REVIEW
published: 13 December 2019
doi: 10.3389/fvets.2019.00444
Frontiers in Veterinary Science | www.frontiersin.org 1 December 2019 | Volume 6 | Article 444
Edited by:
Robert James Ossiboff,
University of Florida, United States
Reviewed by:
Alex M. Costidis,
Virginia Aquarium & Marine Science
Center, United States
Juan Manuel Campos Krauer,
University of Florida, United States
*Correspondence:
Ashley Barratclough
Specialty section:
This article was submitted to
Zoological Medicine,
a section of the journal
Frontiers in Veterinary Science
Received: 06 September 2019
Accepted: 26 November 2019
Published: 13 December 2019
Citation:
Barratclough A, Wells RS,
Schwacke LH, Rowles TK,
Gomez FM, Fauquier DA,
Sweeney JC, Townsend FI,
Hansen LJ, Zolman ES, Balmer BC
and Smith CR (2019) Health
Assessments of Common Bottlenose
Dolphins (Tursiops truncatus): Past,
Present, and Potential Conservation
Applications. Front. Vet. Sci. 6:444.
doi: 10.3389/fvets.2019.00444
Health Assessments of Common
Bottlenose Dolphins (Tursiops
truncatus): Past, Present, and
Potential Conservation Applications
Ashley Barratclough
1
*
, Randall S. Wells
2
, Lori H. Schwacke
1
, Teresa K. Rowles
3
,
Forrest M. Gomez
1
, Deborah A. Fauquier
3
, Jay C. Sweeney
4
, Forrest I. Townsend
5
,
Larry J. Hansen
1
, Eric S. Zolman
1
, Brian C. Balmer
1
and Cynthia R. Smith
1
1
National Marine Mammal Foundation, San Diego, CA, United States,
2
Chicago Zoological Society’s Sarasota Dolphin
Research Program, Mote Marine Laboratory, Sarasota, FL, United States,
3
NOAA, National Marine Fisheries Service, Office
of Protected Resources, Silver Spring, MD, United States,
4
Dolphin Quest, San Diego, CA, United States,
5
Bayside Hospital
for Animals, Fort Walton Beach, FL, United States
The common bottlenose dolphin (Tursiops truncatus) is a global marine mammal
species for which some populations, due to their coastal accessibility, have been
monitored diligently by scientists for decades. Health assessment examinations have
developed a comprehensive knowledge base of dolphin biology, population structure,
and environmental or anthropogenic stressors affecting their dynamics. Bottlenose
dolphin health assessments initially started as stock assessments prior to acquisition.
Over the last four decades, health assessments have evolved into essentia l conservation
management tools of free-ranging dolphin populations. Baseline data e nable comparison
of stressors between geographic l ocations and associated changes in individual and
population health status. In addition, long-term monitoring provides opportunities for
insights into population shifts over time, with retrospective application of novel diagnostic
tests on archived samples. Expanding scientific knowledge enables effective long-term
conservation management strategies by facilitating informed decision making and
improving social understanding of the anthropogenic effects. The ability to use bottlenose
dolphins as a model for studying marine mammal health has been pivotal in our
understanding of anthropogenic effects on multiple marine mammal species. Future
studies aim to build on current knowledge to influence management decisions and
species conservation. This paper reviews the historical approaches to dolphin health
assessments, present day achievements, and development of future conservation goals.
Keywords: dolphin, Tursiops truncatus, conservation, health assessment, veterinary medicine
INTRODUCTION
Assessment of marine mammal health is complex, both from an accessibility standpoint and from
the diverse array of factors influencing both individual and population survival. Baseline data are
particularly crucial to evaluate whether population, or in some cases species, health is deteriorating
by providing points of comparison to assess trends in disease, mortality, and reproductive rates (
1).
From a veterinary perspective, a hands-on physical exam is the optimal approach to provide critic al
Barratclough et al. Bottlenose Dolphin Health Assessments
information for a comprehensive understanding of both
individual and population-level health status. Knowledge gained
from physically examining smaller cetaceans can be extrapolated
to larger, less-accessible cetaceans to improve understanding of
the complexities of adverse health impacts on marine mammal
conservation. The common bottlenose dolphin (Tursiops
truncatus) is an effective model species for understanding both
cetacean and marine ec osystem health.
The overarching aim of conservation is to actively preserve
habitats and the diversity of species dwelling t h erein (
2). Effe ctive
conservation benefits from a foundation of sound scientific
understanding of species biology, population dynamics, and
stressors impacting the ecosystem (3). Marine ecosystem health
is particularly challenging to assess due to immense biological
diversity, as well as t he vast scale and connectivity of the ocean
environment. Multiple factors threaten marine mammal health
(
4); therefore, improving k nowledge of the interplay of these
factors and predicting their long-term effects are essential for
successful conservation.
The emerging discipline of conservation physiology is
particularly important in the marine environment, as it allows
a mechanistic understanding of the drivers of conservation
obstacles at an ecosystem level, in addition to species-specific
challenges. Understanding how species physiologically respond
to environmental alterations is important for successful tailored
conservation strate gies (5). The rate of expansion of the human
population is exacerbating the challenges faced by wildlife with
frequently detrimental consequences to their health (6). The
unprecedented changes occurring in the environment on a
global s cale require novel mitigation strate gies to ensure effective
conservation actions and sustainable wildlife populations (
7).
There is limited understanding of the scale of the negative
anthropogenic impact on marine mammal biodiversity.
Currently 29.2% of marine mammal species are classified as
data deficient according to the International Union for the
Conservation of Nature (8). As a result, shifts in population
viability can be difficult to detect, as the basic natural history
of the species has not been documented (9). Intrinsic traits of
species can be more important predictors of risk than extrinsic
environmental factors, as they provide a measure of the species
inherent susceptibility to human impacts and the ability of
species to recover from them (
10). The bottlenose dolphin is
one of the most closely studied and widely distributed marine
mammal species and provides an opportunity to extrapolate
knowledge and understanding to other marine mammal species.
HISTORICAL PERSPECTIVE
Initially the first common bottlenose dolphin captures occurred
for acquisition for public display, research, or for stock
assessment prior to collection. Over time health assessments
of inshore dolphins have been utilized to better understand
endemic disease, establish baseline physiological measures,
and evaluate exposure to, and potential effects of, chemical,
biological, and physical stressors. Historically, health assessments
developed as additions to existing capture-release efforts for
other purposes, such as marking/tagging and population-lev el
studies to understand movement patterns and site fidelity.
Starting in 1979, Hubbs/SeaWorld Research Institute began
collecting bottlenose dolphin health data in the Indian River
Lagoon of east Florida during capture-release operations to
assess potential population-level impacts in advance of upcoming
zoologic colle ct ions (Figure 1) (
11). Analyses from the samples
and data collected included morphometrics, blood biochemistry,
hematology and reproductive endocrinology, microbiology,
genetics, and life history studies (12). Similar research was
initiated by Marine Animal Productions in 1982 in Mississippi
Sound, with the inclusion of skin, blubber, and liver tissue
sampling in some cases, t o establish a health baseline for dolphins
inhabiting this area, again prior to collections and for comparison
with managed animals (13).
The Sarasota Dolphin Research Program (SDRP) began
incorporating additional biological samples and measurements
in 1984 to their original capture-release program. This supported
tagging and telemetry studies in Sarasota Bay, Florida, which
were initiated in 1970. The inclusion of additional biological
samples shifted the focus from studies of population range
and social patterns to broader scientific investigations of life
history, population dynamics, body condition and health, social
structure, communication, reproductive success, and effe cts of
human interactions. Samples and measurements included in-
depth bloodwork analyses, genetic tests for population structure
and paternity, ultrasonic measurement of blubber thickness,
weight measurement, age determination (tooth growth layer
group counts), further development of tags and tag attachments,
and post-rele ase population monitoring (
1419).
In 1992, the Marine Mammal Health and Stranding Response
Program was formalized within the National Marine Fisheries
Service (NMFS) through an amendment to th e Marine Mammal
Protection Act (MMPA), establishing the stand ards for sample
collections and promoting collaboration and standardization
of bottlenose dolphin health assessments (20). In 1995, NMFS
conducted health assessments in response to the 1987–88
mortality event along the east coast of the U.S., in which over
600 bottlenose dolphins stranded as a result of a large-scale
morbillivirus epizootic (2125). Additional studies were also
conducted to investigate unusual increases in dolphin strandings
near Matagorda Bay, Texas in 1992 (
26), and in the Florida
Panhandle in 2005–2006 (27) (Figure 1) (Table 1).
Supplementary c apture-release studies were initiated by the
National Oceanic and Atmospheric Administration (NOAA) in
support of stock assessment on the east coast, which was by
that time a requirement for NOAAs NMFS (23, 24). Subsequent
capture-release studies used telemetry to understand population
structure along the Atlantic coast (39) following increased
dolphin mortality (40) which was eventually determined to be
associated with morbillivirus (22, 30). The studies found positive
morbillivirus titers in some dolphins sampled in estuarine and
coastal waters near Beaufort, NC, with no positive titers observed
in dolphins sampled in estuaries near Charleston, SC (
30).
This provided crucial information to understanding dolphin
population structure and interaction along the U.S. east coast,
with a mosaic of migratory, non-migratory but coastal, and
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Barratclough et al. Bottlenose Dolphin Health Assessments
FIGURE 1 | Bottlenose dolphin capture-release health assessment locations in the U.S.
small estuarine stocks rather than a single large population as
initially presumed. In addition utilizing archived Sarasota Bay
samples to retrospectively assess morbillivirus titers facilitated
further understanding of virus exposure, seroconversion, and
population naivety (41). Incorporating health assessments
informed scientists that at least some small, estuarine stocks
along the Atlantic coast were naïve to morbillivirus and therefore
particularly vulnerable (38).
In 2003, the Health and Environmental Risk Assessment
(HERA) population monitoring project was initiated for
bottlenose dolphins in the Indian River Lagoon, Florida (IRL),
and waters surrounding Charleston, South Carolina (CHS) (
42).
For both the IRL and CHS field sites, health assessments
were conducted to establish baseline data and to compare
morbidity temporally and across two geographic sites (
34,
43). Higher concentrations of persistent organic pollut a nts
(POPs) including legacy [e.g., dichlorodiphenyltrichloroethanes
(DDTs), polychlorinated biphenyls (PCBs)] as well as “emerging”
contaminants [polybrominated diphenyl ethers (PBDEs) and
perfluorooctane sulfonate (PFOS) compounds] were detected in
CHS dolphins as compared to IRL dolphins (43, 44). Mercury
concentrations in the blood and skin of IRL dolphins were
extremely high, approximately five times higher than those
in CHS dolphins. Higher exposure to many pathogens (e.g.,
morbillivirus and lobomycosis) was also observed for the IRL
dolphins (34).
The incorporation of health assessments into existing capture-
release protocols provided the collection of baseline health
data across multiple populations, thus allowing for investigation
of geographic variability in he a lth parameters (32, 42). The
methodologies established and samples collected during these
earlier projects formed the b asis for developing a risk assessment
framework to quantify the impacts for dolphins affected by
anthropogenic threats (e.g., Deepwater Horizon oil spill) in
geographical areas where baseline data were not available (
36).
THREAT IDENTIFICATION AND
ASSESSMENT
Dolphin capture-release projects provide a unique perspective
to assess individual animal health and extrapolate to overall
health of the surrounding population, species, and ecosystem.
Over the past 40 ye a rs in the U.S., there have been numerous
stressors that have impacted bottlenose dolphin populations, for
which dolphin capture-release projects have been integral to
threat identification and quantification of impacts from a given
stressor (e.g., biotoxins, disease, environmental contaminants, oil
spills, etc.).
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Barratclough et al. Bottlenose Dolphin Health Assessments
TABLE 1 | Historical list of previous capture locations according to Figure 1 including number of animals examined or health assessments (HA) performed, purpose of
captures, and references.
