ArticlePDF Available

Characterisation of fibropapillomatosis tumour growth profiles in green sea turtles (Chelonia mydas)

Authors:
  • University of Florida's Whitney Laboratory for Marine Bioscience

Abstract and Figures

Wild sea turtle populations are currently listed as threatened and endangered as a result of both natural and anthropogenic factors. These include predation, disease, starvation, pollution, fisheries interaction and habitat degradation. Many natural threats including disease outbreaks have been exacerbated by human interaction. One disease of increasing threat to marine turtle populations worldwide is fibropapillomatosis (FP), a virulent cancer, thought to be triggered by a chelonian-specific herpes virus, ChHV5. Fibropapillomatosis reached epizootic proportions in the 1980s, now being present in sea turtle populations circum-globally. While the occurrence of FP tumours and post-surgical regrowth has been recorded previously, the specific growth rates of tumours pre- and post-surgery have never been assessed in detail. Such data is vital for establishing a growth baseline to better understand the disease and factors that may be accelerating its growth. Additionally, tumour growth baselines are crucial when assessing the effectiveness of targeted therapeutics to aid in the identification of the most effective treatments for FP-afflicted patients. Innovative treatment approaches are vital to help maintain healthy marine populations until the chronic underlying causes of these diseases can be addressed and preventative measures can be enforced. Here we document the growth and post-surgical regrowth rates of FP tumours in four Chelonia mydas patients at the University of Florida’s Whitney Sea Turtle Hospital. These data also indicate which tumour locations are more susceptible to post-surgical tumour regrowth. The results provide useful baseline information for future drug treatment studies, as well as suggesting further beneficial refinements to tumour growth profiling techniques.
Content may be subject to copyright.
12 Testudo Vol. 8, No. 5
Characterisation of fibropapillomatosis
tumour growth profiles in green sea turtles
(Chelonia mydas)
Jessica Farrell1, Rachel Thomas1, Mark Q. Martindale1 and David J.
Duffy1,2,3
1 The Whitney Laboratory for Marine Bioscience and Sea Turtle
Hospital, University of Florida, St. Augustine, Florida 32080, USA
2 Molecular Ecology and Fisheries Genetics Laboratory, School of
Biological Sciences, Bangor University, Bangor, Gwynedd LL57 2UW, UK
3 Department of Biological Sciences, School of Natural Sciences,
Faculty of Science and Engineering, University of Limerick, Limerick,
Ireland
Email: duffy@whitney.ufl.edu
d.duffy@bangor.ac.uk
jessicafarrell@ufl.edu
Presented to the BCG Northern Symposium at Chester Zoo on 21st
October 2017
Background
Wild sea turtle populations are currently listed as threatened and endangered
as a result of both natural and anthropogenic factors (Jones et al. 2016;
Duffy et al. 2018; IUCN 2018). These include predation, disease, starvation,
pollution, fisheries interaction and habitat degradation. Many natural threats
including disease outbreaks have been exacerbated by human interaction
(Dos Santos et al. 2010; Jones et al. 2016; Whilde et al. 2017). One disease of
increasing threat to marine turtle populations worldwide is fibropapillomatosis
(FP), a virulent cancer (Fig. 1), thought to be triggered by a chelonian-specific
herpes virus, ChHV5 (Herbst et al. 1995; Jones et al. 2016; Work et al. 2017;
Morrison et al. 2018).
First reported in the scientific literature in 1938, FP prevalence was as low
as 1.5% in the Florida Keys at that time (Smith & Coates 1938). Eyewitness
sources suggest the first cases occurred as early as the late 1800s (Cruz
1985). Fibropapillomatosis did not reach epizootic proportions until the
1980s when a combination of increased coastal development and human-
induced climate change began to significantly degrade juvenile sea turtle
habitats. Presenting as single or several benign fibroepithelial cutaneous
© British Chelonia Group + Jessica Farrell, ~Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
Testudo Vol. 8, No. 5 13
lesions (Jones et al. 2016), the disease significantly affects turtle survivorship
once the tumours are of significant size in locations inhibiting vision, feeding,
internal organ function and locomotive ability. The disease progressed to
a panzootic in the 1990s with outbreaks in the eastern Pacific, Hawaiian
Islands, Indonesia and Australia (Duarte et al. 2012; Page-Karjian et al. 2014;
Hargrove et al. 2016; Jones et al. 2016). Currently, there are a number of
FP visual scoring systems including the fibropapillomatosis index (FPI) (Rossi
et al. 2016) and a four-category size classification which ranks the tumour
burden from 0 to 3 (Work & Balazs 1999).
The number of turtles stranding with FP in Florida has exploded in recent
years, with over 250 entering Florida rehabilitation facilities in 2017. This
trend is likely to continue into the future (Foley 2015; Hargrove et al. 2016;
Duffy et al. 2018). Reported in all seven marine turtle species, FP most
severely impacts green sea turtles (Chelonia mydas). Evidence suggests that
its geographic range is spreading to more northern latitudes where FP was
never previously recorded. The disease is now undermining conservation
efforts across the globe (Duarte et al. 2012; Page-Karjian et al. 2014;
Hargrove et al. 2016; Jones et al. 2016; Duffy et al. 2018).
Currently, the only commonly applied treatment for FP is surgery, which
is expensive, restricted to only a small number of turtle hospitals and 60%
of the time results in tumour regrowth post-surgery (Page-Karjian et al.
2014; Whilde et al. 2017). While the occurrence of FP tumours and post-
surgical regrowth has been recorded previously, the specific growth rates
of tumours pre- and post-surgery have never been assessed in detail. Such
data are vital for establishing a growth baseline to better understand the
disease and factors that may be accelerating its growth. Additionally, tumour
growth baselines are crucial when assessing the effectiveness of targeted
therapeutics. Once baseline FP tumour growth rates are established, these
can be used to compare the rate of tumour growth and regrowth in
patients subjected to various candidate drug treatments in order to identify
the most effective course of treatment for FP-afflicted patients. Innovative
treatment approaches are vital to help maintain healthy marine populations
until the chronic underlying causes of these diseases can be addressed and
preventative measures can be enforced (Duffy et al. 2018).
Objectives
This paper documents the growth and post-surgical regrowth rates of FP
tumours in four C. mydas patients at the University of Florida’s Whitney Sea
Turtle Hospital. These data will indicate which tumour locations are more
susceptible to accelerated tumour regrowth. The results will also be useful as
baseline information for future drug treatment studies, as well as suggesting
further beneficial refinements to tumour growth profiling techniques.
© British Chelonia Group + Jessica Farrell, Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
14 Testudo Vol. 8, No. 5
Method
Sample population: This study used existing images, taken as part of the
rehabilitative care of four juvenile C. mydas patients admitted to the Whitney
Sea Turtle Hospital between September 2016 and April 2017. Images were
taken using an Olympus Tough TG-4 approximately 30cm from each lesion,
with a 25cm scale bar for accurate pixel comparison. All four patients were
found stranded along the east coast of Florida between Anastasia State
Park (north, 29.9083°N, 81.2837°W) and Ponce Inlet (south, 29.0779°N,
80.9211°W), displaying fibropapilloma-like tumours. Each patient received
medical care devised to best suit their particular circumstances; thus the
number of surgeries and duration of tumour growth analysis varies for each
turtle. The outcome of each patient differs, with some determined healthy
enough for release and others requiring euthanasia and necropsy. Tumour
removal surgeries involved the use of a CO2 laser to excise tumours and
cauterize surgical incision sites.
Table 1. Carapace length, weight, origin, condition on arrival and FP tumour scores of green
sea turtles (C. mydas) observed during this study at the Whitney Laboratory for Marine
Bioscience Sea Turtle Hospital.
Patient
ID
Straight
carapace length
(upon admittance)
cm
Weight
(upon admittance)
kg
Origin Condition
on arrival
FP tumour score
(FPI)
(Rossi et al.
2016)
Chrystal 29.2 2.8 Volusia FL Normal body
condition, FP
>66.5
Tamatoa 33.6 4.6 St. Johns
FL
Normal body
condition, FP
22.1
Pons 42.8 7.5 Volusia FL Emaciated, FP >6.5
Remi 35.7 3.8 Volusia FL Emaciated, FP >205.6
Image analysis: ImageJ is an image processing programme designed for
scientific multidimensional images (https://imagej.nih.gov/ij). Image analysis
using this computer software allows accurate measurements of tumour two-
dimensional surface area. It should be noted that the surface measurements
used in this study serve as a proxy for overall tumour growth. In future studies,
physical measurements of the three-dimensional tumour structures will allow
a more in-depth direct assessment of tumour growth dynamics. However, here
we evaluated the use of ImageJ software to track tumour growth. Existing
historical FP patient datasets primarily only contain visual records of tumour
growth, so, if found to be an applicable approach, two-dimensional surface
© British Chelonia Group + Jessica Farrell, ~Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
Testudo Vol. 8, No. 5 15
Fig. 1. Location of designated FP tumour ‘clusters’ on green sea turtle anatomy
(Patient 4: Remi).
