging, which has implica-
tions for how they are used in the captive environ-
ment and their ecological roles in native ecosystems.
Little is understood about the dynamics of wild P.
acroporae populations, although our results may pro-
vide further understanding of the trophic relation-
ships between P. acroporae and natural predators in
reef ecosystems. P. acroporae are cryptic and there
are no documented infestations causing colonial mor-
tality of Acropora colonies in the wild. It does remain
likely that some proportion of wild mortality of Acro-
pora colonies attributed to other causes (e.g. sedi-
mentation and algal competition) is instead experi-
encing negative secondary effects on coral health
from P. acroporae infestation. However, the presence
of natural predators of P. acroporae (e.g. P. hexatae-
nia and L. vittata) may reduce incidences of mortality
in wild Acropora colonies.
In captive systems, pairing both of these biologi-
cal control organisms with the manual removal of
P. acroporae egg clusters is likely to be highly effec-
tive in reducing the overall infestation within a given
aquarium system. However, consideration must be
given to the sustainable supply of the organisms if
used as biological controls. L. vittata are available
through the ornamental trade and can be bred in
captivity. Although peppermint shrimp species from
other regions (e.g. L. wurdmenii, L. boggessi, Rhyne
& Lin 2006) were not investigated in the present
study, they could also be examined for their ability to
interact analogously with P. acroporae and could be
supplied sustainably for biocontrol of flatworm infes-
tations. Although P. hexataenia is categorized as
Least Concern (Bertoncini 2010; IUCN Red List
2010), overharvesting for use as biological controls in
the ornamental trade could impact local populations.
Lessons should be taken from the Scandinavian
salmonid industry, where harvesting of wrasse
broodstock used for biological control of sea lice par-
asites has exerted considerable pressures upon wild
populations (Brooker et al. 2018, Powell et al. 2018).
In summary, this study provides the first empirical
evidence of potential biological control organisms for
P. acroporae in captivity. The ability of both L. vittata
and P. hexataenia to consume P. acroporae renders
them useful preventative measures of infestation in
addition to potentially being used to treat colonies
infested with adult flatworms and thereby drastically
reducing the impact of this pest on captive colonies.
While P. hexataenia had no apparent interest in P.
acroporae egg capsules, L. vittata displayed the
added benefit of consuming egg capsules through
their foraging activities, with encounters with the
egg clusters likely to further control the flatworm
populations in captive systems. The addition of sus-
tainable biological control organisms adds a valuable
tool for flatworm control, which is suitable for both
aquarium hobbyists and large-scale coral aquacul-
ture facilities.
Acknowledgements. We thank Brett Bolte and Rachel Neil
for help in maintaining the P. acroporae culture. We also
thank Kate Rawlinson for constructive comments on the
manuscript. This project was funded through an AIMS@JCU
pilot grant. Experiments were conducted in the National Sea
Simulator, at the Australian Institute of Marine Science,
under James Cook University Animal Ethics approval
(A2466).
LITERATURE CITED
Barton JA, Willis BL, Hutson KS (2017) Coral propagation: a
review of techniques for ornamental trade and reef resto-
ration. Rev Aquacult 9: 238−256
65
Aquacult Environ Interact 12: 61– 66, 2020
Barton JA, Hutson KS, Bourne D, Humphrey C, Dybala C,
Rawlinson KA (2019) The life cycle of the Acropora coral-
eating flatworm (AEFW), Prosthiostomum acroporae; the
influence of temperature and management guidelines.
Front Mar Sci 6: 524
Bates D, Maechler M, Bolker B, Walker S (2015) Fitting lin-
ear mixed-effects models using lme4. J Stat Softw 67:
1−48
Bertoncini A (2010) Pseudocheilinus hexataenia. The IUCN
Red List of Threatened Species 2010: e.T187477 A 85 46
194. https://dx.doi.org/10.2305/IUCN.UK.2010-4. RLTS. T
187477 A8546194.en (accessed 30 January 2020)
Brooker AJ, Papadopoulou A, Gutierrez C, Rey S, Davie A,
Migauhw H (2018) Sustainable production and use of
cleaner fish for the biological control of sea lice: recent
advances and current challenges. Vet Rec 183: 383
Calado R, Figueiredo J, Rosa R, Nunes ML, Narciso L (2005)
Effects of temperature, density, and diet on develop-
ment, survival, settlement synchronism, and fatty acid
profile of the ornamental shrimp Lysmata seticaudata.
Aquaculture 245: 221−237
Caves EM, Frank TM, Johnsen S (2016) Spectral sensitivity,
spatial resolution and temporal resolution and their
implications for conspecific signalling in cleaner shrimp.