Date Location Number of dolphins Purpose References
1979–1981 Indian River Lagoon FL 27
109 total HA
Population assessment (11)
1982 Mississippi Sound MS 57 Commercial assessment (
13, 28)
1984–2019
(ongoing)
Sarasota FL 289 individuals
811 total HA
Biological sampling, technique
development, reference
population
(
29)
1987 Virginia Beach VA 23 Mass mortality investigation (
21)
1992 Matagorda Bay TX 36 Mortality investigation (
26)
1995 Beaufort NC 31 HA post CeMV outbreak (
24)
1998 Virginia Beach VA 1 Stock assessment NOAA unpublished
data
1999 Charleston SC 14 Stock assessment (
30)
1999*
2000*
2006*
Beaufort NC 6
11
19
Stock assessment (
31)
(
30)
(
32)
2002–2003 Brigantine NJ 12 Stock assessment (
30)
2004 Holden Beach NC 10 Persistent organic pollutant
assessment
(
33)
2003–2018 Charleston SC
Indian River Lagoon FL
118
246
Comparative health studies (
34)
2005–2006 St. Joseph Bay FL 30 UME investigation (
27)
2009 Brunswick GA 29 HA legacy environmental
contamination
(
35)
2011–2018 Barataria Bay LA 202 DWH investigation (
36)
2013 Mississippi Sound MS 20 DWH investigation (
37)
2015 Brunswick GA 19 UME investigation (
38)
2018 Dauphin Island AL 18 DWH investigation
*
The numbers provided are for those where samples were used and published it does not necessarily provide a list of the total numbers of animals handled in this location.
Unusual Mortality Events
An unusual mortality event (UME) is defined under the
U.S. Marine Mammal Protection Act as “a stranding that is
unexpected; involves a significant die-off of any marine mammal
population; and demands immediate response.” The UME
program was officially established under Title IV of the MMPA
in 1992. Increased recognition of the occurrence of large scale
dolphin mortality events in the late 1980s spurred the application
of dolphin health assessments beyond population monitoring, to
investigating causes and effects of such mortality events (
21, 24).
Since 1999, a series of UMEs occurred along the northwestern
Florida coastline (Florida Panhandle) including St. Joseph Bay
(45). NOAA conducted two dolphin health assessments during
2005 and 2006 in response to these UMEs in which 30
dolphins were sampled and subsequently t agged (27) (Table 1).
The initial mortalities were tentatively attributed to biotoxins
from red tide algae (Karenia brevis) (
46). Eosinophilia was
obser ved in 23% of sampled dolphins, with associated increased
neutrophil phagocytosis and T-lymphocyte proliferation (27).
Chronic low-level exposure to another algal toxin, domoic acid,
produced by the diatom Pseudo-nitzschia spp., previously linked
to eosinophilia, was also identified (
47). Prior to these UMEs,
little was known about dolphin abundance, distribution, and
site fidelity in this region, and thus, it was unclear which
population(s) of dolphins were impacted (
48, 49). Post-health
assessment tagging data suggested that the timing and spatial
extent of biotoxin events and other potential stressors in the
Florida Panhandle may greatly influence the severity of future
UMEs (50). Cetacean post-mortem examinations can provide
insight into identifying the underlying cause of a UME in
addition to baseline data on disease presence and anthropogenic
causes of mortality (5153). Increased integration of live animal
assessment with post-mortem findings encourages the transfer
of information from the dead to the living, informing scientists
of the underlying pathophysiological mechanisms faced within
free-ranging populations (
54).
Chemical Pollutants
The presence of PCBs and other lipophilic contaminants have
been recorded to be accumulating in the tissues of bottlenose
dolphins and other odontocetes for decades (
31, 5559). Many
marine mammals, particularly piscivorous species, have a high
potential to biomagnify pollutants (
33), with increased levels
resulting from the high trophic position and blubber acting as
a reservoir for lipophilic contaminants (
60). Bot h experimenta l
and observational studies support the correlation between
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Barratclough et al. Bottlenose Dolphin Health Assessments
increased PCB levels and endocrine dysfunction, compromised
immunity, and/or reproductive failure (6166). However, the
common co-occurrence of similarly acting compounds and
uncertainty regarding species-specific dose response functions
makes assessment of th e effects of these contaminants at a
population level challenging (
60, 67).
In addition to their applicability to investigating UMEs,
dolphin health assessments have also been used to investigate
health of populations at risk from environmental contaminants.
For example, dolphins along the Georgia coast have been
identified wit h some of the highest concentrations of PCBs in
the world, and these levels are site-specific to a Superfund Site
in Brunswick, Georgia (60, 68, 69). In 2009, NOAA conducted
health assessments on 29 dolphins in the region and identified
a high proportion (26%) of sa mpled individuals suffered
from anemia (66). In addition, these dolphins had reduced
thyroid hormone levels with total thyroxine, free t hyroxine, and
triiodothyronine negatively correlated with increased blubber
PCB concentrations. T-lymphocyte proliferation and indices of
innate immunity decreased with blubber PCB concentration,
suggesting an increased susceptibility to infectious disease (
66).
As with previously described health assessments, telemetry and
photo-ID data provided perspective on ranging patterns relative
to exposure, subsequent reproductive success, and effects of
long-term impacts from cumulative stressors (70). In 2015,
another health assessment was conducted in Georgia to look at
potential impacts associated with a recent morbillivirus-caused
UME and extremely high levels of PCBs t hat were identified from
previous studies. Dolphin morbillivirus titers differed between
dolphins sampled in coastal and estuarine waters, and tagging
data identified some degree of overlap between these individuals.
This study suggested that estuarine dolphins in this region may
be highly susceptible to future morbillivirus infections as a result
of elevated PCB levels and spatial overlap between coastal and
estuarine dolphins that would facilitate disease transmission (
50).
Petroleum Toxicity
In 2010, the largest marine oil spill in the history of the U.S., the
Deepwater Horizon oil spill (DWH), occurred in the northern
Gulf of Mexico (GoM). Subsequently a multidisciplinary
approach for evaluating the impacts upon cetaceans was
undertaken (
71, 72). Bottlenose dolphins were the focal cetacean
species examined due to the accessibility of dolphins in shallow
coastal and estuarine waters, and the heavy oiling in some of
those same nearshore areas. Health assessments in heavily oiled
areas, particularly Barataria Bay, Louisiana, were initiated as
part of NOAAs Natural Resource Damage Assessment (NRDA).
Veterinary clinical assessment of dolphins living within the
oil spill footprint found significant lung pathology, impaired
stress responses, high reproductive failure, and altered functional
immunity, as compared to findings from un-oiled reference
populations (35, 7375). After the DWH oil spill, an abnormally
high prevalence of lung and adrenal gland pathologies were
documented in post-mortem examinations (
73, 76). Identifying
the baseline incidence of disease in stranded dolphins and
diagnosing pathology in live dolphins through the application of
enhanced health assessment protocols was required to determine
if these findings were correlated with the recent environmental
exposure (75, 77, 78).
Determining a causal link for the multiple pathologies
obser ved post DWH oil exposure has been via a diagnosis of
exclusion; concluding the toxic effects of the oil spill as the
primary differential to both the observed path ologies and the
increased dolphin mortality (
71, 75). Other differential diagnoses
that were the potential causes of previous GoM UMEs were also
ruled out including biotoxins (79), POPs (68), and infectious
disease (45, 73, 80, 81). Successive health assessments during
2016–2018 have provided additional insight into the chronic
health effects. Longitudinal photo-ID surveys allowed estimation
of post-spill survival rate (0.80–0.85) and reproductive success
(20%), the latter was very low for this population (82, 83).
Long-term consequences from oil contamination are difficult to
assess but have been suggested in other marine mammals such
as the killer whale (Orcinus orca) and the sea otter (Enhydra
lutris nereis) (
8487). Future research efforts will aim to improve
understanding of the transgenerational or in utero exposure
effects in a ddition to the direct exposure of those animals alive
at th e time of the oil spill.
Currently there is limited knowledge of the pathophysiology
of reproductive failure in bottlenose dolphins. Improved
understanding of the normal physiological changes occurring
during gest a tion in successful pregnancies will aim to elucidate
possible mechanisms of reproductive failure and identify
abnormalities occurring during failed pregnancies. This
knowledge will be essential to help understand reproductive
challenges, not only for common bottlenose dolphins,
but also for the future management of other cetaceans,
some critically endangered, to help to understand the
reproductive challenges faced in these species and improve
future conservation management.
CAPTURE AND HANDLING
METHODOLOGY
The standard approach to capt ure small (1–5) numbers of
bottlenose dolphins in shallow waters is by encirclement with
a seine net up to 500 m long and 7 m deep (
88, 89). Shallow
water (<1.5 m), minimal currents, and a solid seafloor are
optimum for safe capture and restraint. The seine net is deployed
from a specially designed boat at high speed around the target
dolphin(s), creating a compass (Figure 2A), with well-trained
handlers distributed around the circumference to provide aid
and restraint when the dolphins contact t he net (Figure 2B)
(29). If capture occurs in deep water (>1.5 m), the net compass
can be pulled into nearby shallow water, or th e dolphins are
handled from the side of response vessels and moved onto
specially designed floating mats that are eith er towed to shallow
water or directly onto a processing vessel for sample collection
(Figure 2C). Capture of individual dolphins in waters exceeding
the depth of seine nets has been performed via tail grabs
or hoop-nets, which are placed over the head of bow-riding
bottlenose dolphins or smaller cetacean species as they surface to
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Barratclough et al. Bottlenose Dolphin Health Assessments
FIGURE 2 | Capture methodology with (A) seine net deployed from a specially designed boat creating a compass in the center of the image, with chase boats circling
outside to help contain the animals before completion of the compass and to deliver handlers to the net (two dolphins are visible inside the compass on the left side).
(B) Shallow water set, well-trained handlers distributed around the circumference of the compass to provide aid and restraint when the dolphins contact the net. (C)
Deep water set, dolphin is placed onto a floating mat and disentangled from the net for transport to the processing vessel. All photos taken under NMFS MMPA/EAS
permit No. 18786-03.
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Barratclough et al. Bottlenose Dolphin Health Assessments
breathe (8890). Once dolphins are s afely restrained, veterinary
examinations and sampling are performed.
VETERINARY PROCESSING
Current health assessment examinations require collaboration
among scientists from multiple disciplines and veterinary
specialties to obtain the maximum amount of information from
a single snapshot in time while the animal is in-hand. The
development of veterinary field techniques was enhanced by the
successful management of dolphins in human care. Sampling
varies according to research questions, but typically a suite of
baseline data are collected to maximize knowledge obtained from
a single veterinary exam (Table 2) (
91). Ensuring a standardized
approach to highlight the importance of inter-lab comparability
and sharing information between multiple institutions has
been paramount in the success of developing field collection
methodologies and subsequent sample analysis procedures (
32,
113). As described below, additional field procedures have been
incorporated over the decades as technology, field techniques,
and analytical assays have advanced, and as management needs
have evolved.
Determination of reproductive status (e.g., pregnancy , ovarian
activity, or testis size as an indicator of sexual maturity) using
diagnostic ultrasound was first applied in Sarasota Bay in
1989 (26, 114). Full-body ultrasound has subsequently been
proven to be an invaluable, rea l-time tool during dolphin
health assessments, pioneered by the National Marine Mammal
Foundation and the U.S. Navy Marine Mammal Program
(Figure 3) (
77, 97, 101103). In addition, pregnancy may also
be diagnosed remotely by using blubber biopsy hormone levels
(115, 116). In some cases, post-release visual monitoring and
photographic-identification (photo-ID) have allowed researchers
to track the outcome of the pregnancy (that was determined by
ultrasound or remotely) and determine whether a viable calf was
produced (82, 116, 117).
A holistic approach of including dietary assessment into
the health exam along with urinalysis, blood (Figure 4), and
blubber sampling can aim to elucidate underlying causes
of health abnormalities. In the field, urinary catheterization
has enabled comparison with dolphins in managed care and
further developed the understanding of the development of
renal pathology in dolphins, especially when differences in
diets have been considered (
91, 9799). Important ecological
perspectives can be obtained from diet a ry assessments, along
with information regarding prey availability and potential shifts
in environmental pressure affecting the ecosystem (118121).
Further research is needed in this area to develop a more
standardized nutritional status indicator which can integrate
multiple measures. This could be used for example to improve
understanding of the effects of prey instability or environmental
stressors (122).
Electronic taggi ng technology to assess individual movement
or habitat use has rapidly advanced over the past 40 years so that
now small satellite-linked tags can be attached via a single-pin to
the dorsal fin and have minimal to no long-term effects on the
tagged individual (
70, 111). These tags provide fine-scale data on
individual animal movements for several months, post-rele ase,
and can provide additional insight into the cause of health effects
identified during the veterinary examination (37, 3 8, 117). The
movement pattern data from these electronic tags can also be
used to conduct follow-up monitoring to assess individual animal
health, survival, reproductive success, habitat use, and exposure
to th reats (
82).
