The use of external electronic tags on ish: an
evaluation of tag retention and tagging efects
Jepsen et al.
Jepsen et al. Anim Biotelemetry (2015) 3:49
DOI 10.1186/s40317-015-0086-z
Jepsen et al. Anim Biotelemetry (2015) 3:49
DOI 10.1186/s40317-015-0086-z
Open Access
REVIEW
The use of external electronic tags
on ish: an evaluation of tag retention
and tagging efects
Niels Jepsen1*, Eva B. Thorstad2, Torgeir Havn2 and Martyn C. Lucas3
Abstract
External tagging of fish with electronic tags has been used for decades for a wide range of marine and freshwater
species. In the early years of fish telemetry research, it was the most commonly used attachment method, but later
internal implants became preferred. Recently, the number of telemetry studies using external tagging has increased,
especially with the development of archival tags (data storage tags, DSTs), pop-up satellite archival tags (PSATs) and
other environment-sensing tags. Scientific evaluations of the tagging method are rather scarce for most species. We
identified 89 publications, reporting effects of external tagging for 80 different fish species, which constitute the main
basis for this review. External attachment holds certain benefits compared to other tagging methods, for example,
speed of application, and it may be the only option for fishes with a body shape unsuitable for surgical implantation,
or when using tags with sensors recording the external environment. The most commonly reported problems with
external tags are tissue damage, premature tag loss, and decreased swimming capacity, but the effects are highly
context dependent and species specific. Reduced growth and survival have also been recorded, but direct mortality
caused by external tagging seems rare. Most of the studies reviewed evaluate tag retention, survival, and tissue reactions. There is a general need for more research on the effects of external tagging of fish with electronic tags, but particularly there are few studies on predation risk, social interactions, and studies distinguishing capture and handling
effects from tagging effects. For PSATs, especially those that are large relative to fish size, there are particular problems
with a high proportion of premature tag losses, reduced swimming capacity, and likely increased predation, but
there remains a paucity of tag effect studies related to the use of PSATs. Before embarking on a field study employing
external tagging with electronic tags, we recommend the use of appropriate pilot studies, controlled where possible,
to quantify potential impacts of tagging.
Keywords: Telemetry, Tag attachment, Archival tag, PSAT, Survival, Tissue damage, Tag retention, Growth, Swimming,
Drag, Entanglement, Biofouling, Predation
Background
More than four decades ago, Bruce Shepherd [1] wrote:
“Although many researchers have looked in a cursory
fashion at transmitter attachment and its efect on ish
behavior, none have done so in detail. Results from a
study of ish activity have convinced me of the need for
careful examination of this problem”. his statement is
*Correspondence: nj@aqua.dtu.dk
1
Section for Freshwater Fisheries and Ecology, Technical University
of Denmark, 8600 Silkeborg, Denmark
Full list of author information is available at the end of the article
still valid. In general, the combined efect of capture, handling and tagging may change an animal’s behavior, and
lead to lawed results in telemetry studies.
Electronic tagging (referred to as telemetry and bio-logging) of free-ranging animals is widely used to study ish
spatial ecology, survival, and responses to the environment
[2–4]. he main methods for attaching electronic tags to
ish are surgical implantation in the body cavity, gastric
insertion, and external attachment [5, 6]. External attachment was the most common telemetry tag attachment
method for ish studied in the irst two decades (1956–
1975) of application [2], but was overtaken in popularity
© 2015 Jepsen et al. This article is distributed under the terms of the Creative Commons Attribution 4.0 International License
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Jepsen et al. Anim Biotelemetry (2015) 3:49
in the 1980s by surgical implantation in the body cavity,
largely due to tag miniaturization and extended battery
life [2]. While surgical implantation remains the most
commonly used method for electronic tag attachment to
ish [3], external attachment is widely used, especially, but
certainly not only, with the increased use of archival (data
storage tags, DSTs) and satellite tags [3], particularly popup satellite archival tags (PSATs, or PATs) [7].
While there are several review papers focusing on surgical implantation of tags and of their efects [8, 9], or
wider comparison of tag attachment methodologies [5],
there are relatively few studies on the efects of externally
attached tags and no papers summarizing the experiences
with, and evaluations of, external tagging of ish, across
the breadth of taxa and habitats. Over 20 years ago,
Baras [10] reviewed more than 1000 papers from studies using aquatic telemetry and found only 14 to evaluate
the efects of external attachment of electronic tags on
ish. In 2012, Drenner et al. [11], reviewed tagging studies of salmonids in marine environments and commented
on the lack of evaluations of tagging/handling efects. A
generic problem in such evaluations is to disentangle the
various efects of capture, handling, tagging, holding, and
transporting wild ish. When studies try to estimate the
efect of tagging it is often the combination of efects that
is measured. his makes it diicult to directly compare
diferent tagging methods in terms of adverse efects and
the critical reader should bear this in mind.
In this paper, our aim is to summarize and evaluate experiences with external tagging of ish with electronic tags, based on published studies and the authors’
own experiences. We do not provide a comparison of
the main tagging methods, which is available elsewhere
[3–6]. Instead, we provide a detailed overview of the utility and problems associated with external attachment
of electronic tags, with the aim of helping researchers
to determine the suitability of this method for planned
studies, and to be able to interpret data collected by using
such methods and draw appropriate conclusions from
the studies done. We also highlight key advantages and
disadvantages of external tagging with electronic tags and
suggest some important research areas that need to be
addressed for the better evaluation of external tag efects.
he following sections examine the important issue of
tag retention and appraise evidence for the extent and
nature of impacts of external tags on key attributes of ish
health. he main sections cover tag retention and efects
of tagging on swimming performance, growth, social
interactions, and survival.
Review
Literature searches for this review were made through
the homson Reuters Web of Science database and
Page 3 of 23
ProQuest Biological Sciences database with diferent
combinations of the key words: extern*, tag*, efect*, ish,
telemetry, transmit*. In addition, the authors have undertaken research on tagging efects and performed tagging
studies for many years, and their collections of scientiic
literature were used, as well as searching through reference lists of previous publications. he aim was to cover
publications on efects of external tagging as extensively
as possible. hus, we identiied 89 publications describing various efects of externally attached electronic
tags, ranging from detailed experimental evaluations to
more descriptive, but in our opinion relevant, reports
of observed efects. A body of literature exists reporting the efects of external conventional tags [e.g. 12],
but here we focus only on externally attached electronic
tags. Many of the same issues apply for attachment of
conventional tags, but fundamental diferences are the
larger size of electronic tags and that they usually, but
not always, take longer to attach than conventional tags
and often involve induction of general anesthesia as part
of the tag attachment procedure [3, 6]. In the 89 papers
(Table 1), information on 80 species, representing 20
orders is presented (Fig. 1), giving a total of 122 “species
studies” (several papers cover multiple species). Of these,
45 % were carried out in marine/brackish environments
and 55 % in freshwater. For marine/brackish environments, 38 % of the studies were wholly or partially conducted in controlled laboratory/mesocosm conditions,
while in freshwater, this applied to 64 % of cases. Of 24
studies examining tag efects (including tag retention) on
elasmobranchs, coelacanth, tarpon, tunas, and billishes,
only three were under controlled conditions. Most of the
publications concern tag retention (44), survival (38), tissue reaction to tag presence (31), general behavior (27),
swimming performance (21), growth (17), and feeding
(17). Few papers reported efects regarding physiology
(6), predation (5), catchability (3), and social interactions
(3) (Fig. 2).
A variety of attachment methods have been used for
external tags (Table 2) often optimized/tailored for the
species and study in question, and reined over time.
Early studies often used external attachment methods
based on easily available materials, including ish hooks
[13], alligator clips [14] and pull ties [15], and included
descriptive evaluation of the most efective tagging methods and body locations under semi-controlled conditions,
but without detailed evaluation of efects by comparison
to controls [16]. his lack of detailed studies was also
because early electronic tags were short-lived and so only
the most obvious acute impact efects were considered.