© British Chelonia Group + Jessica Farrell, Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
16 Testudo Vol. 8, No. 5
area measurement would then be retroactively applicable to a large cohort
of patient data. Each tumour is assigned to a ‘cluster’ to enable analysis of
tumour growth in designated locations on the turtle anatomy (Fig. 1 and
Table 2). Each cluster was photographed by a member of the Whitney Sea
Turtle Hospital veterinary team on arrival, at each check-up and after each
surgery. These images were analysed in ImageJ in order to plot the growth
(surface area) and post-surgical regrowth of each cluster.
Table 2. Body location and abbreviations of tumour clusters used in this study.
Location designated as tumour clusters Cluster abbreviation Figure 1 Cluster location
number
Left Eye LEy 1
Right Eye REy 2
Dorsal Neck DNk 3
Ventral Neck VNk 4
Carapace Carapace 5
Plastron Plastron 6
Left Front Flipper Base LFFBa 7
Left Front Flipper Along LFFAl 8
Right Front Flipper Base RFFBa 9
Right Front Flipper Along RFFAl 10
Left Rear Flipper Base LRFBa 11
Left Rear Flipper Along LRFAl 12
Right Rear Flipper Base RRFBa 13
Right Rear Flipper Along RRFAl 14
Tail Tail 15
© British Chelonia Group + Jessica Farrell, ~Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
Testudo Vol. 8, No. 5 17
Results
Patient summaries
PATIENT 1: CHRYSTAL
Chrystal was first photographed at the Whitney Sea Turtle Hospital on January
12th 2017 (Fig. 2A). She underwent three surgeries to mitigate the severity
of her fibropapillomatosis burden. Photographs were taken after each of
Chrystal’s surgeries on the following dates:
RFebruary 8th: removal of tumours from Left Eye (LEy), Right Eye (REy),
Right Rear Flipper Base (RRFBa) and Left Front Flipper Base (LFFBa).
RMay 1st: removal of tumours from Right Front Flipper Base (RFFBa) and
Right Front Flipper Along (RRFAl).
RJune 13th: removal of tumours from LEy and REy (for the second time)
and Dorsal Neck (DNk).
The most persistent tumour regrowth was seen on Chrystal’s eyes (Fig. 2B
& Table 3). Limited regrowth was seen on the RFFBa and RFFAl (Fig. 2B).
No regrowth was seen on the LFFBa. All clusters left untreated by surgery
showed continuous steady growth. Due to continual tumour regrowth and
the diagnosis of internal lung tumours and impacts on quality of life, Chrystal
was euthanised on August 9th 2017, after 210 days in rehab, with a thorough
necropsy providing evidence of significant internal FP tumour growth – in
particular, a large golf ball-sized tumour located within the shoulder of the
RFFBa. The necropsy determined that Chrystal was a female.
© British Chelonia Group + Jessica Farrell, Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
18 Testudo Vol. 8, No. 5
Fig. 2. Fibropapillomatosis in a green turtle (Patient 1: Chrystal).
(A) Chrystal’s initial intake photograph upon admittance to the hospital.
(B) Growth profile of selected FP tumour clusters on Chrystal.
© British Chelonia Group + Jessica Farrell, ~Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
Testudo Vol. 8, No. 5 19
PATIENT 2: TAMATOA
Tamatoa was admitted to the Whitney Sea Turtle Hospital on April 17th 2017
(Fig. 3A), after stranding at Anastasia State Park, Florida.
RTamatoa underwent one surgery on May 15th 2017 to remove tumours
from its RFFBa, LFFBa and RRFBa.
Tamatoa showed no signs of tumour regrowth post-surgery (Fig. 3B & Table 3).
Showing good health and no indication of regrowth, Tamatoa was released
on July 13th 2017, after 88 days in rehab. Tamatoa was subsequently found
re-stranded and alive on August 27th 2017 at Anastasia State Park as a result
of being caught in a cast-net. There was no indication of FP tumours.
Fig. 3. Patient 2: Tamatoa. (A) Tamatoa’s initial intake photograph upon admittance to the
hospital. Tamatoa was found stranded by the Salt Run fish cleaning table in Anastasia State
Park, where he was habitually fed by local fishermen. (B) Growth profile of the surface area of
Tamatoa’s RFFBa cluster, obstructed in (A) due to placement of flipper.
© British Chelonia Group + Jessica Farrell, Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
20 Testudo Vol. 8, No. 5
PATIENT 3: PONS
Pons was reported as stranded to the Whitney Sea Turtle Hospital on September
25th 2016 and was collected from the water at Ponce Inlet, Florida. Pons was
first photographed at the Whitney Sea Turtle Hospital on October 4th 2016
(Fig. 4A). Pons was thin, with a healed propeller wound to the first vertebral
and left costal, and minimal algae and barnacles on the carapace.
RPons underwent one surgery on December 14th 2017 to remove
tumours from its LFFBa, RFFBa, LRFBa, RRFBa and Tail.
Pons showed the start of very minor regrowth on the LFFBa, RRFBa and Tail
(Fig. 4B). No regrowth was seen on the RFFBa or LRFBa. Showing good health
and no further regrowth, Pons was released on March 16th 2017, after 173
days in rehab. Pons was subsequently caught and released by a fisherman on
March 28th 2017; however, there was no indication of FP tumours, suggesting
that the beginnings of regrowth regressed while in the wild.
Fig. 4. Patient 3: Pons.
(A) Pon’s initial intake photograph upon admittance to the hospital. Found floating in Ponce
Inlet, Volusia County, with monofilament tangled around the right rear flipper base.
(B) Growth profile of selected FP tumour clusters on Pons.
© British Chelonia Group + Jessica Farrell, ~Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
Testudo Vol. 8, No. 5 21
Fig. 5. Patient 4: Remi.
(A) Remi’s initial intake photograph upon admittance to the hospital. Remi was found
and collected from the inshore waters of South Daytona Beach Canal off the Halifax River,
underweight and lacking in energy.
(B) Growth profile of selected FP tumour clusters on Remi.
© British Chelonia Group + Jessica Farrell, Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
22 Testudo Vol. 8, No. 5
PATIENT 4: REMI
Remi was reported as stranded to the Whitney Sea Turtle Hospital on April 10th
2017 and was collected from the inshore waters of Halifax River, Florida. Remi was
first photographed at the Whitney Sea Turtle Hospital on April 10th 2017 (Fig. 5A).
Remi was thin and lethargic with mud and algae covering his carapace. The patient
underwent four surgeries to mitigate the severity of its FP burden. Photographs
were taken after each of Remi’s surgeries on the following dates in 2017:
RMay 1st: removal of tumours from Carapace, RFFAl, RFFBa and Plastron.
RMay 30th: removal of tumours from LEy.
RJune 28th: removal of tumours from LFFAl, LFFBa, LRFBa and LRFAl.
RJuly 26th: removal of tumours from RRFBa, RRFAl, LEy (for the second time),
Ventral Neck (VNk) and Plastron (for the second time).
The most persistent tumour regrowth was seen on Remi’s left eye (LEy) as well as
the Plastron (Fig. 5B). Minor regrowth was seen on the LFFBa (Fig. 5B). No regrowth
was seen on the Carapace, VNk, RFFBa, RFFAl, LFFAl, LRFBa, LRFAl, RRFBa and
RRFAl. Due to its multiple surgeries and continued regrowth Remi remained in the
care of the Whitney Sea Turtle Hospital for a total of 344 days, but was successfully
released on 20th March 2018.
Tumour growth rates by individual and cluster locations
We assessed the growth rates of all tumour clusters, examining whether there
was any correlation in cluster location and the pre-surgery growth rate, across all
four patients. Generally, plastron tumours and those at the base of the flippers
tended to grow at a faster rate than other locations (Fig. 6A), although it should
be noted that these clusters also tended to have the largest tumour burdens (Table
3). Regrowth data were not available for some of Chrystal’s FP clusters, as surgery
took place too soon after the first photograph to have a second image available
(Table 3).