J Exp Biol 219: 597−608
Deady S, Varian SJ, Fives JM (1995) The use of cleaner-fish
to control sea lice on two Irish salmon (Salmo salar) farms
with particular reference to wrasse behaviour in salmon
cages. Aquaculture 131: 73−90
Delbeek JC, Sprung J (2005) The reef aquarium: science,
art, and technology, Vol 3. Ricordea Publishing, Coconut
Grove, FL
Eilenberg J, Hajek A, Lomer C (2001) Suggestions for unify-
ing the terminology in biological control. BioControl 46:
387−400
Fox J, Weisberg S (2019) An R companion to applied regres-
sion, 3rd edn. Sage, Thousand Oaks, CA
Geange SW (2010) Effects of larger heterospecifics and
structural refuge on the survival of a coral reef fish,
Thalas soma hardwicke. Mar Ecol Prog Ser 407: 197−207
Geange SW, Stier AC (2009) Order of arrival affects compe-
tition in two reef fishes. Ecology 90: 2868−2878
Gerlach T, Theobald J, Hart NS, Collin SP, Michiels NK
(2016) Fluorescence characterisation and visual ecology
of pseudocheilinid wrasses. Front Zool 13: 13
Gochfeld DJ, Aeby GS (1997) Control of populations of the
coral-feeding nudibranch Phestilla sibogae by fish and
crustacean predators. Mar Biol 130: 63−69
Greathead DJ (1994) History of biological control. Antenna
18: 187−199
Grutter AS, Bshary R (2004) Cleaner fish, Labroides di -
midiatus, diet preferences for different types of mucus
and parasitic gnathiid isopods. Anim Behav 68: 583−588
Hume BC, D’Angelo C, Cunnington A, Smith EG, Wieden-
mann J (2014) The corallivorous flatworm Amakusa-
plana acroporae: an invasive species threat to coral
reefs? Coral Reefs 33: 267−272
Kuwamura T (1981) Diurnal periodicity of spawning activity
in free-spawning labrid fishes. Jpn J Ichthyol 28: 343−348
(in Japanese)
Maeda M, Nogami K, Kanematsu M, Hirayama K (1997) The
concept of biological control methods in aquaculture.
Hydrobiologia 358: 285−290
Nosratpour F (2008) Observations of a polyclad flatworm
affecting acroporid corals in captivity. In: Leewis RJ,
Janse M (eds) Advances in coral husbandry in public
aquariums, Vol 2. Burgers’ Zoo, Arnhem, p 37−46
Powell A, Treasurer JW, Pooley CL, Keay AJ, Lloyd R, Ims-
land AK, Garcia de Leaniz C (2018) Use of lumpfish for
sea lice control in salmon farming: challenges and oppor-
tunities. Rev Aquacult 10: 683−702
Rawlinson KA, Gillis JA, Billings RE, Borneman EH (2011)
Taxonomy and life history of the Acropora-eating flat-
worm Amakusaplana acroporae nov. sp. (Polycladida:
Prosthiostomidae). Coral Reefs 30: 693
Rhyne AL, Lin J (2006) A western Atlantic peppermint shrimp
complex: redescription of Lysmata wurdemanni, descrip-
tion of four new species, and remarks on Lysmata rath-
bunae (Crustacea: Decapoda: Hippolytidae). Bull Mar Sci
79: 165–204
Rhyne AL, Lin J, Deal KJ (2004) Biological control of aquar-
ium pest anemone Aiptasia pallida Verrill by peppermint
shrimp Lysmata Risso. J Shellfish Res 23: 227−230
Rhyne AL, Tlusty MF, Kaufman L (2014) Is sustainable ex -
ploit ation of coral reefs possible? A view from the stand-
point of the marine aquarium trade. Curr Opin Environ
Sustain 7: 101–107
Simmonds FJ, Franz JM, Sailer RI (1976) History of biologi-
cal control. In: Huffaker CB, Messenger PS (eds) Theory
and practice of biological control. Academic Press, New
York, NY, p 17−39
Skiftesvik AB, Bjelland RM, Durif CMF, Johansen IS, Brow-
man HI (2013) Delousing of Atlantic salmon (Salmo salar)
by cultured vs. wild ballan wrasse (Labrus bergylta).
Aquaculture 402-403: 113−118
Smith HS, Basinger AJ (1947) History of biological control in
California. Calif Cultivator 94: 720−729
Tully O, Daly P, Lysaght S, Deady S, Varian S (1996) Use of
cleaner-wrasse (Centrolabrus exoletus (L.) and Cteno-
labrus rupestris (L.)) to control infestations of Caligus
elongatus Nordmann on farmed Atlantic salmon. Aqua-
culture 142: 11−24
Vaughan DB, Grutter AS, Costello MJ, Hutson KS (2017)
Cleaner fishes and shrimp diversity and a re evaluation
of cleaning symbioses. Fish Fish 18: 698−716
Vaughan DB, Grutter AS, Hutson KS (2018a) Cleaner
shrimp are a sustainable option to treat parasitic disease
in farmed fish. Sci Rep 8: 13959
Vaughan DB, Grutter AS, Hutson KS (2018b) Cleaner
shrimp remove parasite eggs on fish cages. Aquacult
Environ Interact 10: 429−436
Zhu J, Zhang D, Lin J (2011) Morphology and distribution
of antennal and antennular setae in Lysmata shrimp.
J Shellfish Res 30: 381−388
66
Editorial responsibility: Tim Dempster,
Melbourne, Victoria, Australia
Submitted: September 26, 2019; Accepted: December 9, 2019
Proofs received from author(s): Februar y 3, 2020