For fusiform and laterally compressed species, electronic
tags are often ixed with steel wires or nylon ilaments
through the muscle at the base of the dorsal in (Fig. 3),
Species
Buoyancy
General
behaviour/
activity
Sea lamprey (Petromyzon
marinus)
×
Catch- Migraability tion
Equilib- Feeding Growth
rium
Infections, PhysiPredawounds,
ological tion
tissue
efects
reactions,
healing
Repro- Response Retention/ Social
Survival Swimming Referduction to transmit-expulsion interacperformance ences
ter output
tions
[99]
×
Basking shark (Cetorhinus
maximus)
×
[17]
Basking shark (Cetorhinus
maximus)
×
[58]
Bigeye thresher shark (Alopias
superciliosus)
×
×
[7]
Great white shark (Carcharodon
carcharias)
×
×
[7]
Shortfin mako shark (Isurus
oxyrinchus)
×
×
[7]
Blacktip reef shark (Carcharhinus
melanopterus)
×
Blue shark (Prionace glauca)
×
[100]
[7]
×
Lemon shark (Negaprion brevirostris)
×
Oceanic whitetip shark (Carcharhinus longimanus)
[73]
×
×
[7]
×
×
[7]
School shark (Galeorhinus galeus) ×
[101]
Silky shark (Carcharhinus
falciformis)
Cownose ray (Rhinoptera
bonasus)
Cownose ray (Rhinoptera
bonasus)
×
×
[102]
×
[55]
Cowtail stingray (Pastinachus
atrus)
×
[100]
Porcupine ray (Urogymnus asperrimus)
×
[100]
Southern stingray (Dasyatis
americana)
West Indian ocean coelacanth
(Latimeria chalumnae)
[103]
×
[59]
Atlantic sturgeon (Acipenser
oxyrinchus oxyrinchus)
×
[29]
Atlantic sturgeon (Acipenser
oxyrinchus oxyrinchus)
×
[104]
×
[31]
×
×
×
Page 4 of 23
×
Lake sturgeon (Acipenser
fulvescens)
Jepsen et al. Anim Biotelemetry (2015) 3:49
Table 1 Summary table of studies that incorporate an evaluation of one or more efects of external tagging
Species
Buoyancy
General
behaviour/
activity
Catch- Migraability tion
Equilib- Feeding Growth
rium
Lake sturgeon (Acienser fulvescens)
Infections, PhysiPredawounds,
ological tion
tissue
efects
reactions,
healing
×
Survival Swimming ReferRepro- Response Retention/ Social
performance ences
duction to transmit-expulsion interactions
ter output
×
Shortnose sturgeon (Acipenser
brevirostrum)
[32]
×
[29]
×
Shortnose sturgeon (Acipenser
brevirostrum)
×
White sturgeon (Acipenser transmontanus)
Tarpon (Megalops atlanticus)
American eel (Anguilla rostrata)
×
×
American eel (Anguilla rostrata)
×
×
×
×
×
×
×
×
×
[30]
×
[33]
×
[38]
[7]
[91]
×
European eel (Anguilla anguilla)
×
European eel (Anguilla anguilla)
×
European eel (Anguilla anguilla) ×
×
×
×
×
Longfin eel (Anguilla dieffenbachia)
×
Common carp (Cyprinus carpio) ×
×
×
×
×
×
×
Tigerfish (Hydrocynus vittatus)
Mekong giant catfish (Pangasianodon gigas)
×
Chinook salmon (Oncorhynchus
tshawytscha)
[85]
×
[106]
×
×
×
[34]
×
×
[36]
×
[81]
×
×
×
[40]
×
×
×
[41]
×
×
×
[23]
×
×
×
×
×
[72]
×
[67]
Page 5 of 23
Chinook salmon (Oncorhynchus
tshawytscha)
Chinook salmon (Oncorhynchus
tshawytscha)
[82]
[77]
×
Chinook salmon (Oncorhynchus
tshawytscha)
Chinook salmon (Oncorhynchus
tshawytscha)
×
×
×
Blue catfish (Ictalurus furcatus)
Chinook salmon (Oncorhynchus
tshawytscha)
[105]
×
×
×
[78]
×
Common carp (Cyprinus carpio)
Tench (Tinca tinca)
[71]
[75]
×
Common bream (Abramis brama) ×
Dace (Leuciscus leuciscus)
[70]
[54]
×
Barbel (Barbus barbus)
[69]
[19]
×
European eel (Anguilla anguilla)
Jepsen et al. Anim Biotelemetry (2015) 3:49
Table 1 continued
Species
Buoyancy
General
behaviour/
activity
Catch- Migraability tion
Equilib- Feeding Growth
rium
Masu salmon (Oncorhynchus
masou)
Rainbow trout (Oncorhynchus
mykiss)
×
Infections, PhysiPredawounds,
ological tion
tissue
efects
reactions,
healing
×
Repro- Response Retention/ Social
Survival Swimming Referduction to transmit-expulsion interacperformance ences
ter output
tions
×
×
×
×
[68]
[1]
×
Rainbow trout (Oncorhynchus
mykiss)
Rainbow trout (Oncorhynchus
mykiss)
×
Atlantic salmon (Salmo salar)
×
×
×
[63]
×
[64]
[74]
×
Atlantic salmon (Salmo salar)
[107]
×
Atlantic salmon (Salmo salar)
[108]
×
Atlantic salmon (Salmo salar)
×
[65]
Atlantic salmon (Salmo salar)
×
[66]
×
[109]
×
[27]
Atlantic salmon (Salmo salar)
×
×
×
Atlantic salmon (Salmo salar)
×
×
×
Atlantic salmon (Salmo salar)
×
×
Brown trout (Salmo trutta)
×
Brown trout (Salmo trutta)
×
Brown trout (Salmo trutta)
×
×
×
[46]
[110]
×
×
×
Brown trout (Salmo trutta)
×
Brown trout (Salmo trutta)
×
×
[93]
×
×
×
×
[93]
×
×
×
×
×
×
×
×
Northern pike (Esox ucius)
×
Northern pike (Esox lucius)
×
×
×
[42]
×
[44]
[113]
×
×
[24]
×
[48]
×
×
Eulachon (Thaleichthys pacificus)
×
×
×
×
×
×
×
×
×
[113]
×
[86]
×
[88]
[50]
×
×
×
[62]
Page 6 of 23
Opah (Lampris guttatus)
Atlantic cod (Gadus morhua)
[1]
[25]
×
×
Muskellunge (Esox masquinongy)
Atlantic cod (Gadus morhua)
[28]
×
×
Inconnu (Stenodus nelma)
Northern pike (Esox lucius)
[26]
×
Cutthroat trout (Salmo clarki)
Arctic char (Salvelinus alpinus)
[111]
[112]
×
×
Brown trout (Salmo trutta)
Lake whitefish (Coregonus
clupeaformis)
[76]
×
×
Brown trout (Salmo trutta)
Arctic char (Salvelinus alpinus)
Jepsen et al. Anim Biotelemetry (2015) 3:49
Table 1 continued
Species
Buoyancy
General
behaviour/
activity
Atlantic cod (Gadus morhua)
×
Equilib- Feeding Growth
rium
×
Atlantic cod (Gadus morhua)
Long-snouted seahorse (Hippocampus guttulatus)
Catch- Migraability tion
Infections, PhysiPredawounds,
ological tion
tissue
efects
reactions,
healing
Repro- Response Retention/ Social
Survival Swimming Referduction to transmit-expulsion interacperformance ences
ter output
tions
[114]
×
×
×
×
[49]
×
[115]
×
European plaice (Pleuronectes
platessa)
×
Sole (Solea solea)
×
×
×
×
×
[49]
[53]
×
Copper rockfish (Sebastes
caurinus)
×
×
×
×
[116]
Quillback rockfish (Sebastes
maliger)
×
×
×
×
[116]
Bluegill (Lepomis macrochirus)
×
Largemouth bass (Micropterus
salmoides)
×
Smallmouth bass (Micropterus
dolmieui)
×
×
Rock bass (Ambloplites rupestris)
×
×
×
×
[80]
[117]
[117]
×
×
European seabass (Dicentrarchus ×
labrax)
×
European sea bass (Dicentrarchus
labrax)
×
×
×
×
×
×
Yellow perch (Perca flavescens)
×
×
Yellow perch (Perca flavescens)
×
×
Yellow perch (Perca flavescens)
×
×
×
×
[119]
×
×
×
[20]
×
[80]
×
×
×
×
×
×
×
[64]
×
×
×
[47]
×
×
[43]
×
×
[52]
×
×
[43]
×
×
[22]
Page 7 of 23
Yellowfin bream (Acanthopagrus ×
australis)
×
[117]
×
×
Mulloway (Argyrosomus
japonicus)
[53]
×
×
×
[16]
[114]
×
Two-spined blackfish (Gadopsis
bispinosus)
Silver perch (Bidyanus bidyanus)
×
[118]
White perch (Morone americana)
Salema porgy (Sarpa salpa)
[79]
×
Yellowtail (Seriola quinqueradiata) ×
River blackfish (Gadopsis marmoratus)
[47]
×
×
Rock bass (Ambloplites rupestris) ×
European seabass (Dicentrarchus
labrax)
Jepsen et al. Anim Biotelemetry (2015) 3:49
Table 1 continued
Species
Buoyancy
General
behaviour/
activity
Golden perch (Macquaria
ambigua)
×
Macquarie perch (Macquaria
australasica)
Catch- Migraability tion
Equilib- Feeding Growth
rium
×
Infections, PhysiPredawounds,
ological tion
tissue
efects
reactions,
healing
Repro- Response Retention/ Social
Survival Swimming Referduction to transmit-expulsion interacperformance ences
ter output
tions
×
×
×
×
[105]
×
[21]
Pink happy (Sargochromis giardia)
×
[60]
Three spot tilapia (Oreochromis
andersonii)
×
[60]
Monkeyface prickleback (Cebidi- ×
chthys violaceus)
×
Black cod (Paranotothenia
angustata)
×
×
Bigeye tuna (Thunnus obesus)
×
[120]
×
[121]
×
[122]
×
Bluefin tuna (Thunnus thynnus)
Yellowfin tuna (Thunnus
albacares)
×
×
×
×
[7]
[122]
×
Yellowfin tuna (Thunnus
albacares)
×
[7]
Swordfish (Xiphias gladius)
×
×
[7]
Black marlin (Istiompax indica)
×
×
[7]
Blue marlin (Makaira nigricans)
×
×
[7]
Striped marlin (Kajikia audax)
×
×
[7]
White marlin (Tetrapturus albidus)
White marlin (Tetrapturus albidus)
Jepsen et al. Anim Biotelemetry (2015) 3:49
Table 1 continued
×
×
×
[88]
×
[90]
Ranked in taxonomic order
Page 8 of 23
Jepsen et al. Anim Biotelemetry (2015) 3:49
Page 9 of 23
25
proportion of premature releases in many studies have
been strong drivers for improved attachment reliability
[7, 17].