We next compared the predicted doubling time of each tumour (start size/pre-
surgery growth rate). Doubling time represents the hypothetical time it would
take (in days) for a tumour to double its original size (size at commencement of
measuring), assuming it continued to grow at its pre-surgery rate. While there
was a slight trend for larger tumours to require a longer doubling time (Fig. 6B),
despite their more rapid growth rate (Table 3), there was no strong correlation
between the size of a tumour and its predicted doubling time (linear correlation,
R2 = 0.01296).
In addition to characterising tumour growth rates as a baseline for future studies,
we also investigated whether there was any prognostic value in the pre-surgery
growth rates in terms of predicting patient outcome or the occurrence of post-
surgery tumour regrowth. However, the average tumour regrowth across all clusters
of an individual turtle were not predictive of rehabilitation outcome (Fig. 6C).
© British Chelonia Group + Jessica Farrell, ~Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
Testudo Vol. 8, No. 5 23
Fig. 6. Analysis of tumour growth rates.
(A) Average pre-surgery tumour growth rates combined by cluster, across all four patients.
(B) Predicted tumour doubling time by tumour starting size. Doubling time represents the
hypothetical time it would take (in days) for a tumour to double its original size, assuming it
had been allowed to continue to grow and maintained its pre-surgery growth rate.
(C) Average pre-surgery tumour growth rates combined by individual patient, related to
rehabilitation outcome.
© British Chelonia Group + Jessica Farrell, Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
24 Testudo Vol. 8, No. 5
Next we examined whether any of the tumours’ growth characteristics
(starting size, growth rate or growth rate/starting size) were predictive of the
occurrence of post-surgery regrowth (Fig. 7A). Interestingly, for those tumour
clusters with growth rate data available, the pre-surgery growth rate did not
clearly indicate whether a tumour would regrow post-surgery (Fig. 7A, B).
Fig. 7. Correlation of pre-surgery growth dynamics with the occurrence of post-surgical FP
tumour regrowth.
(A) Average pre-surgery tumour growth rates (left), tumour starting size (right) and growth
rate/starting size (bottom), across all patients and clusters (for which regrowth information
existed) grouped according to the occurrence of post-surgical tumour regrowth. Error bars
denote standard error.
(B) Tumour growth rate/starting size across patient clusters, grouped according to the
occurrence of post-surgical tumour regrowth.
© British Chelonia Group + Jessica Farrell, ~Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
Testudo Vol. 8, No. 5 25
Neither starting size (t-test, p = 0.6382, d.f. = 21), growth rate (t-test, p =
0.7050, d.f. = 21) or growth rate/starting size (t-test, p = 0.3931, d.f. = 21)
were significantly different between clusters exhibiting regrowth and those
having no post-surgery regrowth.
It should be noted that the negative growth rate for Chrystal’s REy cluster
was as a result of initial inflammation in that tumour being reduced upon
commencement of rehabilitative care. The reduction in size was not due to
genuine natural tumour regression. This inflammation complication also tallies
with the occurrence of post-surgical tumour regrowth in this eye. However,
even if this cluster is excluded from the analysis there remains no significant
difference between the no regrowth and regrowth clusters (t-test for growth
rate p = 0.4925, d.f. = 20, t-test for rate/starting size, p = 0.9634, d.f. =
20). Given this lack of significance we can rule out the use of these growth
characteristics as prognostic markers of tumour regrowth. However, reassessing
these features with a larger sample size would of course be highly desirable.
Discussion
Patients 2 and 3 received one surgery only as their symptoms were far less
advanced than Patients 1 and 4. As their FP was less advanced, they showed
minor or no regrowth and were released back into their wild populations.
Coincidentally, both patients were caught alive and released by fishermen
approximately one month later; however, there was no evidence of tumour
regrowth. As the patients were tagged, the fishermen took photos prior to
release to send to the hospital so as to keep track of patient health and
location.
Patients 1 and 4 displayed far more severe FP symptoms. Despite multiple
rounds of surgery, persistent tumour regrowth was a recurring problem.
The most susceptible sites requiring multiple surgeries were the eyes and
the plastron. Therefore, these sites should receive special focus in any
future adjunct post-surgery drug treatment trials. Due to the severity of
their symptoms, Patient 1 required euthanasia and Patient 4 remained in
rehabilitation almost one year after its initial stranding. Patient 1 displayed
continuous tumour regrowth and poor health. Her necropsy subsequently
showed extensive growth of internal FP tumours.
The two smallest patients, Chrystal and Remi (Table 1), were those most
affected by post-surgical tumour regrowth. Our observation supports the
findings made by Page-Karjian et al. (2014) that smaller turtles (straight
carapace lengths 30-35cm) were the most susceptible to FP tumour
development while in rehabilitation. Page-Karjian et al. (2014) suggested that
turtles are more likely to develop FP tumours during warmer rehabilitation
months (April-September), an observation also postulated elsewhere (Cruz
1985; Herbst et al. 1995; Jones et al. 2016; Duffy et al. 2018). This association
© British Chelonia Group + Jessica Farrell, Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
26 Testudo Vol. 8, No. 5
between warmer months and higher regrowth rates was also apparent with
both Patients 1 and 4 in this study. The most commonly FP-afflicted body
locations are stated to be the R/LFFBa, R/LFFAl, Tail, Plastron and R/LEy (Page-
Karjian et al. 2014). Again, the patients in this study support this finding. The
presence of ocular tumours can be a good indication of the outcome of the
Table 3. Pre-surgery fibropapillomatosis tumour growth characteristics and post-surgery
regrowth rates.
Patient Cluster Start Size
(mm2)
Growth Rate
Prior To
Surgical Removal
(mm2 per day)
Growth
Rate/
Start
Size
Re-Growth
Y/N
Growth
Period
(Days)
1. Chrystal Left Eye 460 7.0 0.016 Y11
Right Eye 485 -17.0 -0.035 Y11
Dorsal Neck 651 13.0 0.021 N138
Ventral Neck 1476 18.0 0.012 N/A 209
Plastron 447 23.0 0.053 N/A 209
Left Front Base 3662 3.0 0.001 N11
Left Front Along 202 15.0 0.076 N/A 209
Right Front Base 6234 94.0 0.015 Y95
Right Front Along 564 10.0 0.019 Y95
Left Rear Base 2111 48.0 0.023 N/A 209
Left Rear Along 43 1.0 0.024 N/A 209
Right Rear Base 7134 100.0 0.014 Y11
Tail 185 15.0 0.081 N/A 209
2. Tamatoa Left Front Base 1232 12.0 0.010 N14
Right Front Base 50 0.2 0.004 N14
Right Rear Base 1806 81.0 0.045 N14
3. Pons Left Front Base 341 3.0 0.010 Y71
Right Front Base 616 5.0 0.010 N71
Left Rear Base 1964 19.0 0.010 N71
Right Rear Base 1143 13.0 0.012 Y71
Tail 268 3.0 0.012 Y71
4. Remi Left Eye 60.03 0.004 Y35
Ventral Neck 78 0.6 0.007 N88
Carapace 1981 N/A N/A N21
Plastron 9903 N/A N/A Y21
Left Front Base 561 4.0 0.007 Y64
Left Front Along 421 8.0 0.021 N64
Right Front Base 1282 N/A N/A N21
Right Front Along 528 N/A N/A N21
Left Rear Base 3738 48.0 0.013 N64
Left Rear Along 1270 14.0 0.011 N64
Right Rear Base 1316 9.0 0.008 N88
Right Rear Along 446 0.5 0.001 N88
© British Chelonia Group + Jessica Farrell, ~Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
Testudo Vol. 8, No. 5 27
patient, as turtles without FP lesions on the eye are eight times more likely to
survive (Page-Karjian et al. 2014). The results from this study also support this
suggestion, as those turtles without eye tumours were able to be released,
while those with eye tumours required euthanasia or prolonged rehabilitation
time and medical care. In previous studies, the number of tumour removal
surgeries has not significantly related to patient outcome (Page-Karjian et
al. 2014). However, in this study a greater number of surgeries did coincide
with worse outcomes (euthanasia, extended rehabilitation time). In previous
studies, 38.5% of turtles experienced post-surgical regrowth within an average
of 36 days (Page-Karjian et al. 2014). In line with this, in our current study
50% of turtles experienced FP regrowth within 40 days. Of the 33 tumour
clusters surgically removed from these 4 patients, one third resulted in tumour
regrowth. This is slightly less than the 60% tumour regrowth observed in
previous studies (Page-Karjian et al. 2014).