MULTIDISCIPLINARY APPROACHES FOR
ASSESSING POPULATION HEALTH
Utilizing a multidisciplinary approach to combine clinical
veterinary knowledge with epidemiological analyses and
population modeling enables long-term forecasting of population
trajectories (36). In UMEs, modeling to estimate mortality based
on the number of stranded carcasses can provide insight into
the immediate losses to the population (71, 123125). However,
integration of available health information and veterinary
interpretation of sublethal, chronic conditions, which are likely
to influence long-term survival and reproductive potential, can
provide a more accurate interpretation of the likely long-term
impacts on t he population (
36). Aside from impacts from acute
events such as oil spills, modeling has been used to simulate
the likely population-level consequences from sublethal effects
of chronic contaminant exposure (60, 67). Estimation of long-
term population effects resulting from mortality or morbidity
events is critical to inform restoration or recovery plans, and
also to appreciate the magnitude of the impact of UMEs on
population numbers or of environmental contaminants on the
surrounding ecosystem. A dvances in modeling application to
marine mammal stock assessments will greatly shape the future
of marine mammal conservation.
ADVANCES IN TECHNOLOGY AND
CONSIDERATIONS FOR ANIMAL
WELL-BEING
Dolphin health assessments provide fine-scale i nformation on
individual animals that can be extrapolated to evaluate overall
population health. While much can be learned from hands-
on health assessments, a major driver of current research is
to develop techniques to obtain maximum health assessment
information from remote sampling and observations. The
methodology for safely handling, sampling, and releasing
dolphins is continually evolving to minimize t h e risk to both the
dolphins and researchers, as well as maximize the data collected.
However, health assessments are still expensive, logistically
challenging, have limited target populations, and there is an
inherent risk when handling large animals (
126, 127). The
development of remote sampling te chnologies is essential to
build upon th e data collected during hands-on studies and to
expand our ability to efficiently and comprehensively assess the
health of dolphin populations beyond nearshore waters, as well
as the health of larger, less tractable cetacean species.
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Barratclough et al. Bottlenose Dolphin Health Assessments
TABLE 2 | List of veterinary processing sample collection from hands-on physical examinations during common bottlenose dolphin health assessments.
Procedure Description Use References
Blood sample
(Figure 4)
Obtained from the periarterial rete on the
ventral aspect of the tail fluke
Biochemistry
Hematology
Blood gas analysis
Endocrinology
Immunology
Serology
Genetics
(
23, 29, 30, 74, 9193)
Surgical biopsy Full thickness wedge biopsies of skin and
blubber are routinely taken via an inverted
“L block under local anesthesia from the
left lateral body wall caudal to the dorsal fin
Genetic population structure (skin)
Foraging ecology (skin)
Chemical contaminants (blubber)
Hormone levels (blubber)
Microbiome
(
31, 33, 49, 57, 9496)
Urinalysis Bladder catheterization Renal function assessment
Dietary analysis
(
91, 9799)
Tooth extraction Single tooth extracted under local
anesthesia
Age determination (
17, 100)
Ultrasonography
(Figure 3)
Thoracic and abdominal internal
assessment
Lung pathology
Reproductive Assessment
Full abdominal exam including renal
assessment
Blubber thickness
(
77, 97, 101103)
Electrocardiography
(Figure 6)
Adapted field use in and out of water Cardiac assessment (
104)
Morphometrics
(Figure 7)
Standardized full body measurements:
lengths, girths, weight
Assess body condition and growth rates (
105)
Auditory evoked
potential
Portable unit adapted for field assessment
audiograms
Assess hearing range and sensitivity (
106)
Lesion biopsy Sample of abnormal skin lesions e.g., pox
or freshwater lesions
Histopathology (
57, 93)
Blow analysis
(Figure 5)
Exhaled breath vapor Pathogen and hormonal analysis
Metabolites
Respiratory function testing
(
107, 108)
Microbiology Swabs/culture plates from oral respiratory
or genital orifices
Bacteriology
Virology
(
109)
Freeze brand Dorsal Fin Identification (
110)
Feces and urine
collection
Swabs or catheter Biotoxin analysis (
46)
Skin biopsy
Electronic and/or
roto tagging
Skin sample from biopsy or during dorsal
fin tagging
Genetics, sex, stable isotopes identification
Ranging patterns reproductive status
Survival
(
70, 111, 112)
Application of new technologies to improve remote sampling
opportunities and maximize information obtained from cetacean
health assessments is pushing the boundaries of current marine
mammal science. Blow samples previously established when in-
hand (Figure 5) can now be obtained remotely utilizing UAVs
(unmanned aerial vehicles). Drones can be used to obt ain
aerial images to perform photogrammetry to assess health
via body condition in large whales unable to be examined
physically (107, 128). Drones can also be used in cetacean
disentanglement approaches to provide accurate assessment of
exact entanglement points and facilitate more informed decisions
on disentanglement methodology. Thermography has been used
to assess dolphin dorsal fin temperatures, as a measure of
individual health status representing appropriate integumentary
thermoregulation (
129), and now thermal imaging from drones
is being developed to apply to large whale health assessments.
Remote temperature assessment will be of increased value in
the future when potential climate change impacts could result
in cetaceans being exposed to higher or lower environmental
temperatures (
130132).
Historically, the st a nd ard method of estimating the age
in dolphin health assessments is via tooth extraction under
local anesthesia and counting the growth layer groups present
on longitudinal section (17). Dental radiography has been
pioneered in an effort to replace the tooth extraction technique,
and validation of the technique is ongoing. Bone density
assessment has also been explored as a possible aging method,
however correlation with age across the entire lifespan was
limited (
133). A promising new methodology is the use of
pectoral flipper radiography to assess bone maturation (134).
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Barratclough et al. Bottlenose Dolphin Health Assessments
FIGURE 3 | Ultrasound examination of a lymph node on board the veterinary examination and sampling vessel (MMPA ESA Permit No. 18786-03).
FIGURE 4 | Blood sample collection from the peri-arterial rete on the ventral aspect of the tail fluke (MMPA ESA Permit No. 18786-01).
The dolphin pectoral flipper displays both hyperphalangy and
paedomorphosis enabling this method to be applied throughout
the entire lifespan due to the predictable chronological osteogenic
changes occurring to the metacarpal and phalangeal bones. This
non-invasive technology could facilitate age estimation for older
animals, replacing tooth extraction.
Additional biological information from remote biopsy dart
sampling is expanding on the knowledge gained from each
individual sample (
135). Currently, sex and population structure
of the animal can be determined from genetic analyses of
skin (112), and contaminant concentrations and stress and
reproductive hormone levels can be measured from blubber
biopsy (33, 116, 136). Present efforts are working toward using
skin to assess the epigenetics of the individual to give an
estimation of age (137). The NMMF are expanding on this even
further in line with recent human advancements to provide an
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Barratclough et al. Bottlenose Dolphin Health Assessments
FIGURE 5 | Exhaled breath sample collection for cytology (MMPA ESA Permit No. 18786-03).
FIGURE 6 | ECG leads attached during sampling and processing to closely
monitor the dolphin’s heart rate and assess cardiac function (MMPA ESA
Permit No. 18786-03).
indication of biological age (138). This emerging technology
could provide a means to assess increased environmental
pressure or poor health status (
139141).
FIGURE 7 | Dolphin suspended in a stretcher for weight measurement via
load cell on board the veterinary processing vessel. This image was published
with permission of MMPA ESA Permit No. 18786-01 for the identifiable
individuals in the image.
Remotely deployed suction cup satellite-linked tags c an
provide short-term (<24 h) data on bioenergetics, respiratory
measures and cardiac data (
142, 143). An additional remote
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Barratclough et al. Bottlenose Dolphin Health Assessments
tool in development is the use of remotely attached single-
pin satellite-linked tags. These techniques will be particularly
useful in marine mammals where capture-release is impractical
due to size, species intolerance to handling or cost restraints.
Future research aims to combine different disciplines to expand
scientific knowledge further and inter-species application of new
technologies, for example, studying acoustic communication as a
proxy to changes in health status (
144, 145).
DISCUSSION
Health assessments with an epidemiological focus can aim
to understand the pathophysiology of disease and interpret
the demographic, anthropogenic, and ecological pressures
contributing to individual disease susceptibility (
146).
Extrapolating from individual health assessments to accurately
understand population health status, requires a strategic
epidemiological approach (
41, 147, 148). Inte grat ion of post-
mortem examinations within the health assessment framework
can provide additional projections from both diagnostic and
scientific perspectives aiming to contribute to identifying the
underlying cause of mortality and also predicting the future
impacts on the population. Performing pro-active marine
mammal health assessment examinations allows an opportunity
to examine population health under natural environmental
conditions, as opposed to during a mass stranding or UMEs.
This baseline knowledge of population health status can
aid understanding of post-mortem examinations during
UMEs and ultimately aim to drive mitigation strategies for
successful conservation and species management. Health
assessments are facilitating a pro-active approach to marine
mammal conservation in addition to a reactive response
to UMEs.
The primary role of wildlife veterinarians is shifting
from management of high mortality disease epidemics to
preventative management and mitigation of anthropogenic
causes of mortality (7). Unlike terrestrial species where mass
mortalities garner a lot of public attention, marine species can die
in large numbers, and the impact can go unnoticed (149). Sharing
information regarding health and thre a ts to local populations
can facilitate public interest in coastal and estuarine bottlenose
dolphin populations. Increased public awareness and reporting
of marine mammals in distress can aid understanding of the
current global changes and interactions between humans and
wildlife, dictating the efforts required to conserve future marine
populations glob ally .
Continuous monitoring of specific populations over time has
the benefit of providing both cross-sectional analyses on an
annual basis, as well as longitudinal analysis over several decades.
Collecting health data consistently across multiple populations
facilitates an understanding of geographic variability, can help
to establish reference ranges that are generalizable across
populations, and can provide a gradient of stressor exposures
for cross-sectional or correlational studies. The combined
approaches support a robust framework for epidemiological
studies to investigate the causal factors for disease. The collection
of decades of archival samples from multiple populations
facilitates retrospective studies to discern between sublethal
pathogen levels, assess temporal and spatial t rends, and elucidate
the intricacies of disease susceptibility at a population health
level. For example, dolphins in Florida are frequently exposed
to various levels of K. brevis red tides (
150, 151). Examining
samples from 1994 to 2003 enabled knowledge of baseline levels
of brevetoxin in the dolphin population and demonstrated t hat
dolphin carcasses not associated with large scale mass mortality
could also contain comparably high levels of brevetoxins (79).
This information is invaluable for future research when the
duration and intensity of red tides in Florida appears to be
increasing ( 152, 153).
An additional benefit of long-term studies and sample
archives generated by health assessments is th e ability to a pply
new technology and diagnostic tests retrospectively enabling
advanced monitoring of he alth changes over time. Identification
of emerging infe cti ous causes of mortality such as cetacean
morbillivirus requires continued monitoring of levels of herd
immunity over long periods of time (
81). Sample archives can
be used to est ablish normal levels and improve understanding
of emergence, dynamics, and history of pathogens such as
morbillivirus or retrospective analysis of brucella (23, 30, 73).
Established baseline data c an aid interpretation of normal
or increased prevalence of positive antibody titers within
the population.
Stress of Health Assessments (Alternative
Perspective)
Prior to considering health assessments for a project, there should
be an in-depth discussion of research priorities and if the short-
term capturing of individual dolphins is truly the best tool to
address the goals of the study. The value of the data obtained from
health assessments of free-ranging dolphins needs to be balanced
against the potential stress and risk to the individual from the
capture, handling, and sampling process (
154157). The stress
of capture often influences baseline dat a such as blood cortisol
and a ldosterone levels (158). If baseline hormone values are the
focus of a study, remote biopsy sampling of blubber can give
an accurate indication of baseline stress hormone levels without
the elevation caused by the stress of capture (
159). However,
the adrenal response to a stimulus such as capture may be of
interest (35), and capture-release studies enable the evaluation
of an individual’s hypothalamic pituitary axis and whether or
not t h e animal is capable of mounting an appropriate stress
response (75).
In general, the molecular physiologica l response to the stress
of the veterinary examination is well-documented across species;
it is transient and the valuable information obtained from the
exam typically offsets any acute stress that may be caused.