20
Tag retention
Nu mb e r o f p u b lic a tio n s
30
15
10
5
Characiformes
Coelacanthiformes
Gasterosteiformes
Elopiformes
Lampriformes
Petromyzontiformes
Osmeriformes
Scorpaeniformes
Pleuronectiformes
Siluriformes
Esociformes
Gadiformes
Lamniformes
Carcharhiniformes
Myliobatiformes
Acipenseriformes
Anguilliforme s
Cypriniforme s
Sa lmoniforme s
Pe rciforme s
0
Fig. 1 Number of publications on effects of externally attached
electronic tags according to taxonomic order
Nu mb e r o f p u b lic a tio n s
50
40
30
20
10
Response to transmitter output
Reproduction
Social interactions
Predation
Catchability
Physiological effects
Buoyancy
Equilibrium
Migration
Growth
Sw imming pe rforma nce
Feeding
Infe ctions, w ounds, tissue re a ctions, he a ling
Ge ne ra l be ha viour / a ctivity
Re te ntion / e x pulsion
Survival
0
Fig. 2 Number of publications on various effects of externally
attached electronic tags
but many variations of this method are used. For tagging larger, marine ish, much development has recently
been carried out to reine methods of pole- and spear
gun-deployed dart attachments and tethers associated
with PSATs. he high cost of these tags and the high
Given the substantial cost of electronic tags, it is no surprise that studies have frequently evaluated rates and duration of tag retention, in some cases under laboratory or
mesocosm conditions, but often under ield conditions.
he use of laboratory or mesocosm environments enables
easy recording of tag loss, but may not be representative
of the natural conditions, particularly in terms of snagging and fouling risks, which may increase the loss rate of
external tags under natural compared to laboratory conditions [e.g. 4, 11, 25]. In the ield, retention of electronic
tags is most often demonstrated by recapture, which can
be habitat- and sampling eiciency dependent. Alternatively, tag loss may be demonstrated by premature release
and reporting of pop-up tags [7, 18, 19]. Double tagging,
where a conventional tag or PIT tag is used in combination with the main telemetry tag, can provide estimates
of tag retention for recaptured ish. A marked change in
movement patterns (most commonly an absence of movement as most tags are heavier than water and sink to the
bottom), depth or temperature, can be indicative of electronic tag loss, although it can also indicate mortality [3].
hus deinitive records of external electronic tag retention,
gained from recapture or direct observation, are most easily recorded in shallow, accessible environments, notably
freshwater and clear inshore, marine environments.
he recent, rapid development and application of
pop-up tags has encouraged greater attention to efective attachment methods due to the high proportion of
premature (before the pre-set time) releases when the
attachment fails [7, 19]. However, problems with retention of radio, acoustic, and data storage tags may be just
as evident across many species in freshwater habitats.
Broadhurst et al. [20] tagged wild two-spined blackish
(Gadopsis bispinosus) with external transmitters and
kept them in aquaria and found that all (100 %) of the
tags were shed within 8 days after tagging. In contrast,
they found no loss of external tags on Macquarie perch
(Macquaria australasica) after 28 days in a similar study
[21]. he two species were tagged the same way, but with
very diferent results, demonstrating the importance
of not uncritically transferring results from one species to others. For wild silver perch (Bidyanus bidyanus)
equipped with external tags, more than 50 % of the ish
had rejected their external tags within 146 days in tanks
or sea-cages [22]. Corbett et al. [23] also reported 100 %
tag loss during a 50-day laboratory experiment with adult
Chinook salmon (Oncorhynchus tshawytscha).
Jepsen et al. Anim Biotelemetry (2015) 3:49
Page 10 of 23
Table 2 Examples of the range of methods used to externally attach electronic tags to ish, several of which are suited
to the speciic morphology or taxa involved
Method
Example taxon
Reference
Fishing hook at base of dorsal fin attached by nylon tether to transmitter
Roccus chrysops
white bass
[13]
Small fishing hook at base of dorsal fin, attached by stiff nylon tether to PIT tag (highly temporary,
minimal handling)
Alosa sapidissima
American shad
[97]
Dorsal fin attachment using miniature alligator clip
Oncorhynchus clarki
cutthroat trout
[14]
Three nylon T-bar tags anchored on pterygiphores used to mount an H-shaped rubber saddle housing
the transmitter
Paranotothenia angustata
black cod
[121]
Pop-up satellite transmitter on monofilament tether with medical grade nylon dart harpoon attached at
base of dorsal fin (other studies have used stainless steel/titanium darts)
Thunnus thynnus
bluefin tuna
[123]
Steel dart attached to transmitter deployed by pneumatic gun; dart aimed at lateral surface of fish,
posterior to second dorsal fin (no internal organs)
Latimeria chalumnae
coelacanth
[59]
Archival tag attached to a barbed nylon pin passed through pre-punched hole in dorsal fin and secured
by female half of cattle ear tag
Galeorhinus galeus
school shark
[101]
Pull tie covered in soft tubing attached around caudal peduncle, tag attached to main pull tie
Sciaenops ocellata
red drum
[15]
Absorbable suture attachment through caudal peduncle, tag on one side, soft plate on other
Esox lucius
northern pike
[24]
Ventral attachment at base of anal fin
Seriola quinqueradiata yellowtail [16]
Ventral attachment in mid-section of abdomen
Gadus morhua
Atlantic cod
[114]
Pannier (dorsal saddle) attachment with tag and battery components on either side of the dorsal fin
Salmo trutta
brown trout
[46]
Side mount attachment on one side of dorsal musculature, below dorsal fin, with a flexible backing plate Oncorhynchus mykiss
on the other side, wire/monofilament through muscle section
rainbow trout
[64]
Side mount attachment with neoprene pad
Leuciscus leuciscus
dace
[77]
Side mount attachment with soft, spacing mounds
Cyprinus carpio
Common carp
[105]
Anterior-dorsal soft saddle attached superficially
Esox lucius
northern pike
[95]
Posterior dorso-lateral soft saddle harness attached through musculature
Esox lucius
northern pike
[48]
Flattened tag attached to inside of operculum using two lengths of monofilament, fastened outside
with washer and crimp
Cebidichthys violaceus
[120]
Tag attached to bony appendages on back of fish with polyfilament Dacron tether
Phycodurus eques
Leafy seadragon
[124]
Tag loss is not necessarily a negative outcome, because
shedding of a tag that becomes snagged in such a way
that it would immobilize the ish prevents sufering of the
animal [24]. his may be achieved if, for example, weak
links or absorbable sutures are used. However, it can
be diicult to do this in such a way that premature tag
losses do not occur before appropriate data have been
gathered and while ensuring that such tag losses can be
identiied. McCubbing et al. [25] used a single absorbable
suture through the dorsal muscle to attach radio tags to
pre-spawning adults of a threatened Arctic char (Salvelinus alpinus) population to ensure that tag attachment
was temporary, but found in preliminary observations
that upon release in the stream, ish sought refuge under
boulders and most tags were rapidly shed. he premature
shedding (determined by locating and recovering shed
tags during mobile tracking) was reduced by releasing
ish in the lake from which they had migrated, several
hundred meters downstream, but still a 25 % (5/20 ish)
tag loss occurred from within a few days after tagging.
More conventional, and more invasive, dorsal musculature tag attachments (body-tight, by use of stainless steel
wires) in salmonids such as adult Atlantic salmon (Salmo
salar) and brown trout (Salmo trutta) in rivers have
much higher retention rates [26–28] than those observed
for char by McCubbing et al. [25].