The growth measurement protocol adopted in this study can be further
improved for future research in order to increase its accuracy and the level
of detailed analysis which is possible. Photos could be taken at a fixed
distance and at a consistent angle for each tumour cluster, and physical
measurements using callipers could be used to record accurate tumour
dimensions. While providing more precise data, these physical methods,
however, are considerably more time-consuming. Thus they are less likely to
be broadly adopted across many rehabilitation facilities, which are generally
time- and resource-limited.
Interestingly, this study suggests that the aggressiveness of the pre-surgery
growth rates do not have a bearing on the occurrence of post-surgery
tumour regrowth rates. Therefore, regrowth may be driven predominantly
by other factors such as inherent genetic/viral features of each tumour,
or tumour cells/tumour stem cells remaining in the body site post-surgery
(deeper surgical margins may alleviate this, although these are not possible
in some locations such as the eye). In line with the potential drivers of FP
regrowth, we have recently shown that adjunct post-surgery treatment with
the anti-cancer drug fluorouracil can help to dramatically reduce FP eye
tumour regrowth (Duffy et al. 2018).
The analysis of tumour growth in these four patients provides a useful
baseline with which to compare FP tumour growth rates in C. mydas
given novel FP treatments. Future studies can compare this baseline with
growth post-candidate drug treatment. Additionally, these data will provide
useful baseline information for studies investigating the effect of potential
environmental aggravators of FP tumour growth, such as UV exposure
and pollutant exposure (Keller et al. 2014; Jones et al. 2016; Duffy et al.
2018). If growth and regrowth rates can be reduced from the baseline rates
indicated in this study, it could eliminate the need for multiple rounds of
© British Chelonia Group + Jessica Farrell, Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
28 Testudo Vol. 8, No. 5
surgery, consequently decreasing the stress on the patient and increasing
their chances of successful re-introduction to their wild population. At a time
when anthropogenic factors are accelerating disease emergence and species
extinction (Whilde et al. 2017), it is vital to not only expand our scientific
understanding of the mechanics of diseases such as fibropapillomatosis,
but to use the knowledge gained to improve the care and recovery of
endangered animal populations.
Acknowledgements
Funding was generously provided by a grant awarded from the Sea Turtle
Grants Program, project number 17-033R, which is funded from proceeds from
the sale of the Florida Sea Turtle License Plate (www.helpingseaturtles.org) and
administered by The Sea Turtle Conservancy, by the Save Our Seas Foundation
under project number SOSF 356, and by a Welsh Government Sêr Cymru II
and the European Union’s Horizon 2020 research and innovation programme
under the Marie Skłodowska-Curie grant agreement No. 663830-BU115.
This research was also supported by Gumbo Limbo Nature Center, Inc d/b/a
Friends of Gumbo Limbo (a 501c3 non-profit organization) through a generous
donation through their Graduate Research Grant programme. Warmest thanks
are due to Catherine Eastman, Dr Brooke Burkhalter, Devon Rollinson, Dr Jenny
Whilde, the volunteers of UF’s Sea Turtle Hospital at the Whitney Laboratory
and to Nancy Condron and the Mickler’s Landing Sea Turtle Patrol.
References
Cruz Sr, E. (1985). Saga of the Sea Turtle. Privately published, Florida, USA.
Dos Santos, R.G., Martins, A.S., Torezani, E., Baptistotte, C., Julyana da Nóbrega,
F., Horta, P., Work, T.M. & Balazs, G. (2010). Relationship between
fibropapillomatosis and environmental quality: a case study with Chelonia
mydas off Brazil. Diseases of Aquatic Organisms 89: 87-95.
Duarte, A., Faísca, P., Loureiro, N.S., Rosado, R., Gil, S., Pereira, N. & Tavares, L.
(2012). First histological and virological report of fibropapilloma associated
with herpesvirus in Chelonia mydas at Príncipe Island, West Africa. Archives of
Virology 157: 1155-1159.
Duffy, D.J., Schnitzler, C., Karpinski, L., Thomas, R., Whilde, J., Eastman, C.,
Yang, C., Krstic, A., Rollinson, D., Zirkelbach, B., Yetsko, K., Burkhalter, B &
Martindale, M.Q. (2018). Sea turtle fibropapilloma tumors share genomic
drivers and therapeutic vulnerabilities with human cancers. Communications
Biology 1(1): 63.
Foley, A.M., Minch, K., Hardy, R., Bailey, R., Schaf, S. & Young, M. (2015).
Distributions, relative abundances, and mortality factors of sea turtles in Florida
during 1980-2014 as determined from strandings. Fish and Wildlife Research
Institute, Jacksonville Field Laboratory, Jacksonville, Florida, USA.
© British Chelonia Group + Jessica Farrell, ~Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
Testudo Vol. 8, No. 5 29
Hargrove, S., Work, T., Brunson, S., Foley, A.M. & Balazs, G. (2016). Proceedings of
the 2015 international summit on fibropapillomatosis: global status, trends,
and population impacts. In: U.S. Department of Commerce, NOAA Technical
Memorandum, NOAA-TM-NMFS-PIFSC-54, 87pp.
Herbst, L.H., Jacobson, E.R., Moretti, R., Brown, T., Sundberg, J.P. & Klein, P.A.
(1995). Experimental transmission of green turtle fibropapillomatosis using cell-
free tumor extracts. Diseases of Aquatic Organisms 22: 1-12.
ImageJ (2018). NIH Image/Image J. Available at: https://imagej.nih.gov/ij. Last
accessed 30th April 2018.
IUCN (2018). The IUCN Red List of Threatened Species.
Available at: http://www.iucnredlist.org/. Last accessed 30th April 2018.
Jones, K., Ariel, E., Burgess, G. & Read, M. (2016). A review of fibropapillomatosis in
green turtles (Chelonia mydas). The Veterinary Journal 212: 48-57.
Keller, J.M., Balazs, G.H., Nilsen, F., Rice, M., Work, T.M. & Jensen, B.A. (2014).
Investigating the potential role of persistent organic pollutants in Hawaiian
green sea turtle fibropapillomatosis. Environmental Science Technology 48(14):
7807-7816.
Morrison, C.L., Iwanowicz, L., Work, T.M., Fahsbender, E., Breitbart, M., Adams, C.,
Iwanowicz, D., Sanders, L., Ackermann, M. & Cornman, R.S. (2018). Genomic
evolution, recombination, and inter-strain diversity of chelonid alphaherpesvirus
5 from Florida and Hawaii green sea turtles with fibropapillomatosis. PeerJ 6:
e4386.
Page-Karjian, A., Norton, T.M., Krimer, P., Groner, M., Nelson, S.E. Jr & Gottdenker,
N.L. (2014). Factors influencing survivorship of rehabilitating green sea turtles
(Chelonia mydas) with fibropapillomatosis. Journal of Zoo and Wildlife Medicine
45: 507-519.
Rossi, S., Sánchez-Sarmiento, A.M., Vanstreels, R.E.T., dos Santos, R.G., Prioste,
F.E.S., Gattamorta, M.A., Grisi-Filho, J.H.H. & Matushima, E.R. (2016).
Challenges in evaluating the severity of fibropapillomatosis: a proposal for
objective index and score system for green sea turtles (Chelonia mydas) in
Brazil. PLOS ONE 11: e0167632.
Smith, G.M. & Coates, C.W. (1938). Fibro-epithelial growths of the skin in large
marine turtles, Chelonia mydas (Linnaeus). Zoologica 23: 93-98.
Whilde, J., Martindale, M.Q. & Duffy, D.J. (2017). Precision wildlife medicine:
applications of the human-centred precision medicine revolution to species
conservation. Global Change Biology 23: 1792-1805.
Work, T.M. & Balazs, G.H. (1999). Relating tumor score to haematology in green turtles
with fibropapillomatosis in Hawaii. Journal of Wildlife Diseases 35: 804-807.
Work, T.M., Dagenais, J., Weatherby, T.M., Balazs, G.H. & Ackermann, M. (2017).
In-vitro replication of chelonid herpesvirus 5 in organotypic skin cultures from
Hawaiian green turtles (Chelonia mydas). Journal of Virology 91: e00404-17.
© British Chelonia Group + Jessica Farrell, Rachel
Thomas, Mark Q. Martindale and David J. Duffy,
2018
... However, this hypothesis that progression and regression relate to tumor morphology has not been further tested or verified in a controlled setting. Generally, FP tumor growth-rate patterns in hospitalized green turtles might have a role in disease severity and outcome [33]. To our knowledge, there have been no clinical studies on FP tumor growth rates with active differentiation of lesions based on morphological characteristics. ...
... Generally, FP tumor growth-rate patterns in hospitalized green turtles might have a role in disease severity and outcome [33]. To our knowledge, there have been no clinical studies on FP tumor growth rates with active differentiation of lesions based on morphological characteristics. ...