Based on ongoing population monitoring, long-term health
consequences of repeated captures have not been found for
individuals examined as many as 15 times or more (160).
Ensuring capture and restraint are relatively brief and as calm
as possible is important, as it has been shown that short
holding times do not induce a significant neuroendocrine st ress
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Barratclough et al. Bottlenose Dolphin Health Assessments
response (154). An experienced team and ongoing training
opportunities among organizations, in both managed and
free-ranging dolphin populations, promote this high standard
of assessment.
Globally, free-ranging dolphins are exposed to a wide range of
anthropogenic stressors including environmental contaminants,
acoustic shipping disturbances, fisheries interactions, habitat
degradation or even loss altogether, exposure to biotoxins,
climate disruption, and human interactions (
161168).
Variability in the level of anthropogenic stress occurs across
geographical locations. Health assessments provide a portal
into the individual and population health status to facilitate
understanding of ecosystem health, and drive conservation
and management decisions. The cost of each individual health
assessment is offset by the biological information obtained
from each examination. Combining these data with additional
stranding information, such as post-mortem examinations
and field observations, helps to improve understanding and
interpretation of biological health assessment data from a
conservation perspective.
International Perspective
Biologists and veterinarians from around the world have had
the opportunity to part ak e in dolphin health assessments across
U.S. waters with the aim of facilitating capacity building
for global cetacean conservation (
92). Established dolphin
health parameter reference ranges enable comparison between
international locations in an effort to tease apart the healt h effects
of different stressors. Throughout the majority of the world,
health monitoring of dolphins primarily involves post-mortem
exams of stranded cetaceans in Europe, physical exams during
translocations such as out-of-habitat animals in Asia and South
America such as the recent intervention in Bolivia, or during
remote biopsy sampling in photo-identific ation studies in the
Mediterranean (
169173).
Increased international collaboration is essential for
mitigating conservation crises and aiming to reduce the
number of marine mammals becoming extinct such as the recent
loss of the Yangtze River dolphin, the baiji (Lipotes vexillifer), or
the high-risk Mediterranean monk seal (Monachus monachus)
and vaquita porpoise (Phocoena sinus) (
4, 174). Knowledge of
capture techniques gained from dolphin he alth assessments in
the U.S. has been applied to alternative species conservation
approaches, such as with the vaquita, in an effort to temporarily
remove animals from a d angerous habitat and relocate them
to a protected environment (175). Marine mammal stranding
networks exist world-wide with varying capacity dependent
on funding, degree of public interest, number of strandings
per year, facilities available, and the extent of inter-agency
cooperation (176). Sharing knowledge and organizational
structure from locations with financial support can aid capacity
building in areas where marine mammal stranding networks are
currently limited.
From examining dolphin communication to understanding
energetics, lung capacity, respiratory metabolomics, and
the mechanisms involved in deep diving physiology, health
assessments are contributing to advancing scientific knowledge
(
108, 177179). S c ientists have improved our understanding of
dolphin anatomy and physiology by observing natural behavior
during health assessments and monitoring activity and behavior
post handling. Collaboration among scientists, veterinarians, and
biologists at different health assessments enables a synergistic
approach to understanding marine mammal health.
Universally, comprehensive cetacean conservation benefits
from an integration of all available cetacean assessment
techniques; hands on veterinary health assessments, post-
mortem examinations, photo-ID surveys, and field observer
data. Ideally a collaborative approach among scientists,
biologists, fishers, local community members, and government
officials would achieve maximum success from a management
perspective. Incre ased discussion will aim to improve future
inter-disciplinary approaches and address anthropogenic
impacts on marine mammals.
CONCLUSION
The advancement of common bottlenose dolphin health
assessments, transitioning from initial population assessments to
endangered species conservation applications has occurred
over several decades, expanding knowledge of marine
mammal medicine and science. As veterinary standards for
dolphins in human care have evolved, so have the standard
protocols for handling and monitoring free-ranging dolphins,
and diagnostics such as clinicopathology, ultrasonography,
radiography, electrocardiography, respirometry, microbiology,
and morphometry (
29, 32, 43, 77, 104, 108, 180, 181). Dolphin
health assessments are a valuable tool to extrapolate from the
individual to understanding both population and ecosystem
health. Combining scientific investigation with longitudinal
population monitoring over multiple dolphin populations
provides information to facilitate informed decisions regarding
conservation, regulations, and protection of marine mammals.
Social education re garding the presence, longevity, and
residence of bottlenose dolphins also allows t he public to engage
with the species and appreciate their intrinsic value within the
ecosystem; dolphins share the same habitat and are impacted
by some of the same stressors as loc al human communities.
Citizen science and public interest peaks during UMEs when
multiple carcasses are observed on the beaches in a short time
frame. This is an opportunity to engage with people to highlight
the environmental pressures faced by these apex preda tors and
explain the anthropogenic impacts on these charismatic species.
An interdisciplinary and interagency approach is needed to
fully understand the complexities of the challenges faced by
marine mammals. Shifts in the tide of social attitudes, interests,
regulations, and funding will have consequences to marine
mammal populations both free-ranging as well as managed.
Understanding the current global challenges and increasing
human a nd wildlife interactions will dictate the mitigation efforts
required to conserve future marine populations. Remaining at
the cutting edge of s cience and advancing the field will aim
to facilit at e conservation of marine mammal populations for
future generations.
Frontiers in Veterinary Science | www.frontiersin.org 12 December 2019 | Volume 6 | Article 444
Barratclough et al. Bottlenose Dolphin Health Assessments
AUTHOR CONTRIBUTIONS
All authors contributed to the past, present, or future
development of dolphin health assessments. AB and RW
completed the manuscript writing with significant contributions
from LS and CS. All authors provided edits and contributed to
the fina l submitted manuscript.
FUNDING
Waiver received for publication fees to Dr. Randy Wells.
ACKNOWLEDGMENTS
Dolphin health assessments would not have been possible
without the vast scientific collaboration from a large global team
of scientific colleagues, research assistants, post-docs, graduate
students, and volunteers. The auth ors would like to thank
Larry Fulford, who was the dolphin catcher for the majority
of health assessments in the southeastern U.S. for 35 years.
The authors would also like to thank the significant program
support for each health assessment in addition to NOAAs Marine
Mammal Health and Stranding Response Program and the Office
of Naval Research. In addition, significant program support
for health assessments has been received from the Chicago
Zoological Society, NOAAs Fisheries Service, National Science
Foundation, Environmental Protection Agency, Marine Mammal
Commission, Dolphin Quest, Inc., Disney’s Animal Programs,
Earthwatch, Inc., and the International Whaling Commission.
The authors also wish to thank the involvement of the U.S. Navy
Marine Mammal Program. This manuscript was made possible in
part by a grant from The Gulf of Mexico Research Initiative. The
scientific results and conclusions, as well as any views or opinions
expressed herein, are those of the authors and do not necessarily
reflect the views of NOAA. Dolphin health assessments were
conducted under various NMFS research permits for the projects
described. This is scientific contribution 246 of the National
Marine Mammal Foundation.
REFERENCES
1. Gulland FMD, Hall AJ. Is marine mammal health deteriorating? Trends in
the global reporting of marine mammal disease. EcoHealth. (2007) 4:135–50.
doi: 10.1007/s10393-007-0097-1
2. Myers N, Mittermeier RA, Mittermeier CG, Da Fonseca GA, Kent J.
Biodiversity hotspots f or conservation priorities. Nature. (2000) 4 0 3:85 3 .
doi: 10.1038/35002501
3. Aguirre AA, Ostfeld RS, Tabor GM, House C, Pearl MC. Conservation
Medicine: Ecological Health in Practice. New York, NY: Oxford University
Press (2002).
4. Reynolds JE, Marsh H, Ragen TJ. Marine mammal conservation. Endang
Species Res. (2009) 7:23–8. doi: 10.3354/esr0017 9
5. Wikelski M, Cooke SJ. Conservation physiology. Trends Ecol Evol. (2006)
21:38–46. doi: 10.1016/j.tree.2005.10.018
6. Daszak P, Cunningham AA, Hyatt AD. Emerging infectious diseases of
wildlife–threats to biodiversity and human health. Science. (2000) 287:443–9.
doi: 10.1126/science.287.5452.443
7. Deem SL, Karesh WB, Weisman W. Putting theory into practice:
wildlife health in conservation. Conserv Biol. (2001) 15:1224–33.
doi: 10.1046/j.1523-1739.2001.00336.x
8. Iucn. The IUCN Red List of Threatened Species. Version 2019-2. (2019).
Available online at: http://www.iucnredlist.org
9. Taylor BL, Martinez M, Gerrodette T, Barlow J, Hrovat YN. Lessons from
monitoring trends in abundance of marine mammals. Mar Mamm Sci.
(2007) 23:157–75. doi: 10.1111/j.1748-7692.2006.00092.x
10. Davidson AD, Boyer AG, Kim H, Pompa-Mansilla S, Hamilton MJ, Costa
DP, et al. Drivers and hotspots of extinction risk in marine mammals. Proc
Natl Acad Sci USA. (2012) 109:3395– 40 0. doi: 10 .10 73 /pnas.1121 46 91 0 9
11. Asper ED, Odell DK. Bottlenose Dolphin Local Herd Monitoring: Captive
Marking, Collection of Biological Data, and Follow-Up Observations of
Marked Animals. Final Report to National Marine Fisheries Service, Contract
NA79 -6 A-C-00027. Hubbs/Sea World Research Institute (1980).
12. Odell DK, Asper ED. Distribution and movements of freeze-branded
bottlenose dolphins in the Indian and Banana Rivers, Florida. In:
Leatherwood S, Reeves R, editors. The Bottlenose Dolphin. Elsevier (1990).
p. 515–40.
13. Solangi MA, Dukes G E. Atlantic Bottlenose Dolphin, Tursiops Truncatus
Herd Studies in the Mississippi Sound, USA: Capture, Freeze Marking and
Biological Sampling. Biloxi, MS: Marine Animal Productions (1983).
14. Irvine B, Wells RS. Results of attempts to tag atlantic bottlenosed dolphins
(Tursiops truncatus). Biol Syst. (1972) 13:1–5.
15. Irvine AB, Scott M, Wells RS, Kaufman JH. Movements and activities of
the Atlantic bottlenose dolphin, Tursiops truncatus, near Sarasota, Florida.
Fishery Bull. (1981) 79:135–43.
16. Wells RS, Scott MD, Irvine AB. The social structure of free-ranging
bottlenose dolphins. In: Genoways HH, editor. Current Mammalogy. New
York, NY: Springer (1987). p. 247–305.
17. Hohn AA, Scott MD, Wells RS, Sweeney JC, Irvine AB. Growth
layers in teeth from known-age, free-ranging bottlenose dolphins.
Mar Mamm Sci. (1989) 5:315–42. doi: 10.1111/j.1748-7692.1989.
tb00346.x
18. Wells RS, Scott MD. Estimating bottlenose dolphin population parameters
from individual identification and capture-release techniques. Rep Int Whal
Commission. (1990) 12:40 7 –1 5.
19. Duffield DA, Wells RS. The combined application of chromosome, protein
and molecular data for the investigation of social unit structure and dynamics
in Tursiops truncatus. In: Hoelzel AR, editor. Genetic Ecology of Whales and
Dolphins. Cambridge, UK (1991). p. 155–69.
20. Becker PR, Wilkinson DM, Lillestolen TI. Marine Mammal Health and
Stranding Response Program: Program Development Plan. NOAA Technical
Memorandum NMFS-OPR-94-2, National Oceanic and Atmospheric
Administration, Silver Spring, MD (1994).
21. Geraci JR. Clinical Investigation of the 1987-88 Mass Mortality of Bottlenose
Dolphins Along the US Central and South Atlantic Coast. Final report to
National Marine Fisheries Service and US Navy Office of Naval Research and
Marine Mammal Commission (1989).
22. Lipscomb TP, Schulman FY, Moffett D, Kennedy S. Morbilliviral disease
in Atlantic bottlenose dolphins (Tursiops tr un catus) from the 1987-
1988 epizootic. J Wildl Dis. (1994) 30:567–71. doi: 10.7589/0090-3558-30.