Generally, external tag attachment in ishes using benthic habitats causes diiculties in achieving adequate
Jepsen et al. Anim Biotelemetry (2015) 3:49
Fig. 3 Example of typical external transmitter placement on a
fusiform-bodied fish (Atlantic salmon, Salmo salar). This radio tag has
a flattened section that lies close to the body surface and is held in
place by stainless steel wires through the musculature. Note that
these tags have conspicuous return information, which is not problematic for adult salmon, but could be an issue for smaller fish that
may be susceptible to increased predation risk
tag retention. Tags must be attached snugly to the body
to minimize the risk of entanglement/snagging, biofouling and to minimize drag. Several studies have reported
problems with external tagging of sturgeon and catish
species. Collins et al. [29] used external radio tagging
on shortnose (Acipenser brevirostrum) and Atlantic (A.
oxyrinchus) sturgeons in a ield study and found poor
retention for both species. In a subsequent tank experiment, only one of 12 individuals retained the tag after
40 days [30]. hey judged external tagging unsuitable
for these species. However, Sutton et al. [31] tested different attachment methods on juvenile lake sturgeon (A.
fulvescens) kept in tanks and reported that heavier suture
material decreased transmitter loss, but the retention
was still poor (75 % loss after 26 days). A subsequent test
of diferent shapes of external tags resulted in loss of over
Page 11 of 23
30 % of the tags in juvenile lake sturgeon after 8 weeks
[32]. In contrast, Counihan and Frost [33] tagged juvenile, hatchery-reared white sturgeon (A. transmontanus) using external tags (two tagging methods/locations)
and observed no tag-loss during the short laboratory
study (7–20 days). Like sturgeon, catishes are known
to exhibit low tag retention [e.g. 34]. Bodine and Fleming [35] attempted an alternative tag attachment method
for blue catish (Ictalurus furcatus) by using the skeletal
structure (supraoccipital bone). In their 2-month laboratory/pond study, tag retention was 100 %, but in the
subsequent ield study in a lake, tag retention was 40 %
at 6 months and 19 % at 12 months. Mitamura et al. [36]
attached dummy (acoustic) tags to the pectoral in of
juveniles Mekong catish (Pangasianodon gigas) kept in
a pond for 2 months. All tagged ish survived and were
retrieved, but all had lost their tags. he reason why catish and sturgeon are shedding both internal and external
tags at a higher rate than most other ishes remains to be
understood, but generally they seem to have very active
tissue reactions to foreign bodies [37].
Adult anguillid eels represent a particularly diicult
group for achieving a high retention rate of external tags.
his is not only because of their benthic habits (except
during migrations in the open sea), but also because of
their body shape and lexibility, enabling them to bite at
tag attachments midway along the body, and facilitating
tag shedding by ‘knotting’ their body or passing through
narrow crevices. In a thorough laboratory study of the
efects of tagging American eel (Anguilla rostrata), Cottril et al. [38] found poor retention (9 %) of external tags
after a 12-week period. Most eels lost the tags within the
irst 3–4 weeks after tagging. Furthermore, considerable
tissue erosion was evident around the stainless steel wire
holding the external tags in place, and major scarring on
eels that shed tags was observed. However, in a similar
study with smaller (18 × 7.3 mm) external tags, European
eels, kept in a perforated tank in a river, showed 100 %
retention after 30 days (M. Lowry, pers. comm.).
Reduction of electronic tag size to a degree suitable for
small ish includes reduction of battery size, and hence
results in a short battery life. hus, since the life of small
electronic tags is usually low (but see [39]), external tagging can be preferred due to lower acute health efects
compared to surgical implantation, where a longer recovery period may be evident. In a ield study on Chinook
salmon smolts, Brown et al. [40] observed 10 % tag loss
9–17 days after tagging, as well as a high proportion of
tags that were loose or displaced. In another laboratory
study on Chinook smolts, only 5 % of the ish lost the
external tags within 2 weeks [41], but tearing and loosening of the sutures holding the tags were also observed.
In lake whiteish (Coregonus clupeaformis), Bégout Anras
Jepsen et al. Anim Biotelemetry (2015) 3:49
et al. [42] observed tag loss for 92 % of the ish within
20 days in tanks. Pursche et al. [43] observed 100 % retention of external miniature acoustic tags (5 days battery
life) on mulloway (Argyrosomus japonicus) and yellowin
bream (Acanthopagrus australis) kept in an aquarium,
after a study period of 7 days. Brown and Eiler [44] externally tagged gravid female inconnu (Stenodus nelma) and
found no evidence of tag loss or mortality in a 2-week
ield tracking study.
Some studies have sought to divide mass and volume
between two elements of a tag on either side of the ish,
attached in a pannier-mount, assuming that this should
reduce disequilibrium, and especially in cases of high tag
to body mass ratio [3, 45]. In general, use of this method
[e.g. 46] is less frequent today due not only to technical
advances in reducing tag size, but also because saddle
type tags, straddling the dorsal surface, are often associated with reduced tag retention rates and because of
greater tissue reaction efects (see below). In a laboratory-based comparison of single-side mounted and pannier type transmitters on bluegill (Lepomis macrochirus)
and yellow perch (Perca lavescens), Weimer et al. [47]
found that 40 % of the perch and 14 % of the bluegill
held in tanks shed their pannier type tags within 40 days.
None of the ish tagged with single-side mounts lost
these. Herke and Moring [48] tested a novel “harnessixed-tag” to attach large radio-tags to pike (Esox lucius)
and concluded that the method gave a high retention
rate, but two of six ish shed their tags during the 115-day
ield study. One pike was recaptured after 54 days with
the tag still in place, but some abrasion and tissue tearing
were evident.
A variety of marine-based studies have used modiications of conventional tagging methods (Floy, T-bar, Carlin, Peterson disc, etc.), to attach acoustic tags and DSTs.
A common method has been to attach a loose-hanging
tether from the electronic tag to a wire saddle through
the dorso-lateral musculature, secured by a Peterson disc
on the other side, for species such as Atlantic cod (Gadus
morhua) and plaice (Pleuronectes platessa) [49, 50] or
through in musculature for thornback ray (Raja clavata)
[51]. he purpose of the Peterson tag is to spread the
tension and reduce cutting of the wire through the skin
and muscle. Righton et al. [50] tagged Atlantic cod in the
laboratory with external DSTs in this way and observed
100 % retention of tags over a 6-month period. Arnold
and Holford [49] reported recaptures of a ‘signiicant proportion’ of plaice with acoustic tags (attached to Petersen
discs with a loose tether) and cod from the North Sea
that had lost acoustic tags, but did not quantify this.
In a comparison of tagging methods for sea bream
(Sarpa salpa) in experimental tanks, all ish with externally mounted acoustic transmitters retained their tag
Page 12 of 23
over a 14-day period, but on all ish some abrasion, injuries, and fouling occurred [52]. In a study of the efects
of tagging on growth of juvenile European seabass
(Dicentrarchus labrax) and juvenile sole (Solea solea) in
saltmarsh ponds, Bégout Anras et al. [53] observed a tagloss of 60 % after 47 days in sea bass, but reported 100 %
retention of tags by sole during 72 days.
When using PSATs, tag retention until the planned
release date is a crucial element of experimental planning
and has been diicult to achieve across a wide variety of
taxa [7, 19, 54]. his is particularly so for migrating eels,
which in the early stages of sea migration inhabit highly
structured environments. PSAT tagging of longin eel
(Anguilla diefenbachii) revealed a high rate of tag loss,
with only three of 10 tags providing data [54]. Results
from 275 silver European eel (A. anguilla) released on
European coasts equipped with PSATs to study the ocean
spawning migration indicated a large premature tag
release [19]. his was partly related to mechanical tag
loss, but also to a high predation rate (>20 % conirmed
predation of eels with PSATs). he natural predation
rate is unknown, so it is unclear to what extent the tag
contributed to an increased predation risk. Mean time
from tagging to premature tag release was 14–21 days
(maximum 9 months). In a laboratory test of four different attachment methods for PSATs on European eel,
Økland et al. [19] observed an overall tag retention after
6 months of 54 %. Retention varied from 0 to 100 %
among the attachment methods, but the method that
achieved no tag loss was regarded as less suitable because
of a strong negative reaction (the tagged ish were struggling to try to shed the tag and did not swim normally)
in the irst 2 days after tagging and showed consequent
damage to the swimming musculature.
PSAT attachment for inshore and demersal ish is
most commonly achieved under sedation or anesthetization by harness attachment to the ish while in a tagging trough, in a manner similar to tagging with radio or
acoustic transmitters. However, for large pelagic species,
tagging with a pole-mounted dart placed at the base of
the dorsal in, usually with the ish still in the water, is
the most common method. Onboard tagging is routinely
performed with large bluein tuna (hunnus thynnus) in
Nova Scotia, with no apparent problems for the ish or
tag retention (M. Stokesbury, pers. comm.). However, a
meta-analysis demonstrated that onboard tagging did
not improve tag retention for tunas and billishes, while
for sharks it reduced tag retention duration [7] and suggests that unless landing is needed (e.g. for insertion of
sensors), in situ tag attachment may be more efective. A
wide range of dart heads and associated attachment elements have been designed and used to try to maximize
retention. Musyl et al. [7] emphasized the importance of
Jepsen et al. Anim Biotelemetry (2015) 3:49
a small entry wound to minimize tissue damage and aid
healing. While ‘umbrella’ and ‘lopper’ dart head types,
with retaining elements that open after dart entry, are
often employed to improve retention, a meta-analysis
demonstrated nylon tag heads to have lower retention
characteristics than all other dart head designs [7].