... Our study is based on previously described methodology that used ImageJ to track FP tumor growth rates in hospitalized individuals [33]. We calculated FP tumor growth based on measurements from photographs of nine rehabilitating green turtles (Cm 1-9) hospitalized at the UFWLSTH during 2015-2021. ...
Article
Full-text available
Fibropapillomatosis (FP) is a neoplastic disease most often found in green turtles (Chelonia mydas). Afflicted turtles are burdened with potentially debilitating tumors concentrated externally on the soft tissues, plastron, and eyes and internally on the lungs, kidneys, and the heart. Clinical signs occur at various levels, ranging from mild disease to severe debilitation. Tumors can both progress and regress in affected turtles, with outcomes ranging from death due to the disease to complete regression. Since its official description in the scientific literature in 1938, tumor growth rates have been rarely documented. In addition, FP tumors come in two very different morphologies; yet, to our knowledge, there have been no quantified differences in growth rates between tumor types. FP tumors are often rugose in texture, with a polypoid to papillomatous morphology, and may or may not be pedunculated. In other cases, tumors are smooth, with a skin-like surface texture and little to no papillose structures. In our study, we assessed growth-rate differences between rugose and smooth tumor morphologies in a rehabilitation setting. We measured average biweekly tumor growth over time in green turtles undergoing rehabilitation at the University of Florida Whitney Laboratory Sea Turtle Hospital in St. Augustine, Florida, and compared growth between rugose and smooth tumors. Our results demonstrate that both rugose and smooth tumors follow a similar active growth progression pattern, but rugose tumors grew at significantly faster rates (p = 0.013) than smooth ones. We also documented regression across several examined tumors, ranging from −0.19% up to −10.8% average biweekly negative growth. Our study offers a first-ever assessment of differential growth between tumor morphologies and an additional diagnostic feature that may lead to a more comprehensive understanding and treatment of the disease. We support the importance of tumor morphological categorization (rugose versus smooth) being documented in future FP hospital- and field-based health assessments.
... Elevated chronic stress conditions resulting from human activities from highly urbanized areas can potentially suppress wildlife immune systems and trigger or exacerbate infection [73]. Sea turtle populations dwelling in urbanized coastal environments have been repeatedly found to present elevated FP prevalence [61,[74][75][76][77][78][79]. Habitat loss, human presence, fishing, boating, and encroachment resulting from proximity to anthropogenic areas can significantly stress sea turtle populations. ...
... River discharge from densely populated areas accounts for high amounts of pollution affecting nearshore water quality, showing a positive correlation with FP prevalence in green turtles [66,86]. The negative impact of environmental contaminants from wastewater on sea turtle health has been discussed since 1995 [59], and there has been increasing evidence and support on the matter [61,74,[76][77][78][79]84]. Findings from Brazil, for example, support the association between water quality and FP as degraded habitats reported higher prevalence (58.3%) compared to other areas of the country (15.4%) [74]. ...
... Herbst et al. observed that higher water temperatures experimentally promoted FP tumor growth, while lower temperatures delayed their onset [59]. Moreover, in rehabilitation facilities, green turtles have a higher chance of FP development during the warmer months [79]. Therefore, climate change and consequent extreme sea water temperatures are potentially additional anthropogenic contributions behind FP dynamics. ...
Article
Full-text available
Emerging infectious diseases of wildlife have markedly increased in the last few decades. Unsustainable, continuous, and rapid alterations within and between coupled human and natural systems have significantly disrupted wildlife disease dynamics. Direct and indirect anthropogenic effects, such as climate change, pollution, encroachment, urbanization, travel, and trade, can promote outbreaks of infectious diseases in wildlife. We constructed a coupled human and natural systems framework identifying three main wildlife disease risk factors behind these anthropogenic effects: (i) immune suppression, (ii) viral spillover, and (iii) disease propagation. Through complex and convoluted dynamics, each of the anthropogenic effects and activities listed in our framework can lead, to some extent, to one or more of the identified risk factors accelerating disease outbreaks in wildlife. In this review, we present a novel framework to study anthropogenic effects within coupled human and natural systems that facilitate the emergence of infectious disease involving wildlife. We demonstrate the utility of the framework by applying it to Fibropapillomatosis disease of marine turtles. We aim to articulate the intricate and complex nature of anthropogenically exacerbated wildlife infectious diseases as multifactorial. This paper supports the adoption of a One Health approach and invites the integration of multiple disciplines for the achievement of effective and long-lasting conservation and the mitigation of wildlife emerging diseases.
... From the data collected in our study, a maximum of 15 tumours per individual were identified, this is low compared to cases reported in Brazil, where up to 129 tumours per turtle have been found (Rossi et al. 2016), but it coincides with reports from Costa Rica (Brenes et al. 2013), where a maximum of 12 tumours per individual was found in nesting olive ridley turtles. The predominance of small tumours is consistent with the findings in other studies from the Mexican Pacific (Gámez et al. 2009) and Gulf of Mexico (Suárez-Domínguez et al. 2020) but differ from those reported in places where the prevalence of FP is high, such as Hawaii and Florida, where it is common that tumours exceed 10 cm in diameter (Work et al. 2004;Farrell et al. 2018). The differences between the sizes of the tumours may be because the turtles in regions like Hawaii and Florida have presence of the disease for a longer time, and as the disease progresses, the lesions increase in size (Farrell et al. 2018). ...
... The predominance of small tumours is consistent with the findings in other studies from the Mexican Pacific (Gámez et al. 2009) and Gulf of Mexico (Suárez-Domínguez et al. 2020) but differ from those reported in places where the prevalence of FP is high, such as Hawaii and Florida, where it is common that tumours exceed 10 cm in diameter (Work et al. 2004;Farrell et al. 2018). The differences between the sizes of the tumours may be because the turtles in regions like Hawaii and Florida have presence of the disease for a longer time, and as the disease progresses, the lesions increase in size (Farrell et al. 2018). The anatomical distribution of the tumours was predominant in the anterior region of the body, like what is reported in other regions of the EP (Aguirre et al. 1999;Reséndiz et al. 2015), north Pacific (Work et al. 2004) and Gulf of Mexico (Suárez-Domínguez et al. 2020). ...
Article
Full-text available
Fibropapillomatosis (FP) - tumour-associated chelonid alphaherpesvirus 5 (ChHV5; Scutavirus chelonidalpha5) - is a disease that affect marine turtles around the world, and characterized by the formation of cutaneous tumours that can appear anywhere on the body. We carried out a thorough literature search (from 1990 to 2024) in the feeding sites of North-western Mexico, a region that hosts important habitats for feeding, development, and reproduction for five of the seven existing sea turtle species. We found 18 reports recording a total of 32 cases of FP and/or ChHV5/Scutavirus chelonidalpha5 in coastal and insular areas of North-western Mexico. Baja California Sur resulted with the highest number of cases (75%). While the first case of ChHV5/Scutavirus chelonidalpha5 infection was reported in 2004, the presence of FP tumours was reported in 2014 and became more frequent between 2019 and 2024. The affected species were black, Chelonia mydas (50%), olive ridley, Lepidochelys olivacea (46.8%) and loggerhead turtles, Caretta caretta (3.2%). Tumours occurred mainly in anterior flippers (46.1%) and neck (22.5%), and most had a nodular and verrucous appearance with a rough surface. In the study region, there is a potential sign of the emergence of the ChHV5/Scutavirus chelonidalpha5 infections and FP disease during the last 20 years, with a rapid increase during the last 10 years. As long as infections by ChHV5/Scutavirus chelonidalpha5 and the prevalence of the FP disease may be potentially influenced by anthropogenic activities, a One Health approach is needed to understand and improve sea turtles’ health.
... Temperatures in our Florida in-water dataset ranged from 24.7 • C to 27.3 • C, with an FP prevalence of 50-60% observed mostly around 26 • C. Studies witnessing higher water temperature effects on tumor growth of hospitalized sea turtles had a similar temperature range in rehabilitation tanks (23 • C to 27 • C) [60]. Further studies in rehab facilities observed the same pattern of a higher likelihood of green turtles' FP development during the warmer months [22]. This pattern could be attributable to pathogenic behavior, often showing a trend of higher growth rate and reproductive output at higher temperatures [25]. ...
... For sea turtles, the negative effects of environmental contaminants from wastewater were already discussed in 1995, as research indicated environmental pollutants greatly impact turtle health [19,76]. Sea turtle populations living in heavily polluted coastal environments were repeatedly found to present elevated FP prevalence [15,22,[28][29][30][31]50]. Research observed a substantially lower FP prevalence in open ocean sites compared to a coastal lagoon (Indian River Lagoon) which is heavily degraded by urban development and polluted from local drainage system inputs [4]. ...