4.567
23. Duignan PJ, House C, Odell DK, Wells RS, Hansen LJ, Walsh MT, et
al. Morbillivirus infection in bottlenose dolphins: evidence for recurrent
epizootics in the western Atlantic and Gulf of Mexico. Mar Mamm Sci. (1996)
12:499–515. doi: 10.1111/j.1748-7692.1996.tb00063.x
24. Hansen LJ, Wells RS. Bottlenose Dolphin Health Assessment: Field Report
on Sampling Near Beaufort, North Carolina, During July, 1995. NOAA
Technical Memorandum NMFS-SEFSC-382 (1996).
25. Mclellan WA, Friedlaender AS, Mead JG, Potter CW, Pabst DA. Analysing
25 years of bottlenose dolphin (Tursiops truncatus) strandings along
the Atlantic coast of the USA: do historic records support the coastal
migratory stock hypothesis? J Cetacean Res Manag. (2002) 4:297–
304. Available online at: https://pdfs.semanticscholar.org/1ec1/
4350253d6e3276a4d1d0021959b20fc59706.pdf
Frontiers in Veterinary Science | www.frontiersin.org 13 December 2019 | Volume 6 | Article 444
Barratclough et al. Bottlenose Dolphin Health Assessments
26. Sweeney JC, Stone LR, Townsend FI, Casper D, Hansen L. Population Health
Assessment on Tursiops truncatus From Matagorda Bay, Texas, Following a
Mortality Event, 1992. NOAA-NMFS, SEFSC Contribution MIA-92/93-41,
10 pp + appendices (1992).
27. Schwacke LH, Twiner MJ, De Guise S, B almer BC, Wells RS, Townsend FI,
et al. Eosinophilia and biotoxin exposure in bottlenose dolphins (Tursiops
truncatus) from a coastal area impacted by repeated mortality events.
Environ Res. (2010) 110:548–55. doi: 10.1016/j.envres.2010.05.003
28. Lohoefener R, Hoggard W, Mullin K, Ford R, Benigno J. Studies of Mississippi
Sound Bottlenose Dolphins: Estimates of Bottlenose Dolphin density in
Mississippi Sound From Small Boat Surveys. Pascagoula, MS: National Marine
Fisheries Service (1990).
29. Wells RS, Rhinehart HL, Hansen LJ, Sweeney JC, Townsend FI,
Stone R, et al. Bottlenose dolphins as marine ecosystem sentinels:
developing a health monitoring system. EcoHealth. (20 04 ) 1:246–54.
doi: 10.1007/s10393-004-0094-6
30. Rowles T, Schwacke L, Wells R, S aliki J, Hansen L, Hohn A, et al. Evidence of
susceptibility to morbillivirus infection in cetaceans from the United States.
Mar Mamm Sci. (2011) 27:1–19. doi: 10.1111/j.1748-7692.2010.00393.x
31. Hansen LJ, Schwacke LH, Mitchum GB, Hohn AA, Wells RS, Zolman
ES, et al. Geographic variation in polychorinated biphenyl and
organochlorine pesticide concentrations in the blubber of bottlenose
dolphins from the US Atlantic coast. Sci Total Environ. (2004) 319 :14 7 –72 .
doi: 10.1016/S0048-9697(03)00371-1
32. Schwacke LH, Hall AJ, Townsend FI, Wells RS, Hansen LJ, Hohn AA, et
al. Hematologic and serum biochemical reference intervals for free-ranging
common bottlenose dolphins (Tursiops truncatus) and variation in the
distributions of clinicopathologic values related to geographic sampling site.
Am J Vet Res. (2009) 70:973–85. doi: 10.2460/ajvr.70.8.973
33. Kucklick J, Schwacke L, Wells R, Hohn A, Guichard A, Yordy J, et al.
Bottlenose dolphins as indicators of persistent organic pollutants in the
western North Atlantic Ocean and northern Gulf of Mexico. Environ Sci
Cons. (2011) 45:4270–7. doi: 10.1021/es1042244
34. Bossart GD, Fair P, Schaefer AM, Reif JS. Health and Environmental Risk
Assessment Project for bottlenose dolphins Tursiops truncatus from the
southeastern USA. I Infectious diseases. Dis Aquat Org. (2017) 125:141–53.
doi: 10.3354/dao03142
35. Schwacke LH, Smith CR, Townsend FI, Wells RS, Hart LB, Balmer BC, et al.
Health of common bottlenose dolphins (Tursiops truncatus) in Barataria Bay,
Louisiana, following the deepwater horizon oil spill. Environ Sci Technol.
(2014) 48:93–103. doi: 10.1021/es403610f
36. Schwacke LH, Thomas L, Wells RS, Mcfee WE, Hohn AA, Mullin KD, et
al. Quantifying injury to common bottlenose dolphins from the Deepwater
Horizon oil spill using an age-, sex-and class-structured population model.
Endang Species Res. (2017) 33:265–79. doi: 10.3354/ esr00777
37. Mullin KD, Mcdonald T, Wells RS, Balmer BC, Speakman T, Sinclair
C, et al. Density, abundance, survival, and ranging patterns of common
bottlenose dolphins (Tursiops truncatus) in Mississippi Sound following
the Deepwater Horizon oil spill. PLoS ONE. (2017) 12:e018626 5.
doi: 10.1371/journal.pone.0186265
38. Balmer B, Zolman E, Rowles T, Smith C, Townsend F, Fauquier D,
et al. Ranging patterns, spatial overlap, and association with dolphin
morbillivirus exposure in common bottlenose dolphins (Tursiops truncatus)
along the Georgia, USA coast. Ecol Evol. (2018) 8:128 90 –4 . doi: 10.1002/ece
3.4727
39. Garrison LP, Hohn AA, Hansen LJ. Seasonal Movements of Atlantic Common
Bottlenose Dolphin Stocks Based on Tag Telemetry Data. Southeast Fisheries
Science Center, Protected R esources and Biodiversity Division (2017). p. 75.
40. Scott GP, Burn DM, Hansen LJ. The Dolphin Dieoff: Long-Term Effects and
Recovery of the Population. IEEE (1998). p. 819–2 3.
41. Rowles TK, Schwacke LH, Hall AJ, Barbieri M. Population health assessment
study design. In: Gulland FMD, Whitman KL, Dierauf LA, editors. CRC
Handbook of Marine Mammal Medicine. CRC Press (2018). p. 813–22.
42. Goldstein JD, Reese E, Reif JS, Varela RA, Mcculloch SD, Defran RH,
et al. Hematologic, biochemical, and cytologic findings from apparently
healthy atlantic bottlenose dolphins (Tursiops truncatus) Inhabiting the
Indian River Lagoon, Florida, USA. J Wildl Dis. (2006) 42:447–54.
doi: 10.7589/0090-3558-42.2.447
43. Reif JS, Fair PA, Adams J, Joseph B, Kilpatrick DS, Sanchez R, et al. Evaluation
and comparison of the health status of Atlantic bottlenose dolphins from the
Indian River Lagoon, Florida, and Charleston, South Carolina. J Am Vet Med
Ass. (2008) 233 :29 9– 30 7. doi: 10 .24 60 /javma.233.2.299
44. Reif JS, Schaefer AM, Bossart GD, Fair PA. Health and environmental
risk assessment project for bottlenose dolphins Tursiops truncatus from
the southeastern USA. II Environment al aspe cts. Dis Aquat Org. (201 7)
125:155–66. doi: 10.3354/dao03143
45. Litz JA, Baran MA, Bowen-Stevens SR, Carmichael RH, Cole grove KM,
Garrison LP, et al. Review of historical unusual mortality events (UMEs)
in the Gulf of Mexico (1990-2009): providing context for t he multi-ye ar
northern Gulf of Mexico cetacean UME declared in 2010. Dis Aquat Org.
(2014) 112:161–75. doi: 10.3354/dao02807
46. Twiner MJ, Flewelling LJ, Fire SE, Bowen-Stevens SR, Gaydos
JK, Johnson CK, et al. Comparative analysis of three brevetoxin-
associated bottlenose dolphin (Tursiops truncatus) mortality events
in the Florida panhandle region (USA). PLoS ONE. (2012) 7:e42974.
doi: 10.1371/journal.pone.0042974
47. Gulland FMD, Haulena M, Fauquier D, Langlois G, Lander ME, Zabka T, et
al. Domoic acid toxicity in Californian sea lions (Zalophus californianus):
clinical signs, treatment and survival. Vet Rec. (2002) 150:475–80.
doi: 10.1136/vr.150.15.475
48. Balmer BC, Wells RS, Nowacek SM, Nowacek DP, Schwacke LH, Mclellan
WA, et al. 157 Seasonal abundance and distribution patterns of common
bottlenose dolphins (Tursiops truncatus) near St. Joseph Bay, Florida, USA.
J Cetacean Res Manage. (2008) 10:157–67. Available online at: https://uncw.
edu/mmsp/documents/balmer_et_al_2008.pdf
49. Vollmer NL, Rosel PE. A review of common bottlenose dolphins (Tursiops
truncatus truncatus) in the northern Gulf of Mexico: population biology,
potential threats, and management. Southeastern Natural. (2013) 12:1–44.
doi: 10.1656/058.012.m601
50. Balmer B, Mcdonald T, Hornsby F, Adams J, Allen J, Barleycorn A, et al.
Long-term trends in a northern Gulf of Mexico common bottlenose dolphin
(Tursiops truncatus) population in the wake of the Deepwater Horizon oil
spill. J Cetacean Res Manage. (2018) 18:1–9. Available online at: https://
www.researchgate.net/profile/Brian_Balmer/publication/328076117_
Long-term_trends_in_a_northern_Gulf_of_Mexico_common_bottlenose_
dolphin_Tursiops_truncatus_population_in_the_wake_of_the_Deepwater_
Horizon_oil_spill/links/5bb6324e4585159e8d86662f/Long-term-trends-
in-a-northern-Gulf-of-Mexico-common-bottlenose-dolphin-Tursiops-
truncatus-population-in-the-wake-of-the-Deepwater-Horizon-oil-spill.
pdf
51. Fauquier D, Kinsel M, Dailey M, Sutton G, Stolen M, Wells R, et al.
Prevalence and pathology of lungworm infection in bottlenose dolphins
Tursiops truncatus from southwest Florida. Dis Aquat Org. (2009) 88:85–90.
doi: 10.3354/dao02095
52. Bogomolni AL, Pugliares KR, Sharp SM, Patchett K, Harry CT, Larocque
JM, et al. Mortality trends of stranded marine mammals on Cape Cod
and southeastern Massachusetts, US A, 2000 to 2006. Dis Aquat Org. (2010)
88:143–55. doi: 10.3354/dao02146
53. Wells RS, Allen JB, Lovewell G, Gorzelany J, Delynn RE, Fauquier DA, et
al. Carcass-recovery rates for resident bottlenose dolphins in Sarasota Bay,
Florida. Mar Mamm Sci. (2015) 31:355–68. doi: 10.1111/mms.12142
54. Moore MJ, Mclellan WA, Daoust PY, Bonde RK, Knowlton AR . Right whale
mortality: a message from the dead to the living. In: Kraus SD, Rolland R,
editors. The Urban Whale: North Atlantic Right Whales at the Crossroads.
Cambridge, MA: Harvard University Press (2007).
55. Martineau D, Béland P, Desjardins C, Lagacé A. Le vels of organochlorine
chemicals in tissues of beluga whales (Delphinapterus leucas) from the
St. Lawrence Estuary, Quebec, Canada. Environ Contamin Toxic. (1987)
16:137–47. doi: 10.1007/BF01055795
56. Kuehl DW, Haebler R. Organochlorine, organobromine, metal, and selenium
residues in bottlenose dolphins (Tursiops trun catus) collected during an
unusual mortality event in the Gulf of Mexico, 1990. Arch Environ Contam
Toxicol. (1995) 28:494–9. doi: 10.1007/BF00211632
57. Wells RS, Tornero V, Borrell A, Aguilar A, Rowles TK, Rhinehart HL,
et al. Integrating life-history and reproductive success data to examine
potential relationships with organochlorine compounds for bottlenose
Frontiers in Veterinary Science | www.frontiersin.org 14 December 2019 | Volume 6 | Article 444
Barratclough et al. Bottlenose Dolphin Health Assessments
dolphins (Tursiops truncatus) in Sarasota Bay, Florida. Sci Total Environ.