Key factors likely contributing to PSAT loss in ield
studies are the relatively high drag and buoyancy of these
devices, causing local pressure at the attachment point
[55], increased by biofouling [7, 18]. Biofouling has also
been reported for standard telemetry tags [56]. Most
PSAT tags in large, pelagic species are lost from tens to
a few hundred days after attachment, while conventional
tag losses in tunas, for example, are typically 2–5 % per
year [57]. Witt et al. [58] reported high premature loss
rates of PAT (pop-up archival transmitting) tags attached
to basking shark (Cetorhinus maximus) at the base of the
dorsal in. Eight of nine tags released prematurely, and
four of these were lost after just 2 months. hey found
that nine of 12 smaller PAT tags attached the same way
were retained after 7 months. his supports a causal relationship between tag-size, drag, and tag loss in this species. As tag size continues to shrink with technological
advances, this should give improved retention in most
species when dart-head deployments of PSATs are used.
In deep-water environments, darting may be more efective than other external tagging methods, since other
methods than darting require the ish’s ascent to the surface for tagging. Shauer et al. [59] used in situ darting
to tag 11 coelacanths (Latimeria chalumnae) with large
(30 g) transmitters. Despite the hard ganoid scales of the
coelacanth, the dart was shot into the ish using a pneumatic gun from a manned submersible. Tracking records
demonstrated that the tags stayed in place for “at least
3–4 weeks”. After a period, the tags eventually came of
and apparently caused minimal harm to the ish.
As evident from the above-referred studies, tag retention is a major problem in many studies using external
tagging. Even for short-term studies this problem can
occur. It can be diicult to mount a tag so that it stays
in place without injuring the ish or resulting in premature tag-loss. External tagging is particularly problematic
for ish that live in close contact with sediment, vegetation or that take shelter in hard structures (roots, woody
debris, rocks or crevices). In general, the best success
with external tagging has been with large, robust freeswimming ish like adult Atlantic salmon, brown trout;
large, open-ocean ishes, or bottom dwelling latishes
that live on lat sediments. Likewise, experience with
external tags for large cichlids has been good [60, 61].
For fusiform and laterally compressed ishes tagged ex
situ, a tag lattened on one side, mounted close to the
body, below the dorsal in and aixed by wire or nylon
Page 13 of 23
through the musculature, seems to be the best method,
whereas most pannier-saddle-type mounts have been
problematic. For many large marine pelagic and deepwater species, external tags may best be applied in situ
by darting.
Swimming performance
Reduced swimming performance is one of the expected
efects of attaching external tags to ish because of the
additional drag exerted by the tag as the ish moves
through the water. External tags will change the streamlined body shape that many ish species possess, disturb
balance and, at worst, cause loss of equilibrium if the
tag is too heavy compared to the mass of the ish. Predatory species that rely on speed to catch prey may be less
successful and sufer reduced growth. For prey species
dependent on escaping predators, the additional drag
and weight of a tag (tag burden) may skew the balance
between life and death. he most commonly used metric
of tag burden is the ratio of tag mass to ish body mass
in air, though for external tags it may not be the most
relevant, since tag shape and volume strongly inluence
drag imparted and may inluence swimming, especially
at higher speeds, since drag increases as the square of
velocity. For migrating species, changes in swimming
performance may delay or reduce migration success.
Such indirect efects of tagging are diicult to assess, but
we identiied 21 studies that have used diferent methods
to evaluate efects on swimming performance by externally tagged ish.
In an early study, Shepherd [1] reported a swim trial
where the oxygen consumption rate of externally tagged
wild cutthroat trout (Salmo clarki) was compared with
control ish. he study demonstrated a higher oxygen
demand of tagged ish. A similar approach with small
numbers of tagged and untagged cod showed a higher
mass-speciic oxygen consumption rate of tagged ish
during swimming, indicating that there is a measurable
drag efect from the tag [62], as predicted by Arnold and
Holford [49]. In a study of the efect of external tagging
on juvenile rainbow trout (Oncorhynchus mykiss), Lewis
and Muntz [63] used tail beat frequency, opercular beat
rate, and drag measurements as indicators of swimming
performance. All three indicators were elevated in tagged
ish compared to controls, and a pannier-saddle-mounted
tag, generating more drag than a single-side mount,
caused a greater impact. Tests with a dorsal saddle-type
tag on the same species showed that time to exhaustion
was shorter for externally tagged ish than for surgically
implanted and control ish [64]. he same test with white
perch (Morone americana) showed large individual variation, but no diference was found between treatments
[64].
Jepsen et al. Anim Biotelemetry (2015) 3:49
A common approach to determine tagging impacts on
the swimming performance of ishes is to measure the
critical swimming speed (Ucrit), which is based on incremental increases in water velocity, and hence swimming
velocity, in a lume. Peake et al. [65] detected a diference in Ucrit between tagged and untagged wild Atlantic
salmon smolts, both for surgically implanted and externally tagged ish. his diference was not found in hatchery ish. In a similar study of hatchery smolts, McCleave
and Stred [66] found external tags to reduce the critical
swimming speed in comparison with untagged control
ish and intragastrically tagged ish. In a recent, comprehensive study by Janak et al. [67] on hatchery-reared
Chinook smolts, the mean Ucrit for control ish was 11
and 22 % higher than the mean for ish tagged with small
and large external transmitters, respectively. For juvenile masu salmon (Oncorhynchus masou), the Ucrit of
externally tagged ish was lower than that of surgically
implanted and sham-tagged (surgical procedure without
a tag inserted) groups [68]. Externally tagged juvenile
white sturgeon also exhibited lower Ucrit than control
ish [33].
Cottril et al. [38] did not ind any diferences in swimming performance between American eels tagged with
dummy acoustic tags (0.5 % tag/bm ratio) by external,
surgically implanted, and gastric methods and untagged
ish. However, for larger PSAT tags (2–3 % tag/bm), several studies have reported strong efects on swimming
performance of eels, including up to three-fold increases
in energy cost of transport [69–71]. Using spherical
PSAT dummies of varying sizes, in a series of respirometry measurements and kinematic analyses, Tudorache
et al. [71] suggested that the optimal location for single
point attachment of PSAT tags is more anterior than at
the middle of the body length in eels.
For adult Atlantic salmon, horstad et al. [27] compared swimming endurance between ish with large
external tags, small external tags, surgically implanted
tags, and control ish, and found no diferences among
groups in endurance, nor in values of plasma glucose,
haematocrit and plasma chloride. In a ield evaluation,
Gray and Haynes [72] compared rates of upstream movement of adult Chinook salmon tagged externally and
with gastric implanted tags in a ield study in the Columbia River, and found no diference in upstream movements between the groups. Sundström and Gruber [73]
attached large speed sensing tags to seven juvenile lemon
sharks (Negaprion brevirostris) in the ield and observed
“elevated swimming speed” during the irst 24 h after tagging, but after that “normal” behaviour was observed.
In general, these studies document a measurable efect
on oxygen demand and swimming performance from
ishes carrying an external electronic tag. his efect is
Page 14 of 23
most pronounced in relatively small ish, or when large
buoyant tags have been applied, as in the case of PSATs
and related devices. No marked efect was observed for
adult Atlantic salmon and lemon sharks with closely
attached traditional telemetry tags of less than 3 % tag
mass to body mass ratio [72, 73].
Growth
External tags may afect feeding and thus growth,
because movement can be impaired by the presence of
the tag. Furthermore, capture, handling, holding, and
tagging may compromise the health of a ish, afecting
the motivation and physical capability for feeding. External tags also involve additional mass and drag, which
may result in increased energy expenditure and reduced
growth, even if the ish is feeding normally. hus, growth
integrates a range of efects into one measurable parameter, because reduced performance will likely result in a
reduced growth. Growth rate can, therefore, be a good
indicator of long-term efects by tagging and a useful metric of impact. Field experiments where a tagged
ish must compete with untagged conspeciics for food
and habitat provide the best test, but most evaluations
of tag efects on growth are based on laboratory/mesocosm studies. he challenges of doing ield-based growth
experiments on identiiable individual ish (from which
individual growth rates can be measured) are signiicant
and it is both costly and risky for data capture to move
from laboratory to ield, thus limiting the number of
studies.
For hatchery-reared juvenile Atlantic salmon, Greenstreet and Morgan [74] observed a negative efect of dorsal saddle-type external tags on growth (in tanks) for all
size classes, with the smallest ish losing weight during a
17-day period. Weimer et al. [47] found a similar negative efect on growth in yellow perch and bluegill in tanks
carrying a saddle-type tag. hese species tagged with a
single-side mounted external tag also showed reduced
growth during the 40-day period, but the efect was less
pronounced than for the ish with saddle-type tags [47].
A similar pattern was also observed in hatchery-reared
juvenile Chinook salmon, tested for three tagging methods, with reduced growth evident after 2 weeks, and
the most pronounced negative efect seen in the saddletagged group [41]. Tank-reared barbel (Barbus barbus)
with side-mounted external dummy tags (2 % of body
mass) lost an average of 10 % of their body mass in the
60 days post tagging, compared to controls that gained
2 % of body mass. Externally tagged barbel had a signiicantly lower growth rate than surgically tagged ish
[75]. Externally tagged sub-adult farmed Atlantic salmon
exhibited normal activity and feeding in tanks the day
after intervention (unlike surgically implanted ish), but
Jepsen et al. Anim Biotelemetry (2015) 3:49
after 6 weeks, their growth rate was still only half that of
controls [76].