Article
Full-text available
Fibropapillomatosis is a neoplastic disease of marine turtles, with green turtles (Chelonia mydas) being the most affected species. Fibropapillomatosis causes debilitating tumor growths on soft tissues and internal organs, often with lethal consequences. Disease incidence has been increasing in the last few decades and the reason is still uncertain. The potential viral infectious agent of Fibropapillomatosis, chelonid herpesvirus 5, has been co-evolving with its sea turtle host for millions of years and no major mutation linked with increased disease occurrence has been detected. Hence, frequent outbreaks in recent decades are likely attributable to external drivers such as large-scale anthropogenic changes in the green turtle coastal marine ecosystem. This study found that variations in sea surface temperature, salinity, and nutrient effluent discharge from nearby rivers were correlated with an increased incidence of the disease, substantiating that these may be among the significant environmental drivers impacting Fibropapillomatosis prevalence. This study offers data and insight on the need to establish a baseline of environmental factors which may drive Fibropapillomatosis and its clinical exacerbation. We highlight the multifactorial nature of this disease and support the inclusion of interdisciplinary work in future Fibropapillomatosis research efforts.
... While sea turtle species' ranges and distributions have altered over the years, so too have those of their pathogens, including fibropapillomatosis (FP), now afflicting every sea turtle species in every ocean globally Farrell et al., 2018;Farrell, Yetsko, et al., 2021;Jones et al., 2016;Smith & Coates, 1938;Williams et al., 1994;Yetsko et al., 2021). We recently employed eDNA-based approaches to study the shedding of the virus (ChHV5) associated with this disease, and these results, combined with the results of this study, can provide insight into the health and population status of wild sea turtles inhabiting our study sites Yetsko et al., 2020). ...
... Indeed, some of the rehabilitation water and sand eDNA samples utilized for sea turtle detection in the present study, were also simultaneously utilized to quantify a viral pathogen of sea turtles . This pathogen is a turtlespecific ChHV5 virus and can result in the tumor disease, fibropapillomatosis (FP) (Chaves et al., 2017;Farrell et al., 2018;Farrell, Yetsko, et al., 2021;Page-Karjian et al., 2015Work et al., 2015Work et al., , 2020Yetsko et al., 2021). We previously adapted the eDNA methodology described here to successfully detect, quantify, and temporally track the concentration of ChHV5 DNA in water (qPCR and shotgun sequencing) and sand (qPCR only) samples in a controlled rehabilitation setting Yetsko et al., 2021). ...
Article
Elusive aquatic wildlife, such as endangered sea turtles, are difficult to monitor and conserve. As novel molecular and genetic technologies develop, it is possible to adapt and optimize them for wildlife conservation. One such technology is environmental (e)DNA – the detection of DNA shed from organisms into their surrounding environments. We developed species‐specific green (Chelonia mydas) and loggerhead (Caretta caretta) sea turtle probe‐based qPCR assays, which can detect and quantify sea turtle eDNA in controlled (captive tank water and sand samples) and free ranging (oceanic water samples and nesting beach sand) settings. eDNA detection complemented traditional in‐water sea turtle monitoring by enabling detection even when turtles were not visually observed. Furthermore, we report that high throughput shotgun sequencing of eDNA sand samples enabled sea turtle population genetic studies and pathogen monitoring, demonstrating that non‐invasive eDNA techniques are viable and efficient alternatives to biological sampling (e.g. biopsies and blood draws). Genetic information was obtained from sand many hours after nesting events, without having to observe or interact with the target individual. This greatly reduces the sampling stress experienced by nesting mothers and emerging hatchlings, and avoids sacrificing viable eggs for genetic analysis. The detection of pathogens from sand indicates significant potential for increased wildlife disease monitoring capacity and viral variant surveillance. Together, these results demonstrate the potential of eDNA approaches to ultimately help understand and conserve threatened species such as sea turtles.
... Many of these ailments are due to anthropogenic interactions such as boat strikes, fishing line/hook entanglements, and ingestion of large quantities of plastic (Bjorndal et al. 1994;Chaloupka et al. 2008;Barreiros 2015;Eastman et al. 2020). Marine turtles, particularly green sea turtles (Chelonia mydas), also strand afflicted by virulent tumours, fibropapillomatosis (FP) (Foley et al. 2007;Chaloupka et al. 2008;Page-Karjian et al. 2014;Duffy et al. 2018;Farrell et al. 2018;Whilde et al. 2019;Yetsko et al. 2021), the incidence of which correlated to humaninduced alterations to inshore habitats (Van Houtan et al. 2010;Hargrove et al. 2016;Jones et al. 2016). Currently, surgery is the primary treatment for turtles with FP, but post-surgical tumour regrowth is common, prolonging rehabilitation (Page-Karjian et al. 2012;Duffy et al. 2018;Farrell et al. 2018;Whilde et al. 2019). ...
... Marine turtles, particularly green sea turtles (Chelonia mydas), also strand afflicted by virulent tumours, fibropapillomatosis (FP) (Foley et al. 2007;Chaloupka et al. 2008;Page-Karjian et al. 2014;Duffy et al. 2018;Farrell et al. 2018;Whilde et al. 2019;Yetsko et al. 2021), the incidence of which correlated to humaninduced alterations to inshore habitats (Van Houtan et al. 2010;Hargrove et al. 2016;Jones et al. 2016). Currently, surgery is the primary treatment for turtles with FP, but post-surgical tumour regrowth is common, prolonging rehabilitation (Page-Karjian et al. 2012;Duffy et al. 2018;Farrell et al. 2018;Whilde et al. 2019). As captive environments are more restrictive and simplistic than natural ones, longer rehabilitation periods further curtail turtles' abilities to exhibit their full range of natural behaviours. ...
Article
Full-text available
Wild sea turtles that are admitted to turtle hospitals and rehabilitation centers suffering from illnesses and injuries may be held for extended periods of months to years, until they are recovered and ready for release back to the wild. During this time, natural behaviors may be limited, potentially adversely affecting the long-term rehabilitation success, however, little research has been carried out on the behavior of hospitalized sea turtles. Here we report that environmental enrichment can be an effective means of encouraging natural behaviors in turtles in hospital/rehabilitation and aquarium settings, but find that enrichment should be monitored and tailored to individual turtles to achieve positive results.
... First described in the scientific literature in the 1930 s [9], This disease is most prevalent in green turtles (Chelonia mydas), which also tend to be the most severely afflicted; however, FP has been documented, to a lesser extent, in all other species [5,7,10,11]. Fibropapillomatosis manifests as multiple tumours that primarily arise from the soft tissues of sea turtles, including: cutaneous, ocular and visceral tumours (fibromas, fibrosarcomas, mixofibromas and mixomas), which can vary in size and distribution [12,13]. These tumours can be severely debilitating; impairing vision, locomotion, feeding, predator evasion and other natural behaviours, and preventing affected turtles from providing their valuable ecosystem services and keystone species functions [1,11,12,14,15]. ...
... Fibropapillomatosis is one of the most significant transmissible diseases known in sea turtles and remains a persistent health concern despite conservation successes and significant growth of some affected populations [17]. The FP epizootic has been identified as one of the five major threats to sea turtles, which has been reflected in the renewed scientific interest in this disease in the last decade [5,7,11,13,[18][19][20][21][22][23][24][25][26]. Prevalence statistics reveal the rapid establishment of FP among many sea turtle populations, with reported increases from 13.3 to 42% in Florida, USA (2005-2016), 13.2 to 35.3% in northeastern Brazil (2012)(2013)(2014)(2015), 0% to 33% in Guinea-Bissau (2009-2019) and 0.6% to 35.2% in Texas, USA (2010USA ( -2018 [7,17,[27][28][29][30][31]. ...
Article
Full-text available
The spreading global sea turtle fibropapillomatosis (FP) epizootic is threatening some of Earth’s ancient reptiles, adding to the plethora of threats faced by these keystone species. Understanding this neoplastic disease and its likely aetiological pathogen, chelonid alphaherpesvirus 5 (ChHV5), is crucial to understand how the disease impacts sea turtle populations and species and the future trajectory of disease incidence. We generated 20 ChHV5 genomes, from three sea turtle species, to better understand the viral variant diversity and gene evolution of this oncogenic virus. We revealed previously underappreciated genetic diversity within this virus (with an average of 2035 single nucleotide polymorphisms (SNPs), 1.54% of the ChHV5 genome) and identified genes under the strongest evolutionary pressure. Furthermore, we investigated the phylogeny of ChHV5 at both genome and gene level, confirming the propensity of the virus to be interspecific, with related variants able to infect multiple sea turtle species. Finally, we revealed unexpected intra-host diversity, with up to 0.15% of the viral genome varying between ChHV5 genomes isolated from different tumours concurrently arising within the same individual. These findings offer important insights into ChHV5 biology and provide genomic resources for this oncogenic virus.