(2005) 349:106–19. doi: 10.1016/j.scitotenv.2005.01.010
58. Yordy JE, Pabst DA, Mclellan WA, Wells RS, Rowles TK, Kucklick JR. Tissue-
specific distribution and whole-body burden estimates of persistent organic
pollutants in the bottlenose dolphin (Tursiops truncatus). Environ Toxicol
Chem. (2010) 29:1263–73. doi: 10.1002/etc.152
59. Jepson PD, Law RJ. Persistent pollutants, persistent threats. Science. (2016)
352:1388–9. doi: 10.1126/science.aaf9075
60. Schwacke LH, Voit EO, Hansen LJ, Wells RS, Mitchum GB, Hohn
AA, et al. Probabilistic risk assessment of reproductive effects of
polychlorinated biphenyls on bottlenose dolphins (Tursiops truncatus) from
the southeast United States coast. Envi ron Toxicol Chem. (2002) 21:2752–64.
doi: 10.1002/etc.5620211232
61. Reijnders PJ. Reproductive failure in common seals feeding on fish from
polluted coastal waters. Nature. (1986) 324:456–7. doi: 10.1038/324456a0
62. Ross PS, Ellis G, Ikonomou M, Barrett-Lennard L, Addison R. High
PCB concentrations in free-ranging Pacific killer whales, Orcinus orca:
effects of age, sex and dietary preference. Mar Poll Bull. (2000) 40:504–1 5.
doi: 10.1016/S0025-326X(99)00233-7
63. Reddy ML, Reif J, Bachand A, Ridgway S. Opportunities for using
Navy marine mammals to explore associations between organochlorine
contaminants and unfavorable effects on reproduction. Sci Tot Environ.
(2001) 274:171–82. doi: 10.1016/S0048-9697(01)00741-0
64. Hall AJ, Hugunin K, Deaville R, Law RJ, Allchin CR, Jepson PD. The risk
of infection from polychlorinated biphenyl exposure in the harbor porpoise
(Phocoena phocoena): a case–control approach. Environ Health Persp. (2006)
114:704–11. doi: 10.1289/ehp.8222
65. Mori C, Morsey B, Levin M, Nambiar PR, De Guise S. Immunomodulatory
effects of in vitro exposure to organochlorines on T-cell proliferation in
marine mammals and mice. J Tox Environ Health A. (2006) 69:283–302.
doi: 10.1080/15287390500227472
66. Schwacke LH, Zolman ES, Balmer BC, De Guise S, George RC, Hoguet
J, et al. Anaemia, hypothyroidism and immune suppression associated
with polychlorinated biphenyl exposure in bottlenose dolphins (Tursiops
truncatus). Proc Biol Sci. (2012) 279:48–57. doi: 10.1098/rspb.2011.0665
67. Hall AJ, Mcconnell BJ, Rowles TK, Aguilar A, Borrell A, S chwacke L, et al.
Individual-based model framework to assess population consequences of
polychlorinated biphenyl exposure in bottlenose dolphins. Environ Health
Persp. (2005) 114:60–4. doi: 10.1289/ehp.8053
68. Balmer BC, Ylitalo GM , Mcgeorge LE, Baugh KA, Boyd D, Mullin KD, et
al. Persistent organic pollutants (POPs) in blubber of common bottlenose
dolphins (Tursiops truncatus) along the northern Gulf of Mexico coast, USA.
Sci Total Environ. (2015) 527:306–12. doi: 10.1016/j.scitotenv.2015.05.016
69. Balmer JE , Ylitalo GM, Rowles TK, Mullin KD, Wells RS, Townsend FI, et
al. Persistent organic pollutants (POPs) in blood and blubber of common
bottlenose dolphins (Tursiops truncatus) at three northern Gulf of Mexico
sites following the Deepwater Horizon oil spill. Sci Total Environ. (2018)
621:130–7. doi: 10.1016/j.scitotenv.2017.11.209
70. Balmer BC, Wells RS, Howle LE, Barleycorn AA, Mclellan WA, Ann
Pabst D, et al. Advances in cetacean telemetry: a review of single-pin
transmitter attachment techniques on small cetaceans and de velopment of
a new satellite-linked transmitter design. Mar Mamm Sci. (2014) 30:656–73.
doi: 10.1111/mms.12072
71. Takeshita R, Sullivan L, Smith C, Collier T, Hall A, Brosnan T, et al. The
Deepwater Horizon oil spill marine mammal injury assessment. Endanger
Species Res. (2017) 33:95–106. doi: 10.3354/ esr00808
72. Wallace BP, Brosnan T, Mclamb D, Rowles T, Ruder E, Schroeder B, et
al. Effects of the Deepwater Horizon oil spill on prote cted marine spe cies.
Endang Species Res. (2017) 33:1–7. doi: 10.3354 /esr0078 9
73. Venn-Watson S, Colegrove KM, Litz J, Kinsel M, Terio K, Saliki J, et al.
Adrenal gland and lung lesions in Gulf of Mexico common bottlenose
dolphins (Tursiops truncatus) found dead following the Deepwater Horizon
oil spill. PLoS ONE. (2015) 10:e0126538. doi: 10.1371/journal.pone.0126538
74. De Guise S, Levin M, Gebhard E, Jasperse L, Hart LB, Smith CR, et al.
Changes in immune functions in bottlenose dolphins in the northern Gulf
of Mexico associated with the Deepwater Horizon oil spill. Endang Species
Res. (2017) 33:291–303. doi: 10.3354/esr00814
75. Smith CR, Rowles TK, Hart LB, Townsend FI, Wells RS, Zolman ES, et
al. Slow recovery of Barataria Bay dolphin health following the Deepwater
Horizon oil spill (2013-2014), with evidence of persistent lung disease
and impaired stress response. Endang Species Res. (2017) 33:127–42.
doi: 10.3354/esr00778
76. Venn-Watson S, Garrison L, Litz J, Fougeres E, Mase B, Rappucci
G, et al. Demographic clusters identified within the northern Gulf
of Mexico common bottlenose dolphin (Tursiops truncates) unusual
mortality event: January 2010-June 2013. PLoS ONE. (2015) 10:e0117248.
doi: 10.1371/journal.pone.0117248
77. Smith CR , Solano M, Lutmerding BA, Johnson SP, Meegan JM, Le-
Bert CR, et al. Pulmonary ultrasound findings in a bottlenose dolphin
Tursiops truncatus population. Dis Aquat Organ. (2012) 101:243–55.
doi: 10.3354/dao02537
78. Venn-Watson S, Daniels R, Smith C. Thirty year re trospective evaluation of
pneumonia in a bottlenose dolphin Tursiops truncatus population. Dis Aquat
Org. (2012) 99:237–42. doi: 10.3354/dao02471
79. Fire SE, Fauquier D, Flewelling LJ, Henry M, Naar J, Pierce R, et al.
Brevetoxin exposure in bottlenose dolphins (Tursiops truncatus) associated
with Karenia brevis blooms in Sarasota Bay, Florida. Mar Biol. (2007)
152:827–34. doi: 10.1007/s00227-007-0733-x
80. Colegrove KM, Venn-Watson S, Litz J, Kinsel MJ, Terio KA, Fougeres E, et
al. Fetal distress and in utero pneumonia in perinatal dolphins during the
Northern Gulf of Mexico unusual mortality event. Dis Aquat Org. (2016)
119:1–16. doi: 10.3354/dao02969
81. Fauquier DA, Litz J, Sanchez S, Colegrove K, Schwacke LH, Hart
L, et al. Evaluation of morbillivirus exposure in cetaceans from the
northern G ulf of Mexico 2010-2014. Endang Species Res. (2017) 33:211–20.
doi: 10.3354/esr00772
82. L ane SM, Smith CR, Mitchell J, Balmer BC, Barry KP, Mcdonald T, et
al. Reproductive outcome and survival of common bottlenose dolphins
sampled in Barataria Bay, Louisiana, USA, following the Deepwater
Horizon oil spill. Proc Biol Sci. (2015) 282:201519 44 . doi: 10.1098/rspb.
2015.1944
83. Mcdonald TL, Hornsby FE, Speakman TR, Zolman ES, Mullin KD, Sinclair
C, et al. Survival, density, and abundance of common bottlenose dolphins
in Barataria Bay (USA) following the Deepwater Horizon oil spill. Endang
Species Res. (2017) 33:193–209. doi: 10.3354 /esr0080 6
84. Monson DH, Doak DF, Ballachey BE, Johnson A, Bodkin JL. Long-term
impacts of the Exxon Valdez oil spill on sea otters, assessed through age-
dependent mortality patterns. Proc Nat Acad Sci USA. (2000) 97:6562–7.
doi: 10.1073/pnas.120163397
85. Bodkin JL, Ballachey BE, Dean T, Fukuyama AK, Jewett S, Mcdonald
L, et al. Sea otter population status and the process of recovery from
the 1989 ‘Exxon Valdez’oil spill. Mar Ecol Prog Ser. (2002) 241:237–54.
doi: 10.3354/meps241237
86. Matkin C, Saulitis E, Ellis G, Olesiuk P, Rice S. Ongoing population-level
impacts on killer whales Orcinus orca following the’Exxon Valdez’oil spill
in Prince William Sound, Alaska. Mar Ecol Prog Ser. (2008) 356:269–81.
doi: 10.3354/meps07273
87. Helm RC, Costa DP, Debruyn TD, O’shea TJ, Wells RS, Williams TM.
Overview of effects of oil spills on marine mammals. In: Fingus MF, editor.
Handbook of Oil Spill Science and Technology. John Wiley & Sons, Inc. (2015).
p. 455–75.
88. Asper ED. Techniques of live capture of smaller Cetacea. J Fish Res Board
Can. (1975) 32:1191–6. doi: 10.1139/f75-138
89. Loughlin T, Cunningham L, Gales N, Wells RS, Boyd I. Marking and
capturing. In: Boyd IL, Don Bowen W, Iverson SJ, editors. Marine Mammal
Ecology and Conservation: A Handbook of Techniques. Oxford: Oxford
University Press (2010). p. 16–41.
90. Klatsky LJ, Wells RS, Sweeney JC. Offshore bottlenose dolphins (Tursiops
truncatus): movement and dive behavior near the Bermuda Pedestal. J
Mammal. (2007) 88:59–66. doi: 10.1644/0 5- MAM M- A-365R1.1
91. Townsend FI, Smith CR, Rowles T. Health assessment of bottlenose dolphins
in capture-release studies. In: Gulland FMD, Whitman KL, Dierauf LA,
editors. CRC Handbook of Marine Mammal Medicine. CRC Press (2018).
p. 823–33.
Frontiers in Veterinary Science | www.frontiersin.org 15 December 2019 | Volume 6 | Article 444
Barratclough et al. Bottlenose Dolphin Health Assessments
92. Wells RS. Learning from nature: bottlenose dolphin care and husbandry. Zoo
Biol. (2009 ) 2 8:63 5 –5 1. doi: 10.1002/zoo.20252
93. Ridgway SH. Medical care of marine mammals. J Am Vet Med Ass.
(1965) 147:1077–85.
94. Kellar NM, Trego ML, Chivers SJ, Archer FI. Pregnancy patterns of
pantropical spotted dolphins (Stenella attenuata) in the eastern tropical
Pacific determined from hormonal analysis of blubber biopsies and
correlations with the purse-seine tuna fishery. Mar Biol. (2013) 160:3113–24.
doi: 10.1007/s00227-013-2299-0
95. Rossman S, Barros NB, Ostrom PH, Stricker CA, Hohn AA, Gandhi H,
et al. Retrospective analysis of bottlenose dolphin foraging: a legacy of
anthropogenic ecosystem disturbance. Mar Mamm Sci. (2013) 29:705–18.
doi: 10.1111/j.1748-7692.2012.00618.x
96. Boggs ASP, Schock TB, Schwacke LH, Galligan TM, Morey JS,
Mcfee WE, et al. Rapid and reliable steroid hormone profiling in
Tursiops truncatu s blubber using liquid chromatography tandem mass
spectrometry (LC-MS/MS). Analyt Bioanalyt Chem. (2017) 409:5019–2 9.
doi: 10.1007/s00216-017-0446-z
97. Smith CR, Venn-Watson S, Wells RS, Johnson SP, Maffeo N, Balmer
BC, et al. Comparison of nephrolithiasis prevalence in two bottlenose
dolphin (Tursiops truncatus) populations. Front Endocrinol. (2013) 4:145.
doi: 10.3389/fendo.2013.00145
98. Smith CR, Poindexter JR, Meegan JM, Bobulescu IA, Jensen ED,
Venn-Watson S, et al. Pathophysiological and physicochemical basis of
ammonium urate stone formation in dolphins. J Urol. (2014) 1 92 :26 0– 6.
doi: 10.1016/j.juro.2014.01.008
99. Ardente A, Wells R, Smith C, Walsh M, Jensen E, Schmitt T, et
al. Dietary cation–anion difference may explain why ammonium urate
nephrolithiasis occurs more frequently in common bottlenose dolphins
(Tursiops tru ncatus) under human care than in free-ranging common
bottlenose dolphins. J Anim Sci. (20 17 ) 95:1396–406. doi: 10.2527/jas.