In a study of wild Atlantic cod, the use of externally
attached data-storage tags was tested both in the laboratory and in a large ield experiment [49]. he laboratory
results showed that growth of tagged cod did not differ from untagged control ish. In the ield experiment,
growth of recaptured cod was compared to the growth
of wild untagged cod and a slightly (but not signiicantly)
lower growth rate (length) was observed for the tagged
cod. Cottrill et al. [38] compared length and weight of
European eels in a laboratory study (control, gastric, surgically implanted, external) 8–10 weeks after treatment
and found no efect of tagging. Likewise, Økland et al.
[19] found no diference in growth (weight loss) between
tagged and untagged silver eels after 4 weeks. In the case
of silver eel, growth is not a strong indicator of tagging
efects because silver eels, like many other semelparous
ish species, are known not to feed after they start their
seaward migration. However, during migration, energy
use and weight loss of eels with large external tags may
be elevated due to increased drag. Beaumont et al. [77]
observed externally tagged dace (Leuciscus leuciscus) in
a glass-sided luviarium tank and compared the condition-factor (K) between tagged and untagged ish after
a 10-week period, and no signiicant diference was
recorded.
As most studies using external tagging with electronic
tags are relatively short-term, potential impacts on
growth have not been of deep concern, but the studies
above show negative efects on growth or body condition
in Atlantic salmon juveniles, yellow perch, bluegill, and
barbel, but not in cod, eel, and dace. he negative efect
on growth was stronger for dorsal-mounted pannier-saddle-type tags than for single-sided tags.
Social interactions
Movement and habitat use is partly determined by social
interactions in many ish species. Stress caused by capture, handling, and tagging may change aggression, position in dominance hierarchies, competition, parental
care, shoaling, and other types of social behavior, and
thus, lead to biased results in telemetry studies. Further,
features such as bright colors, speciic color patterns,
body size and shape, or size and shape of other morphological attributes (for instance adipose in size in reproductively mature male salmonids, degree of asymmetry)
have evolved in many ishes through sexual selection
either to increase attractiveness to the opposite sex or
related to competition with rivals of the same sex, with
the ultimate aim to maximize reproductive success. he
presence of an external tag on a ish may, due to the size,
shape or color of the tag, interfere with such signals.
Page 15 of 23
External tags may also increase the visibility of the ish
to such an extent that the predation risk is increased (see
“Survival” section below). Such efects may be reduced
by dying the tag to blend with ish color, thus camoulaging the tag [67]. Bright tag labels with return-information
should be kept on the side of the tag towards the ish to
reduce the visibility.
Only a few studies have been carried out to evaluate the
efects of external tagging on social interactions in ish
(Fig. 2), and the existing studies have not revealed severe
impacts. In a study of rainbow trout, dominance rank of
individual ish only changed marginally after tagging [64].
Externally tagged dace were observed to integrate into
a shoal after tagging [77]. When externally radio tagged
bream (Abramis brama) were located and recaptured
by seine netting, they were always part of a bream shoal,
demonstrating that after tagging they had reintegrated
[78]. Using ield observational methods, Cooke [79]
found no evidence that externally attached radio transmitters afect parental care by rock bass (Ambloplites
rupestris). Studies of social interactions may be more
sensitive to subtle but chronic efects by external tagging
than studies of other type tagging efects, but are diicult
to carry out in a controlled way. here is clearly a need
for more studies on social interactions. he lack of documented efects is not indicative of a lack of real efects,
because the number of existing studies is so low.
Survival
Survival is not a suicient indicator of the suitability of
a tagging method, but low survival is often a good indicator for a problematic method. In most telemetry studies, survival rates of externally tagged ish have been high,
but with species, habitat, and methodological variations.
hus, half of the studies where survival of externally
tagged ish was reported found no increased mortality
[compared to control ish (laboratory) or expected levels (ield)]. Mortalities reported in laboratory/mesocosm
studies are rarely predation related, as relatively few such
tests have been done (but see, for example, Ross and
McCormick [80] who quantiied such efects), whereas,
in the ield, mortalities represent a composite of disease, stress, physiological insult, and predation efects,
but these impacts are often diicult to disentangle. In
the laboratory, Greenstreet and Morgan [74] observed
relatively high mortality of the smallest Atlantic salmon
juveniles tagged with a “saddle-pack” dummy transmitter, but no mortality for larger individuals (18–20 cm).
Tests of single-side and saddle type transmitters on wild
bluegill and yellow perch, kept in tanks, showed up to
50 % mortality, mainly for perch, and highest with the
saddle mounted tags [47]. Testing of an external attachment method, as an alternative to surgical implantation,
Jepsen et al. Anim Biotelemetry (2015) 3:49
on wild blue catish kept in ponds, revealed mortality of
13 % over 6 months, possibly related to tagging. However, the authors also state that this may be attributed to
elevated stress and subsequent infection associated with
coninement in the hatchery pond [35]. Brown et al. [81]
compared survival of externally tagged hatchery-reared
Chinook salmon juveniles during simulated turbine passage (laboratory) and found no diference in mortality
between tagged and control ish. A further (ield) comparison between surgically implanted (PIT-tags) and
externally tagged hatchery-reared Chinook smolts during
passage of hydropower stations and along river reaches
showed that external tags were suitable for short-term
migration studies, but not for longer periods than 10 days
due to tag loss and mortality [40]. In masu salmon (Oncorhynchus masou) juveniles, kept in an outdoor tank, 83 %
of externally tagged and 42 % of surgically implanted ish
died within 68 days [68]. By contrast, Broadhurst et al.
[21] found high mortality (and tag expulsion) in the surgically implanted group, but no mortality or tag loss in
the externally tagged group in wild Macquarie perch kept
in aquaria. he same result was found in a study of common carp (Cyprinus carpio), kept in concrete ponds in
Africa, where all ish in the surgically implanted group
died and all externally tagged ish survived [82].
Corbett et al. [23] compared external tagging with gastric implant for adult Chinook in a 50-day laboratory
experiment. Only one of 10 externally tagged salmon
died, whereas there was high mortality (19/20) of ish
with gastric implants. In the ield, horstad et al. [28]
found little mortality (1 out of 39 ish did not migrate
upstream) in externally tagged sea trout (anadromous S.
trutta). A similar outcome for this species was recorded
by Økland et al. [26]. Likewise, in a lowland Danish river,
Aarestrup and Jepsen [83] used externally attached radio
tags to study wild sea-trout pre- and post-spawning
movements. hey observed some mortality (<20 %) of
tagged ish, but ascribed this to natural post-spawning
mortality. Some tagged ish left the river after the spawning period, but 10 of 25 tagged ish were retrieved by
electroishing with the tags still in place and only minor
abrasions. No tag loss was observed [83]. Similar results
were recorded for externally tagged Atlantic salmon in
the same river [84]. However, in a similar study of sea
trout spawning migration, in a smaller stream with abundant vegetation, the external tagging method had to be
abandoned due to tag loss, mortality, and observation of
wounds at the tag position, most likely caused by entanglement in vegetation (N. Jepsen, unpublished). By contrast, for externally tagged tench (Tinca tinca) in a weedy
lake after 1 month at liberty, nine of 15 ish were recovered with tags [85]. While some of the tags in this study
were shown to have loosened, the method was judged as
Page 16 of 23
successful even with ish living in a weedy environment.
he “tilt-tags” employed in this study also indicated
that tench exhibited the head-down feeding behaviors
expected [85], suggesting normal behavior.
Low mortality levels have been reported for mulloway and yellowin bream externally tagged with miniature acoustic tags in controlled studies of short (7 days)
duration [43]. However, over a longer timescale and for
larger silver perch with external tags, elevated mortality
occurred for tagged ish (40 %) compared to control ish
(10 %) after 257 days, and all surviving ish had shed their
tags [22]. Hanson and Ostrand [86] tested diferent electronic tagging methods on small anadromous eulachon
(haleichthys paciicus) and found high mortality (50 %)
after only 5 days, of all groups, including non-tagged control ish, indicating that this species is sensitive to capture, handling, and holding (in aquaria). For yellow perch
tagged with externally attached transmitters, Ross and
McCormick [80] found low survival (7 %) after 86 days
in a pond with low oxygen levels in summer, compared
to 82 % of control ish from the same pond, suggesting a
chronic impact of external tagging, combined with poor
water quality. In another experiment, they found that
externally tagged yellow perch, in a small pond with good
water quality and a small number of predatory northern pike, exhibited 41 % survival, compared to 94 % for
controls [80]. Several tagged perch were found in pike
stomachs at the end of the experiment, and the authors
inferred diferent susceptibility to predation to be a key
cause of mortality.