... Fibropapillomatosis manifests as multiple tumours that primarily arise from the soft tissues of sea turtles including: cutaneous, ocular and visceral tumours, which can vary in size and distribution [12,13]. These tumours can be severely debilitating; impairing vision, locomotion, feeding, predator evasion and other natural behaviours, and preventing affected turtles from providing their valuable ecosystem services and keystone species functions [1,11,12,14,15]. ...
... Fibropapillomatosis is one of the most significant transmissible diseases known in marine turtles and remains a persistent health concern despite conservation successes and significant growth of some affected populations [17]. The FP epizootic has been identified as one of the five major threats to marine turtles, which has been reflected in the renewed scientific interest in this disease in the last decade [5,7,11,13,[18][19][20][21][22][23][24][25][26]. Prevalence statistics reveal the rapid establishment of FP among many sea turtle populations; with reported increases from 13.3 to 42% in Florida, USA (2005-2016), 13.2 to 35.3% in northeastern Brazil (2012)(2013)(2014)(2015), 0% to 33% in Guinea-Bissau and 0 to 35.2% in Texas, USA [7,17,[27][28][29][30][31]. ...
Preprint
Full-text available
The spreading global sea turtle fibropapillomatosis (FP) epizootic is threatening some of Earth’s ancient reptiles, adding to the plethora of threats faced by these keystone species. Understanding this neoplastic disease, and its likely aetiological pathogen, chelonid alphaherpesvirus 5 (ChHV5), is crucial to understand how the disease impacts sea turtle populations and species and the future trajectory of disease incidence. We generated 20 ChHV5 genomes, from three sea turtle species, to better understand the viral variant diversity and gene evolution of this oncogenic virus. We revealed previously underappreciated genetic diversity within this virus (with an average of 2,035 single nucleotide polymorphisms [SNPs], 1.54% of the ChHV5 genome) and identified genes under the strongest evolutionary pressure. Furthermore, we investigated the phylogeny of ChHV5 at both genome and gene level, confirming the propensity of the virus to be interspecific with related variants able to infect multiple sea turtle species. Finally, we revealed unexpected intra-host diversity, with up to 0.15% of the viral genome varying between ChHV5 genomes isolated from different tumours concurrently arising within the same individual. These findings offer important insights into ChHV5 biology and provide genomic resources for this oncogenic virus.
... S ea turtle fibropapillomatosis (FP) is an epizootic (animal epidemic) tumor disease, affecting endangered sea turtles worldwide [1][2][3][4][5] . The disease is characterized by the formation of cutaneous and internal fibro-epithelial tumors, which can lead to debilitation and death. ...
... However, Koch's postulates to confirm its causative role have yet to be fulfilled, because ChHV5 is extremely difficult to isolate and propagate in the laboratory 3,5,[34][35][36][37] . Similarly, despite advances in FP tumor research 1,3,5,30,31,[38][39][40][41][42][43][44][45][46] , many open questions remain regarding the role of ChHV5 in driving FP tumorigenesis, including whether it is a cause of the disease or an opportunistic pathogen, exploiting immunocompromised tumor-afflicted turtles 3,5,31 . Interestingly, levels of ChHV5 (ChHV5 gB and UL30 gene DNA detected by qPCR, and ChHV5 glycoprotein H peptides detected by ELISA) in clinically healthy turtles are closer to that of FP tumors, than in non-tumored tissue of FP-afflicted turtles 34,47 . ...
Article
Full-text available
Pathogen-induced cancers account for 15% of human tumors and are a growing concern for endangered wildlife. Fibropapillomatosis is an expanding virally and environmentally co-induced sea turtle tumor epizootic. Chelonid herpesvirus 5 (ChHV5) is implicated as a causative virus, but its transmission method and specific role in oncogenesis and progression is unclear. We applied environmental (e)DNA-based viral monitoring to assess viral shedding as a direct means of transmission, and the relationship between tumor burden, surgical resection and ChHV5 shedding. To elucidate the abundance and transcriptional status of ChHV5 across early, established, regrowth and internal tumors we conducted genomics and transcriptomics. We determined that ChHV5 is shed into the water column, representing a likely transmission route, and revealed novel temporal shedding dynamics and tumor burden correlations. ChHV5 was more abundant in the water column than in marine leeches. We also revealed that ChHV5 is latent in fibropapillomatosis, including early stage, regrowth and internal tumors; higher viral transcription is not indicative of poor patient outcome, and high ChHV5 loads predominantly arise from latent virus. These results expand our knowledge of the cellular and shedding dynamics of ChHV5 and can provide insights into temporal transmission dynamics and viral oncogenesis not readily investigable in tumors of terrestrial species.
... Examples of the use of species-specific PCR in marine biosecurity include application to the Atlantic wedge clam (Rangia cuneata), the soft-shell clam (Mya arenaria), and the Australian tubeworm (Ficopomatus enigmaticus; Zaiko et al. 2018). Therefore, it is evident that eDNA has already been successfully implemented in numerous scientific studies, including one of our two case studies, the fibropapillomatosis panzootic in green sea turtles (Chelonia mydas; Work et al. 2015, Chaves et al. 2017, Page-Karjian et al. 2017, Farrell et al. 2018, Yetsko et al. 2021. ...
... One pathogen of particular concern in relation to the conservation of endangered marine turtle species and the monitoring of harmful pathogens is the turtle-specific DNA virus, chelonid herpesvirus 5 (ChHV5; Chaves et al. 2017, Yetsko et al. 2021. This alphaherpesvirus has been identified as the most likely etiological agent of a devastating neoplastic disease, fibropapillomatosis, affecting all seven species of sea turtle, particularly juvenile green sea turtles (Chelonia mydas) found in tropical and subtropical oceans worldwide (Chaves et al. 2017, Farrell et al. 2018. Fibropapillomatosis can result in fatalities through both direct and indirect mechanisms. ...
Article
Novel forensics-inspired molecular approaches have revolutionized species detection in the wild and are particularly useful for tracing endangered or invasive species. These new environmental DNA or RNA (eDNA or eRNA)-based techniques are now being applied to human and animal pathogen surveillance, particularly in aquatic environments. They allow better disease monitoring (presence or absence and geographical spread) and understanding of pathogen occurrence and transmission, benefitting species conservation and, more recently, our understanding of the COVID-19 global human pandemic. In the present article, we summarize the benefits of eDNA-based monitoring, highlighted by two case studies: The first is a fibropapillomatosis tumor-associated herpesvirus (chelonid herpesvirus 5) driving a sea turtle panzootic, and the second relates to eRNA-based detection of the SARS-CoV-2 coronavirus driving the COVID-19 human pandemic. The limitations of eDNA-or eRNA-based approaches are also summarized, and future directions and recommendations of the field are discussed. Continuous eDNA-or eRNA-based monitoring programs can potentially improve human and animal health by predicting disease outbreaks in advance, facilitating proactive rather than reactive responses.
Article
Full-text available
Wildlife populations are under intense anthropogenic pressures, with the geographic range of many species shrinking, dramatic reductions in population numbers and undisturbed habitats, and biodiversity loss. It is postulated that we are in the midst of a sixth (Anthropocene) mass extinction event, the first to be induced by human activity. Further, threatening vulnerable species is the increased rate of emerging diseases, another consequence of anthropogenic activities. Innovative approaches are required to help maintain healthy populations until the chronic underlying causes of these issues can be addressed. Fibropapillomatosis in sea turtles is one such wildlife disease. Here, we applied precision-medicine-based approaches to profile fibropapillomatosis tumors to better understand their biology, identify novel therapeutics, and gain insights into viral and environmental triggers for fibropapillomatosis. We show that fibropapillomatosis tumors share genetic vulnerabilities with human cancer types, revealing that they are amenable to treatment with human anti-cancer therapeutics.