2016.1113
100. Sweeney JC, Ridgway SH. Procedures for the clinical management of small
cetaceans. J Am Vet Med Assoc. (1975) 167:540–5.
101. Smith CR, Jensen ED, Blankenship BA, Greenberg M, D’agostini DA,
Pretorius DH, et al. Fetal omphalocele in a common bottlenose
dolphin (Tu rsiops truncatus). J Zoo Wildlife Med. (2013) 44:87– 92 .
doi: 10.1638/1042-7260-44.1.87
102. Seitz KE, Smith CR, Marks SL, Venn-Watson SK, Ivancic M. Liver
ultrasonography in dolphins: use of ultrasonography to establish a technique
for hepatobiliary imaging and to evaluate metabolic disease-associated liver
changes in bottlenose dolphins (Tursiops truncatus). J Zoo Wildl Med. (2016)
47:1034–43. doi: 10.1638/2015-0173.1
103. Martony ME, Ivancic M, Gomez FM, Meegan JM, Nollens HH, Schmitt TL,
et al. Establishing marginal lymph node ultrasonographic characteristics in
healthy bottlenose dolphins (Tursiops truncatus). J Zoo Wildl Med. (2017)
48:961–71. doi: 10.1638/2016-0251.1
104. Harms CA, Jensen ED, Townsend FI, Hansen LJ, Schwacke LH, Rowles TK.
Electrocardiograms of bottlenose dolphins (Tursiops truncatus) out of water:
habituated collection versus wild postcapture animals. J Zoo Wildl Med.
(2013) 44:972–81. doi: 10.1638/2013-0093.1
105. Read A, Wells R , Hohn A, Scott M. Patterns of growth in wild
bottlenose dolphins, Tursiops truncatus. J Zool. (1993) 231:107–23.
doi: 10.1111/j.1469-7998.1993.tb05356.x
106. Houser DS, Finneran JJ. Variation in the hearing sensitivity of a dolphin
population determined through the use of e voked potential audiometry. J
Acoutic Soc Am. (2006) 120:4090–9. doi: 10.1121/1.2357993
107. Apprill A, Miller CA, Moore MJ, Durban JW, Fearnbach H, Barrett-
Lennard LG. Extensive core microbiome in drone-captured whale blow
supports a framework for health monitoring. mSystems. (2017) 2:e001 19 –1 7 .
doi: 10.1128/mSystems.00119-17
108. Fahlman A, Brodsky M, Wells R, Mchugh K, Allen J, Barleycorn A, et al.
Field energetics and lung function in wild bottlenose dolphins, Tursiops
truncatus, in Sarasota Bay Florida. R Soc Open Sci. (2018) 5:171280.
doi: 10.1098/rsos.171280
109. Buck JD, Wells RS, Rhinehart HL, Hansen LJ. Aerobic microorganisms
associated wit h free-ranging bottlenose dolphins in coastal Gulf of
Mexico and Atlantic Ocean waters. J Wildl D is. (2006) 42:536–44.
doi: 10.7589/0090-3558-42.3.536
110. Wells RS. Identification methods. In: Würsig B, Thewissen JGM, Kovacs K,
eitors. Encyclopedia of Marine Mammals. 3rd ed. San Diego, CA: Academic
Press (2018). p. 503–9.
111. Scott MD, Wells RS, Ir vine AB, Mate BR. Tagging and marking s tudies on
small cetaceans. In: Appel MJ, editor. The Bottlenose Dolphin. New York, NY:
Elsevier (1990). p. 489–514.
112. Rosel PE. PCR-based sex determination in Odontocete cetaceans. Conserv
Genet. (2003) 4:647–9. doi: 10.1023/A:1025666212967
113. Schwacke L, Hall AJ, Wells RS, Bossart GD, Fair P, Hohn AA, et al. Health
and risk assessment for bottlenose dolphin (Tursiops truncatus) populations
along the southeast United States coast: current status and future plans. Paper
SC/56/E20 Presented to the IWC Scientific Committee. Sorrento (2004).
114. Wells RS, Smith CR, Sweeney JC, Townsend FI, Fauquier DA, Stone
R, et al. Fetal survival of common bottlenose dolphins (Tursiops
truncatus) in Sarasota Bay, Florida. Aquat Mamm. (2014) 40:252.
doi: 10.1578/AM.40.3.2014.252
115. Kellar NM, Trego ML, Marks CI, Dizon AE. Determining pregnancy from
blubber in three species of delphinids. Mar Mamm S ci. (2006) 22:1–16.
doi: 10.1111/j.1748-7692.2006.00001.x
116. Kellar NM, Speakman TR, S mith CR, Lane SM, Balmer BC, Trego ML,
et al. Low reproductive success rates of common bottlenose dolphins
Tursiops truncatus in the northern Gulf of Mexico following the Deepwater
Horizon disaster (2010-2015). Endang Species Res. (2017) 33:143–58.
doi: 10.3354/esr00775
117. Wells RS, Schwacke LH, Rowles TK, Balmer BC, Zolman E, Speakman T, et
al. Ranging patterns of common bottlenose dolphins Tursiops truncatus in
Barataria Bay, Louisiana, following the Deepwater Horizon oil spill. Endang
Species Res. (2017) 33:159–80. doi: 10.335 4 /esr00732
118. Heithaus MR, Dill LM. Food availability and tiger shark predation risk
influence bottlenose dolphin habitat use. Ecology. (2002) 83:480–91. doi: 10.
1890/0012-9658(2002)083[0480:FAATSP]2.0.CO;2
119. Mccabe EJB, Gannon DP, Barros NB, Wells RS. Prey s election by resident
common bottlenose dolphins (Tursiops truncatus) in Sarasota Bay, Florida.
Mar Biol. (2010) 157:931–42. doi: 10.1007/s00227-009-1371-2
120. Santos MB, German I, Correia D, Read FL, Cedeira JM, Caldas M, et al. Long-
term variation in common dolphin diet in relation to prey abundance. Mar
Ecol Prog Ser. (2013) 481:249–68. doi: 10.3354/meps10233
121. Wells R, Mchugh KA, Douglas DC, Shippee S, Berens Mccabe EJ, Barros NB,
et al. Evaluation of potential protective factors against metabolic syndrome
in bottlenose dolphins: feeding and activity patterns of dolphins in Sarasota
Bay, Florida. Front Endocrinol. (2013) 4:139. doi: 10.3389/fendo.2013.
00139
122. Jodice PGR, Roby DD, Turco KR, Suryan RM, Irons DB, Piatt JF, et al.
Assessing the nutritional stress hypothesis: relative influence of diet quantity
and quality on seabird productivity. Mar Ecol Prog Ser. (2006) 325:267 –79 .
doi: 10.3354/meps325267
123. Hohn AA, Thomas L, Carmichael RH, Litz J, Clemons-Che vis C, Shippee SF,
et al. Assigning stranded bottlenose dolphins to source stocks using stable
isotope ratios following the Deepwater Horizon oil spill. Endang Species Res.
(2017) 33:235–52. doi: 10.3354/esr00783
124. Rosel PE, Wilcox LA, Sinclair C, Speakman TR, Tumlin MC, Litz JA, et al.
Genetic assignment to stock of stranded common bottlenose dolphins in
southeastern Louisiana after the Deepwater Horizon oil spill. Endang Species
Res. (2017) 33:221–34. doi: 10.3354/esr00780
125. Thomas L, Booth CG, Rosel PE, Hohn A, Litz J, Schwacke LH. Where
were they from? Modelling the source stock of dolphins stranded after the
Deepwater Horizon oil spill using genetic and stable isotope data. Endang
Species Res. (2017) 33:253–64. doi: 10.335 4 /esr00754
126. Wilson RP, Mcmahon CR. Measuring devices on wild animals: what
constitutes acceptable practice? Frontiers Ecol Environ. (2006) 4:147–54.
doi: 10.1890/1540-9295(2006)0040147:MDOWAW2.0.CO;2
127. Balmer BC, Wells RS, Schwacke LH, Schwacke JH, Danielson B, George
RC, et al. Integrating multiple techniques to identify stock boundaries
of common bottlenose dolphins (Tursiops truncatus). Aquat Conserv Mar
Freshw Ecosyst. (2014) 24:511–21. doi: 1 0.10 0 2/aqc.235 7
Frontiers in Veterinary Science | www.frontiersin.org 16 December 2019 | Volume 6 | Article 444
Barratclough et al. Bottlenose Dolphin Health Assessments
128. Pirotta V, Smith A, Ostrowski M, Russell D, Jonsen ID, Grech A, et al. An
economical custom-built drone for assessing whale health. Front Mar Sci.
(2017) 4:425. doi: 10.3389/fmars.2017.00425
129. Barbieri MM, Mclellan WA, Wells RS, Blum JE, Hofmann S, Gannon
J, et al. Using infrared thermography to assess seasonal trends in dorsal
fin surface temperatures of free-swimming bottlenose dolphins (Tursiops
truncatus) in Sarasota Bay, Florida. Mar Mamm Sci. (2010) 26:53–66.
doi: 10.1111/j.1748-7692.2009.00319.x
130. Learmonth JA, Macleod CD, Santos MB, Pierce GJ, Crick H, Robinson R.
Potential effects of climate change on marine mammals. Oceanogr Mar Biol.
(2006) 44:431. doi: 10.1201/9781420006391.ch8
131. Burek KA, Gulland FMD, O’hara TM. Effects of climate change on Arctic
marine mammal health. Ecol Appl. (2008) 18:126–34. doi: 10.1890/06-0553.1
132. Edwards HH. Potential impacts of climate change on warmwater megafauna:
the Florida manatee example (Trichechus manatus latirostris). Clim Change.
(2013) 121:727–38. doi: 10.1007/s10584-013-0921-2
133. Powell JWB, Duffield DA, Kaufman JJ, Mcfee W. Bone density cannot
accurately predict age in the common bottlenose dolphin, Tursiops truncatus.
Mar Mam Sci. (2019) 35:1597–602. doi: 10.1111/mms.12591
134. García-Párraga D, Schmitt TL, Jensen E. Use of radiographic parameters for
age estimation in bottlenose dolphins (Tursiops truncatus). In: International
Association of Aquatic Animal Health Conference Proceedings. (2011).
135. Weller DW, Cockcroft VG, Würsig B, Lynn SK, Fertl D. Behavioral responses
of bottlenose dolphins to remote biopsy sampling and observations of
surgical biopsy wound healing. Aquat Mamm. (1997) 23:49–58.