In the case of PSATs, it is possible to identify mortality in pelagic species because a static depth record over
several days is indicative of mortality, with the tagged
ish lying on the bottom, as opposed to normal changes
in depth through the water column. When released from
the ish, PSATs will loat to the surface, due to their positive buoyancy. Most PSATs will automatically release in
response to a preset time threshold at a stable depth (typically when on the bottom) and hence data can be used
to determine mortality rates [87], but may be unreliable
in some species, such as basking shark, which may spend
protracted periods at a stable depth. Since mortality may
also occur over deep-ocean areas, a failsafe release is
deployed at a speciic depth to prevent pressure damage
to the PSAT, which can also be used to estimate mortality
rates [87]. Mortality through predation can be identiied
on occasion, due to the tag’s light sensor recording darkness (in the predator’s gut) over an extended period, and
thermistor and depth log information can help to identify the predator type (e.g. persistent elevated temperatures, with temperatures characteristic of endothermic
tunas and sharks, or marine mammals) [88, 89]. While
such mortality estimates are possible, they were not
Jepsen et al. Anim Biotelemetry (2015) 3:49
included in Musyl et al.’s detailed meta-analytical study
[7], perhaps because interpretation of mortality in such
instances is an inexact science. Holland and Braun [17]
identiied a discussion-based reticence to report mortalities, as this could jeopardize some PSAT-based research.
We consider it likely that many PSAT-recorded mortalities of large oceanic ish [e.g. 87] relect capture and handling efects more than direct efect of tagging. Indeed,
many of those studies are actually directed at assessing
survival of released large pelagic species from unwanted
by-catch in commercial operations [e.g. 87, 90]. As
smaller ishes are being tagged with miniaturized PSATs,
predation is increasingly likely (large carnivores eat
smaller animals), but to distinguish the efects of natural
mortality from the increase due to PSAT tagging is dificult. he high mortality rates of PSAT-tagged American
eel [91], attributed most likely to predation by porbeagle
shark (Lamna nasus), may have been facilitated at least in
part by the relatively large and buoyant tag, perhaps making the eel more conspicuous than normal. Undoubtedly,
migrating eels can provide reliable food sources for top
predators, but identifying the additional efect of tagging
with large, positively buoyant tags in such an environment is diicult.
From the published studies, it appears that direct mortality caused by external tagging is usually low, but that
tagging may be contributory. Particularly, when tagging
ishes of relatively small size compared to the large buoyant PSAT tags, there seem to be an extra risk of mortality
due to predation. Hence, one should be cautious to draw
conclusions on natural mortality levels of relatively small
ishes, and causes for this mortality, based on results
from PSAT tagged ish. he combined efect of capture,
handling, tagging, and holding ish for observation can
cause signiicant mortality, and it is diicult to separate
between the efects of the tag and tagging itself, and the
efects of capture and handling. It is therefore important
to include untagged control ish in studies, whenever
possible (laboratory/tanks/ponds), or, for instance, by
comparing with less invasive tagging methods like dyemarking, coded wire tagging, or PIT-tagging in ield studies. In general, it seems that external tagging of juvenile
salmonids can be done, but the experiences are not as
good as they are for the surgical implant or tag injection
[39] techniques. Also perciforms (including Percidae,
Teraponidae, Centrarchidae) can be vulnerable to external tagging, but here the results vary among species and
studies. Overall, there is large variation in survival rates
among studies. In few cases, increased mortality rate
can be directly linked to the tagging procedure, but usually acute mortality is caused by the combined efect of
being captured, held, handled, and/or carrying the tag,
whereas the carrying of the tag is manifested principally
Page 17 of 23
as a chronic efect on growth, though in some cases with
increased incidence of mortality, linked to disease and/or
predation.
Discussion
A vital element of telemetry studies is that the tag should
not alter animal behavior or performance, and if it does,
that the efect can be measured and accounted for and
thus does not interfere with the conclusions of the study
[3]. Based on the information covered in this review, it is
clear that while external tagging can be a valuable method
to attach electronic tags to ish, substantial tag loss and
adverse efects to the ish can occur. In this context, it
is important to distinguish between acute and chronic
impacts of external tagging on ish behavior and health.
External attachment of standard electronic tags can be
achieved more quickly and less invasively than by surgical implantation employing suture closure, and may, particularly through dart-deployment in the ield, require no
anesthesia or handling of the ish [9]. herefore, recovery
and subsequent change in behavior from external tagging
may be minimal and involve no immediate risk of pathogen entry to the body cavity. However, while incision and
closure (by suturing) of the body wall in surgical implantation is invasive, once healed, long-term impacts are
often low, while increased tissue abrasion, tag visibility to
predators, and long-term elevated drag efects have the
potential to generate marked chronic impacts in external telemetry tagging applications [4, 8]. his is the main
reason for generally recommending surgical implants for
long-term studies.
Some of the subtle efects of tagging and release into
the natural environment, such as predation risk, are
among the best indicators of impact [92], but are increasingly diicult to evaluate under controlled conditions
because of complexities in obtaining ethical/welfare committee decisions to do so. One of the few examples of
studying increased predation risk resulting from external
electronic tagging [80] is more than 30 years old. Control
ish (handled and individually identiiable but not telemetry-tagged) cannot easily be recaptured from many natural environments, so this inhibits or biases assessment of
their survival, by comparison to telemetry tagged ish, the
known locations of which facilitate recapture, at least in
shallow water. Also, under ield conditions, without direct
observation or tag recovery, it can be diicult to distinguish telemetry tag loss from mortality of the tagged
ish, and to determine the cause of mortality (whether
from disease or predation, for example), in many aquatic
habitats. he best options for quantifying efects may be
in experiments using semi-natural closed systems that
can be drained down and eiciently sampled, and where
densities of predators and prey, including instrumented/
Jepsen et al. Anim Biotelemetry (2015) 3:49
treated ish, can be manipulated. However, there can be
problems with obtaining animal welfare permission to
establish such systems where the prime objective is to
expose tagged, sham-treated, and control animals to predation risk. Animal welfare committees can perceive this
as unnecessarily stressful to the experimental prey ish,
but demonstration of no impact (and hence bias) under
nature-like conditions for telemetry studies needs exactly
this type of experiment and evidence base.
Advantages and disadvantages of external tagging
Advantages of external tagging include (1) the attachment
can be easy and fast and requires less training than some
other tagging methods; (2) the method can be used for
ishes with a body shape not suitable for surgical implantation, for instance, in laterally or dorso-ventrally compressed ish with little space available in the body cavity;
(3) external tag position is an advantage if sensors are
used to record external variables (e.g. water temperature,
light, acceleration, salinity and oxygen concentration);
(4) anesthetization is not always required or desirable
(e.g. for many large, marine, pelagic species, or for large
freshwater ishes like sturgeon); (5) tagging ish like adult
salmon, that may be used for consumption, without using
anesthesia, makes it possible to release these immediately
after tagging without a withdrawal period [89]. Such a
period is often required to prevent human consumption of ‘narcotics’, and (6) if recovery of tags is essential,
external tags can easily be identiied by ishers at recapture and there is no need for a conventional external tag
to identify tagged ish (which is especially important for
data storage tags that need to be returned to download
stored data). Further, externally tagged ish can be more
easily recaptured, because the external tags can be entangled in gillnets [93]. his may be regarded as a disadvantage, but it is sometimes an advantage if the tags need to
be retrieved (e.g. data storage tags [93]). External attachment is the only option for PSATs that must be released
from the ish and loat to the surface to be able to transmit data to satellites. A last advantage of external tagging
is that it can be applied to female ish close to the spawning period. Using surgical implants on gravid females
may be problematic due to the presence of large gonads
(lack of room) and the concern that a tag may block the
passage of eggs and thus interfere with spawning.
he most commonly reported problems with external
tags are tissue damage, tag loss and decreased swimming
capacity. In summary, the disadvantages of external tagging are that (1) the tag interferes with the streamlined
body shape of the ish and increases drag, disequilibrium
and energy expenditure, and reduces swimming performance, (2) algae and sessile animals may grow on the
tag and antenna (fouling, especially in coastal areas) and
Page 18 of 23
increase the drag, which may further reduce swimming
performance, (3) the tag or antenna can be entangled
in aquatic vegetation, roots, between rocks or in ishing
nets, (4) the visible tag may afect predation risk, competition and other interactions with conspeciics, (5) the
method is not well-suited in the long term for fast-growing or non-feeding ish, (6) attachment wires may, in the
long term, cause extensive damage to muscle and integument, (7) there is potential for substantial tag loss in long
term studies (size/shape/species dependent), and (8) the
method is not usually suitable for measuring internal,
physiological variables in the long-term. In many cases
researchers can test for these disadvantages in preparation for or during the study. Knowledge about the species
in question, the habitat the tagged ish will be in and of
the current literature on tagging efects, will aid the decision of tagging method.
There is no perfect tagging method: which method
to choose?
here is no method for attaching electronic tags without some degree of negative impact on the ish, though
in many cases the efects may be minimal and may not
be detectable in comparisons with controls. he lack of a
perfect tagging method and the diversity of taxa and system-speciic efects make it diicult to choose which tagging method to use. Choice of method should be based
on careful evaluation of advantages and disadvantages of
the diferent tagging methods, dependent on ish species,
size, and life stage to be studied and the habitat, duration,
and aim of the study. Information and advice to aid the
decision can be found in the literature, and particularly
from studies of tagging efects in the same or similar species and habitats, but in many cases pilot experiments are
necessary.