136. Boggs ASP, Ragland JM, Zolman ES, Schock TB, Morey JS, Galligan TM,
et al. Remote blubber sampling paired with liquid chromatography tandem
mass spectrometry for steroidal endocrinology in free-ranging bottlenose
dolphins (Tursiops truncatus). Gen Comp Endocr i nol. (2019) 281:164–72.
doi: 10.1016/j.ygcen.2019.06.006
137. Beal A, Kiszka JJ, Wells RS, Eirin-Lopez JM. The Bottlenose dolphin
Epigenetic Aging Tool (BEAT): a molecular age estimation tool for small
cetaceans. Front Mar Sci. (2019) 6:561. doi: 10.3389/fmars.2019.00561
138. Horvath S. DNA met hylation age of human tissues and cell types. Genome
Biol. (2013 ) 1 4:31 5 6. doi: 10.1186/gb-2013-14-10-r115
139. Levine ME, Hosgood HD, Chen B, Absher D, Assimes T, Horvath S. DNA
methylation age of blood predicts future onset of lung cancer in the women’s
health initiative. Aging. (2015) 7:690–700. doi: 10.18632/aging.100809
140. Perna L, Zhang Y, Mons U, Holleczek B, Saum KU, Brenner H.
Epigenetic age acceleration predicts cancer, cardiovascular, and all-
cause mortality in a German c ase cohort. Clin Epigenet. (2016) 8:64.
doi: 10.1186/s13148-016-0228-z
141. Roetker NS, Pankow JS, Bressler J, Morrison AC, Boerwinkle E. Prospective
study of epigenetic age acceleration and incidence of cardiovascular disease
outcomes in the ARIC study (atherosclerosis risk in communities). Circ
Genom Precis Med. (2018) 11:e001937. doi: 10.1161/CIRCGEN.117.001937
142. Shorter KA, Shao Y, Ojeda L, Barton K, Rocho-Levine J, Van Der Hoop
J, et al. A day in the life of a dolphin: Using bio-logging tags for
improved animal health and well-being. Mar Mamm Sci. (2017) 33:785–802.
doi: 10.1111/mms.12408
143. Mcdonald BI, Johnson M, Madsen PT. Dive heart rate in harbour
porpoises is influenced by exercise and expectations. J Experim Biol. (2018)
221:jeb168740. doi: 10.1242/jeb.168740
144. Sayigh LS, Tyack PL, Wells RS, Scott MD. Signature whistles of
free-ranging bottlenose dolphins Tursiops truncatus: stability and
mother-offspring comparisons. Behav Ecol Sociobiol. (1990) 26:247–60.
doi: 10.1007/BF00178318
145. Jones B, Zapetis M, Samuelson MM, Ridgway S. Sounds produced by
bottlenose dolphins (Tursiops): a review of the defining characteristics and
acoustic criteria of the dolphin vocal repertoire. Bioacoustics. (2019) 18:1–42.
doi: 10.1080/09524622.2019.1613265
146. Bossart G. Marine mammals as sentinel species for oceans and human health.
Vet Path. (2011) 48:676–90. doi: 10.1177/0300985810388525
147. Hall AJ, Gulland FM, Hammond JA, Schwacke L H, Boyd I, Bowen W, et al.
Epidemiology, disease, and health assessment. In: Boyd IL, Don Bowen W,
Iverson SJ, editors. Marine Mammal Ecology and Conservation. New York,
NY: Oxford University Press (2010). p. 144–64.
148. Gulland FM, Dierauf LA, Whitman KL. CRC Handbook of Marine Mammal
Medicine. 3rd ed. Boca Raton, FL: CRC Press. (2018).
149. Hall MA, Alverson DL, Metuzals KI. By-catch: problems and solutions. Mar
Poll Bull. (2000) 41:204–19. doi: 10.1016/S0025-326X(00)00111-9
150. Fire SE, Wang Z, Byrd M, Whitehead HR, Paternoster J, Morton SL.
Co-occurrence of multiple classes of harmful algal toxins in bottlenose
dolphins (Tursiops truncatus) stranding during an unusual mortality event
in Texas, USA. Harmful Algae. (2011) 10:330–6. doi: 10.1016/j.hal.2010.
12.001
151. Mchugh KA, Allen JB, Barleycorn AA, Wells RS. Severe Karenia brevis
red tides influence juvenile bottlenose dolphin (Tursiops truncatus)
behavior in Sarasota Bay, Florida. Mar Mamm Sci. (2011) 27:622–43.
doi: 10.1111/j.1748-7692.2010.00428.x
152. Weisberg RH, Liu Y, Lembke C, Hu C, Hubbard K, Garrett M. The
coastal ocean circulation influence on the 2018 West Florida Shelf
K. brevis red tide bloom. J Geophys Res Oceans. (2019) 124:2501–12.
doi: 10.1029/2018JC014887
153. Zohdi E, Abbaspour M. Harmful algal blooms (red tide): a review of causes,
impacts and approaches to monitoring and prediction. Int J Environ Sci Tech.
(2019) 16:1789–806. doi: 10.1007/s13762-018-2108-x
154. Ortiz R M, Worthy GA. Effects of capture on adrenal steroid and
vasopressin concentrations in free-ranging b ottlenose dolphins
(Tursiops truncatus). Comp Biochem Phys A Phys. (2000) 125:317–24.
doi: 10.1016/S1095-6433(00)00158-6
155. Norman SA, Hobbs RC, Foster J, S chroeder JP, Townsend FI.
A review of animal and human health concerns during capture-
release, handling and tagging of odontocetes. J Cetacean Res Manag.
(2004) 6:53–62. Available online at: https://pdfs.semanticscholar.org/e0dc/
57f496a9434514ea187083bf672c7d10eeeb.pdf
156. Mancia A, Warr GW, Chapman RW. A transcriptomic analysis of
the stress induced by capture–release health assessment studies in
wild dolphins (Tursiops truncatus). Mol Ecol. (2008) 17:2581–9.
doi: 10.1111/j.1365-294X.2008.03784.x
157. Fair PA, Schaefer AM, Romano TA, Bossart GD, Lamb SV, R eif JS. Stress
response of wild bottlenose dolphins (Tursiops truncatus) during capture–
release health assessment studies. Gen Comp Endocrinol. (2014) 206:2 03 –1 2.
doi: 10.1016/j.ygcen.2014.07.002
158. Hart LB, Wells RS, Kellar N, Balmer BC, Hohn AA, Lamb SV, et al.
Adrenal hormones in common b ottlenose dolphins (Tursiops truncatus):
influential factors and reference intervals. PLoS ONE. (2015) 10:e0127432 .
doi: 10.1371/journal.pone.0127432
159. Champagne CD, Kellar NM, Trego ML, Brendan D, Rudy B, Wasser SK, et al.
Comprehensive endocrine response to acute stress in the bottlenose dolphin
from serum, blubber, and feces. Gen Comp Endocrin. (2018) 266:178–93.
doi: 10.1016/j.ygcen.2018.05.015
160. Wells RS. Social structure and life history of bottlenose dolphins near
Sarasota Bay, Florida: insights from four decades and five generations. In:
Yamagiwa J, Karczmarski L, editors. Primates and Cetaceans. Tokyo: Springer
(2014). p. 149–72.
161. Broadhurst MK. Bottlenose dolphins, Tursiops truncatus, removing by-catch
from prawn-trawl codends during fishing in New South Wales, Australia.
Mar Fish Rev. (1998) 60:9–14.
162. Ingram SN, Rogan E. Identifying critical areas and habitat preferences of
bottlenose dolphins Tursiops truncatus. Mar Ecol Prog Ser. (2002) 244:247–
55. doi: 10.3354/meps244247
163. Díaz López B. Interactions between Mediterranean bottlenose dolphins
(Tursiops truncatus) and gillnets off Sardinia, Italy. J Mar Sci. (2006) 63:946–
51. doi: 10.1016/j.icesjms.2005.06.012
164. Read AJ, Drinker P, Northridge S. Bycatch of marine mammals
in US and global fisheries. Conserv Biol. (2006) 20:163–9.
doi: 10.1111/j.1523-1739.2006.00338.x
165. Brotons JM, Grau AM, Rendell L. Estimating the impact of
interactions between bottlenose dolphins and artisanal fisheries
around the Balearic Islands. Mar Mamm Sci. (2008) 24:112–27.
doi: 10.1111/j.1748-7692.2007.00164.x
166. Wells RS, Allen JB, Hofmann S, Bassos-Hull K, Fauquier DA, Barros NB,
et al. Consequences of injuries on survival and reproduction of common
Frontiers in Veterinary Science | www.frontiersin.org 17 December 2019 | Volume 6 | Article 444
Barratclough et al. Bottlenose Dolphin Health Assessments
bottlenose dolphins (Tursiops truncatus) along the west coast of Florida. Mar
Mamm Sci. (2008) 24:774–94. doi: 10.1 11 1 /j.1 74 8- 76 9 2.2 00 8.0 02 12 .x
167. Pulster EL, Smalling KL, Zolman E, Schwacke L, Maruya KA. Persistent
organochlorine pollutants and toxaphene congener profiles in bottlenose
dolphins (Tursiops truncatus) frequenting the Turtle/Brunswick River
Estuary, Georgia, USA. Environ Contamin Toxic. (2009) 28:1390–9.
doi: 10.1897/08-240.1
168. Wells RS. Feeling the heat: potential climate change impacts on bottlenose
dolphins. Whalewatcher. (2010) 39:12–7. Available online at: https://iucn-
csg.org/wp-content/uploads/2010/03/Whalewatcher-Climate-Change-
2010.pdf
169. Bearzi G, Agazzi S, Bonizzoni S, Costa M, Azzellino A. Dolphins in a bottle:
abundance, residency patterns and conservation of bottlenose dolphins
Tursiops truncatus in the semi-closed eutrophic Amvrakikos Gulf, Greece.
Aquat Conserv Mar Freshw Ecosyst. (2008) 18:130–46. doi: 10.1002/aqc.843
170. Aliaga-Rossel E. Conservation of the river dolphin (Inia boliviensis) in
Bolivia. In: Garcia M, Shostell J, editors. Biology, Evolution and Conservation
of the River Dolphins in South America and Asia: Unknown Dolphins in
Danger. New York, NY: Nova Science Publishers (2010). p. 55–70.
171. Braulik GT, Noureen U, Arshad M, Reeves RR. Review of status, threats,
and conservation management options for the endangered Indus River blind
dolphin. Biol Conserv. (2015) 192:30–41. doi: 10.1016/j.biocon.2015.09.008
172. Khan MS. Factors affecting the survival of Indus River dolphin and
species tolerance towards anthropogenic pressures. Mar Freshwat Res. (2017)
68:1245–50. doi: 10.1071/MF16001
173. Centelleghe C, Da Dalt L, Marsili L, Zanetti R, Fernandez A,
Arbelo M, et al. Insights into dolphins’ immunology: immuno-
phenotypic study on Mediterranean and Atlantic stranded
cetaceans. Front Immunol. (2019) 10:888. doi: 10.3389/fimmu.2019.
00888
174. Turvey ST, Pitman RL, Taylor BL, Barlow J, Akamatsu T, Barrett LA , et
al. First human-caused extinction of a cetacean species? Biol Lett. (2007)
3:537–40. doi: 10.1098/rsbl.2007.0292
175. Rojas-Bracho L, Gulland FMD, Smith CR, Taylor B, Wells RS, Thomas PO, et
al. A field effort to capture critically endangered vaquitas Phocoena sinus for
protection from entanglement in illegal gillnets. Endang Species Res. (2019)
38:11–27. doi: 10.3354/esr00931
176. Wilkinson D, Worthy GAJ. Marine mammal stranding networks. Conserv
Manage Mar Mamm. (1999) 2:396 –4 11 .
177. Watwood SL, Tyack PL, Wells RS. Whistle sharing in paired male bottlenose
dolphins, Tursiops truncatus. Behav Ecol Sociobiol. (2004) 55:531–43.
doi: 10.1007/s00265-003-0724-y
178. Bejarano AC, Wells RS, Costa DP. Development of a bioenergetic model
for estimating energy requirements and prey b iomass consumption of the
bottlenose dolphin (Tursiops truncatus). Ecol Model. (2017) 356 :16 2– 72 .
doi: 10.1016/j.ecolmodel.2017.05.001
179. Pasamontes A, Aksenov AA, Schivo M, Rowles T, Smith CR, Schwacke LH,
et al. Noninvasive respiratory metabolite analysis associated with clinical
disease in cetaceans: a deepwater horizon oil spill study. Environ Sci Technol.
(2017) 51:5737–46. doi: 10.1021/acs.est.6b06482
180. Hall AJ, Wells RS, Sweeney JC, Townsend FI, Balmer BC, Hohn AA, et al.
Annual, seasonal and individual variation in hematology and clinical blood
chemistry profiles in bottlenose dolphins (Tu rsiops truncatus) from Sarasota
Bay, Florida. Comp Biochem and Phys Part A Phys. (2007) 148:266–77.
doi: 10.1016/j.cbpa.2007.04.017
181. Houser DS, Finneran JJ, Ridgway SH. Research with navy marine
mammals benefits animal care, conservation and biology. Int J Comp
Psych. (2010) 23:249–68. Available online at: https://escholarship.org/uc/
item/3pm7v89g
Conflict of Interest: JS was employed by the company Dolphin Quest.
The remaining authors declare that the research was conducted in the absence of
any commercial or financial relationships that could be construed as a potential
conflict of interest.
Copyright © 2019 Barratclough, Wells, Schwacke, Rowles, Gomez, Fauquier,
Sweeney, Townsend, Hansen, Zolman, Balmer and Smith. This is an open-access
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Frontiers in Veterinary Science | www.frontiersin.org 18 December 2019 | Volume 6 | Article 444