Our own experiences with tagging adult Atlantic
salmon and brown trout with radio transmitters can
serve as an example of considerations and compromises made when selecting the tagging method. In general, we commonly use surgical implantation for tagging
ishes with electronic tags, but have often used external
attachment, for example, for adult salmonids during the
riverine upstream migration. he reason is that surgical
incisions may not heal easily in ish that are in periods of
high physical activity, and incisions may open up when
ish are jumping and swimming in waterfalls and strong
currents (own observations in Atlantic salmon, [27]). An
alternative could be to tag ish with surgically implanted
tags and hold them for some weeks after tagging in a pen
to let the incision heal before release. However, the risk
that keeping wild ish in captivity during the migration
stage might afect their post-release behavior is too large
[e.g. 94]. Laboratory studies in a swim speed chamber
Jepsen et al. Anim Biotelemetry (2015) 3:49
have shown that even relatively large external tags (1–3 %
tag to body mass ratio) do not afect the swimming performance of Atlantic salmon compared to ish with surgically implanted tags and untagged control ish [27].
However, large external tags (2–5 % tag to body mass
ratio) have been shown to reduce the total migration distance of the ish in rivers with strong currents and waterfalls, and increase the duration of delay below waterfalls
compared to ish tagged with smaller (0.5–1 % tag to
body mass ratio) external or surgically implanted tags
in both sea trout and Atlantic salmon ([27] and unpublished results). Hence, it seems that large external tags
may afect burst activity and jumping ability more than
sustainable swim speeds [27] as would be expected from
drag vs swimming velocity relationships. A comparison
between ish with small external tags and untagged ish
has not been possible in these ield studies. In summary,
we have concluded that both surgically implanted and
external tags may negatively afect upstream-migrating
salmonids in high-gradient rivers with strong lows and
obstructions to passage, but that external tags overall
have less negative impact than implants in such cases.
We use the smallest tags possible in fast-lowing rivers, even though this reduces the duration of the study
period, and when we draw conclusions from the results
we have to consider that a tagged ish might migrate a
shorter distance and at a slower speed than an untagged
ish in some cases.
he best success in studies using external tag attachment for fusiform or laterally compressed ish has often
been achieved with the simplest methods; a tag lattened
on the side facing the ish, ixed closely to the body on
one side of the ish, usually close to the dorsal in, with
two wires through the dorsal muscles. However, as an
example of how it is possible to adjust and modify tagging methods to achieve better retention, Beaumont and
Masters [24], Armstrong et al. [95], and Herke and Moring [48] all tagged pike externally with diferent methods for diferent purposes and perspectives. Each of the
methods had speciic advantages and limitations.
For researchers not entirely sure about the choice of
tagging method, controlled tag efect studies will be useful to carry out. If resources are small and such studies
not possible, it can still be useful to tag a few ish and
observe them in the laboratory for shorter or longer
time-periods. his can be cost-efective by reducing
the risk of performing large ield studies that result in
little or heavily biased data because of a large tag loss
rate or mortality. Useful information can also be collected by recapture of some of the tagged ish towards
the end of ield studies to evaluate tagging efects. his
is particularly feasible in smaller freshwater systems, but
recaptures by ishers in larger systems, and also in some
Page 19 of 23
marine systems, can also help to evaluate the tagging
methods.
Fish and tag size
Despite considerable emphasis on limits of tag mass to
ish body mass (e.g. the so-called 2 % rule, [45]), there is
no generally applicable rule for how large the tag can be
in relation to ish body size [96]. he appropriate maximum relationship between tag size and ish body size is
determined by the speciic study objectives, the tagging
method, the species/life stage involved, and evidence
from pilot studies and related insights. In some cases, tag
efects are demonstrated with tags weighing less than 2 %
of the body mass of the ish, and in other cases larger tags
can be used without any signiicant tagging efects [96].
For potential tagging efects, tag size (volume) can be as
important as tag mass. If tags must be large, it is possible
to produce them so they are neutrally buoyant in water
to reduce the efects of extra weight, but the larger size
of the tag may increase drag and risk of entanglement in
aquatic vegetation. For PSATs, which are slightly positively buoyant and are attached by a tether, two forces
act on the tagged animal: the lift from the tag’s buoyancy
and drag as the tag is moved through the water column.
Hence, the attachment of PSATs is more challenging than
of external tags that can be attached against the ish body.
Nevertheless, we would also be very cautious in applying external telemetry tags for studies concentrating on
measuring peak swimming performance such as in ishway trials, due to drag efects, though it should be noted
that some studies have applied small external PIT tags
(0.6 g, <0.5 % tag to body mass ratio), with minimal ish
handling, for such evaluations with good outcomes (e.g.
[97]).
For small ish (<15 cm body length), the authors generally prefer to use surgical implantation instead of external
attachment methods. his is because a similar sized tag
can be carried inside the body cavity better than externally, because the tag is nearer the ish’s center of mass
and there is no drag. However, the recent advent of radioand acoustic ‘picotags’ (<1 g in weight) now allow the
tracking of smaller individuals, albeit over shorter time
periods (7–21 days), and may in some instances be wellsuited for external attachment as some of the cited papers
have shown. Equally, Deng et al’s [39] demonstration of
an injectable acoustic tag, 0.22 g mass in air and 3.4 mm
in diameter with a life of 100 days provides a long-life,
rapid tagging option that may herald a new generation of
picotag with low tagging impact.
here is no clear tag/ish size threshold, so we recommend using as small tags as possible to safeguard against
negative efects, even though this may compromise the
duration of the study period. If the goal is to study ish
Jepsen et al. Anim Biotelemetry (2015) 3:49
behavior over several seasons, an option is to tag new
ish each season instead of studying the same ish over
longer term. Several studies have shown that tag efects
are less severe for smaller tags when compared to larger
tag sizes (e.g. [28, 58]). For example, a larger proportion
of ish with large external tags had signs of wounds at the
tag attachments than those tagged with smaller tags [27].
Tag shape
External tags are often attached with stainless steel wires
or nylon ilaments through the muscle at the dorsal in,
with the tag resting at the skin below the in. Tags with
a lat shape facing the body are better suited for such
external attachment than cylindrical tags because they
interfere less with a streamlined body shape, rest closer
to the ish, and are, therefore, less likely to loosen and
cause long-term negative impacts. However, due to the
components of acoustic tags, they are usually produced
with a cylindrical shape and are, therefore, less suitable
for external tagging than radio transmitters and archival tags, which are available in both cylindrical and lat
shapes. An exception to this may be for sturgeon, which
seems to have better tag retention for cylindrical tags
than lat tags when using external attachment, likely
because of their concave body shape beneath the bone
plates (scutes) [31].
The way forward
he large variation in results, even from the same tags
attached to the same species and size of ish, makes it
diicult to generalize tagging advice, and the best advice
is to test the speciic method as thoroughly as possible
before using it in the ield. here is a need for more tag
efect studies (including externally mounted electronic
tags) in both ield and laboratory environments, particularly studies including control groups of untagged ish,
studies evaluating efects of diferent tag/ish sizes, and
studies with larger sample sizes. Also, inclusion of sham
tagged groups could be useful to separate possible efects
of the tagging process from the efects of carrying a tag.
In studies of surgical implanting, sham-tagged control
groups are often included, but this has not been the case
in external tagging studies.
Although potentially relevant, subtle efects like social
interactions and predation are the least studied impacts.
Studies of predation risk related to tagging may be among
the best bioassays of impact (e.g. [98]) and are important
to evaluate how well tagged ish represent natural mortality in diferent ecosystems. here is, however, still a
need for studies of tag loss, swimming performance, and
growth for many species, as well as studies that can be
used to reine tagging methods.
Page 20 of 23
For large PSATs, published tagging efect studies have
demonstrated particular problems related to tag loss,
reduced swim capacity, and likely increased predation.
However, there is still a paucity of tag efect studies
related to the use of PSATs and a large need for studies
quantifying tagging efects and studies that can be used
to reine tagging methods and reduce possible efects.
In all tagging experiences, it is crucial that the experimental ish are captured (if wild) and handled in the most
careful way. Most experienced ish researchers agree that
acquiring the right ish, at the right time, in the right condition, is often the most challenging part of a telemetry
study, especially when using wild ish. here is much
focus in the literature and by ethical committees on tag
efects, but often the combined efects of capture and
handling may be even more important for the welfare of
the ish and the outcome of the study than tagging itself.
We would, therefore, like to emphasize the particular
need for more studies on efects of capture and handling,
by comparison to tagging, on subsequent performance in
the short and longer term.
Authors’ contributions
All authors contributed to the collection of the literature and drafting of the
manuscript. All authors read and approved the final manuscript.
Author details
1
Section for Freshwater Fisheries and Ecology, Technical University of Denmark, 8600 Silkeborg, Denmark. 2 Norwegian Institute for Nature Research
(NINA), 7485 Trondheim, Norway. 3 School of Biological and Biomedical Sciences, Durham University, South Road, Durham DH1 3LE, UK.
Acknowledgements
NJ was funded by Fiskeplejen (the Danish Rod License), and EBT and TBH were
funded by the Norwegian Institute for Nature Research (NINA).
Compliance with ethical guidelines
Competing interests
The authors declare that they have no competing interests.
Received: 3 June 2015 Accepted: 17 September 2015
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