Article
Full-text available
Chelonid alphaherpesvirus 5 (ChHV5) is a herpesvirus associated with fibropapillomatosis (FP) in sea turtles worldwide. Single-locus typing has previously shown differentiation between Atlantic and Pacific strains of this virus, with low variation within each geographic clade. However, a lack of multi-locus genomic sequence data hinders understanding of the rate and mechanisms of ChHV5 evolutionary divergence, as well as how these genomic changes may contribute to differences in disease manifestation. To assess genomic variation in ChHV5 among five Hawaii and three Florida green sea turtles, we used high-throughput short-read sequencing of long-range PCR products amplified from tumor tissue using primers designed from the single available ChHV5 reference genome from a Hawaii green sea turtle. This strategy recovered sequence data from both geographic regions for approximately 75% of the predicted ChHV5 coding sequences. The average nucleotide divergence between geographic populations was 1.5%; most of the substitutions were fixed differences between regions. Protein divergence was generally low (average 0.08%), and ranged between 0 and 5.3%. Several atypical genes originally identified and annotated in the reference genome were confirmed in ChHV5 genomes from both geographic locations. Unambiguous recombination events between geographic regions were identified, and clustering of private alleles suggests the prevalence of recombination in the evolutionary history of ChHV5. This study significantly increased the amount of sequence data available from ChHV5 strains, enabling informed selection of loci for future population genetic and natural history studies, and suggesting the (possibly latent) co-infection of individuals by well-differentiated geographic variants.
Article
Full-text available
Fibropapillomatosis (FP) is a tumor disease of marine turtles associated with chelonid herpesvirus 5 (ChHV5), which has historically been refractory to growth in tissue culture. Here we show, for the first time, de novo formation of ChHV5-positive intranuclear inclusions in cultured green turtle cells, which is indicative of active lytic replication of the virus. The minimal requirements to achieve lytic replication in cultured cells included (i) either in vitro cultures of ChHV5-positive tumor biopsy specimens (plugs) or organotypic cultures (rafts) consisting of ChHV5-positive turtle fibroblasts in collagen rafts seeded with turtle keratinocytes and (ii) keratinocyte maturation induced by raising raft or biopsy cultures to the air-liquid interface. Virus growth was confirmed by detailed electron microscopic studies that revealed intranuclear sun-shaped capsid factories, tubules, various stages of capsid formation, nuclear export by budding into the perinuclear space, tegument formation, and envelopment to complete de novo virus production. Membrane synthesis was also observed as a sign of active viral replication. Interestingly, cytoplasmic particles became associated with keratin filaments, a feature not seen in conventional monolayer cell cultures, in which most studies of herpesvirus replication have been performed. Our findings draw a rich and realistic picture of ChHV5 replication in cells derived from its natural host and may be crucial not only to better understand ChHV5 circulation but also to eventually complete Koch's postulates for FP. Moreover, the principles described here may serve as a model for culture of other viruses that are resistant to replication in conventional cell culture. IMPORTANCE A major challenge in virology is the study of viruses that cannot be grown in the laboratory. One example is chelonid herpesvirus 5 (ChHV5), which is associated with fibropapillomatosis, a globally distributed, debilitating, and fatal tumor disease of endangered marine turtles. Pathological examination shows that ChHV5 is shed in skin. Here we show that ChHV5 will grow in vitro if we replicate the complex three-dimensional structure of turtle skin. Moreover, lytic virus growth requires a close interplay between fibroblasts and keratinocytes. Finally, the morphogenesis of herpesviral growth in three-dimensional cultures reveals a far richer, and likely more realistic, array of capsid morphologies than that encountered in traditional monolayer cell cultures. Our findings have applications to other viruses, including those of humans.
Article
Full-text available
Fibropapillomatosis (FP) is a neoplastic disease that affects marine turtles worldwide, especially green sea turtles (Chelonia mydas). FP tumors can develop on the body surface of marine turtles and also internally in the oral cavity and viscera. Depending on their quantity, size and anatomical distribution, these tumors can interfere with hydrodynamics and the ability to feed, hence scoring systems have been proposed in an attempt to quantify the clinical manifestation of FP. In order to establish a new scoring system adapted to geographic regions, we examined 214 juvenile green sea turtles with FP caught or rescued at Brazilian feeding areas, counted their 7466 tumors and classified them in relation to their size and anatomical distribution. The patterns in quantity, size and distribution of tumors revealed interesting aspects in the clinical manifestation of FP in specimens studied in Brazil, and that FP scoring systems developed for other areas might not perform adequately when applied to sea turtles on the Southwest Atlantic Ocean. We therefore propose a novel method to evaluate the clinical manifestation of FP: fibropapillomatosis index (FPI) that provides the Southwest Atlantic fibropapillomatosis score (FPSSWA). In combination, these indexing and scoring systems allow for a more objective, rapid and detailed evaluation of the severity of FP in green sea turtles. While primarily designed for the clinical manifestation of FP currently witnessed in our dataset, this index and the score system can be adapted for other areas and compare the characteristics of the disease across regions. In conclusion, scoring systems to classify the severity of FP can assist our understanding on the environmental factors that modulate its development and its impacts on the individual and population health of green sea turtles.
Article
Full-text available
Despite being identified in 1938, many aspects of the pathogenesis and epidemiology of fibropapillomatosis (FP) in marine turtles are yet to be fully uncovered. Current knowledge suggests that FP is an emerging infectious disease, with the prevalence varying both spatially and temporally, even between localities in close proximity to each other. A high prevalence of FP in marine turtles has been correlated with residency in areas of reduced water quality, indicating that there is an environmental influence on disease presentation. Chelonid herpesvirus 5 (ChHV5) has been identified as the likely aetiological agent of FR The current taxonomic position of ChHV5 is in the family Herpesviridae, subfamily Alphahmesvirinae, genus Scutavirus. Molecular differentiation of strains has revealed that a viral variant is typically present at specific locations, even within sympatric species of marine turtles, indicating that the disease FP originates regionally. There is uncertainty surrounding the exact path of transmission and the conditions that facilitate lesion development, although recent research has identified atypical genes within the genome of ChHV5 that may play a role in pathogenesis. This review discusses emerging areas where researchers might focus and theories behind the emergence of FP globally since the 1980s, which appear to be a multi-factorial interplay between the virus, the host and environmental factors influencing disease expression.
Article
Full-text available
Marine turtle fibropapillomatosis (FP) is a debilitating, infectious neoplastic disease that has reached epizootic proportions in several tropical and subtropical populations of green turtles (Chelonia mydas). FP represents an important health concern in sea turtle rehabilitation facilities. The objectives of this study were to describe the observed epidemiology, biology, and survival rates of turtles affected by FP (FP+ turtles) in a rehabilitation environment; to evaluate clinical parameters as predictors of survival in affected rehabilitating turtles; and to provide information about case progression scenarios and potential outcomes for FP+ sea turtle patients. A retrospective case series analysis was performed using the medical records of the Georgia Sea Turtle Center (GSTC), Jekyll Island, Georgia, USA, during 2009–2013. Information evaluated included signalment, morphometrics, presenting complaint, time to FP onset, tumor score (0–3), co-morbid conditions, diagnostic test results, therapeutic interventions, and case outcomes. Overall, FP was present in 27/362 (7.5%) of all sea turtles admitted to the GSTC for rehabilitation, either upon admittance or during their rehabilitation. Of these, 25 were green and 2 were Kemp’s ridley turtles. Of 10 turtles that had only plaque-like FP lesions, 60% had natural tumor regression, all were released, and they were significantly more likely to survive than those with classic FP (P ¼ 0.02 [0.27–0.75, 95% CI]). Turtles without ocular FP were eight times more likely to survive than those with ocular FP (odds ratio ¼ 8.75, P ¼ 0.032 [1.21–63.43, 95% CI]). Laser-mediated tumor removal surgery is the treatment of choice for FP+ patients at the GSTC; number of surgeries was not significantly related to case outcome.
Article
Full-text available
It has been hypothesized for decades that environmental pollutants may contribute to green sea turtle fibropapillomatosis (FP) possibly through immunosuppression leading to greater susceptibility to the herpesvirus, the putative causative agent of this tumor-forming disease. To address this question, we measured concentrations of 164 persistent organic pollutants (POPs) and halogenated phenols in 53 Hawaiian green turtle (Chelonia mydas) plasma samples archived by the Biological and Environmental Monitoring and Archival of Sea Turtle Tissues (BEMAST) project at the National Institute of Standards and Technology Marine Environmental Specimen Bank. Four groups of turtles were examined: free-ranging turtles from Kiholo Bay (0 % FP, Hawaii), Kailua Bay (low FP, 8 %, Oahu), and Kapoho Bay (moderate FP, 38 %, Hawaii) and severely tumored stranded turtles that required euthanasia (high FP, 100 %, Main Hawaiian Islands). Four classes of POPs and seven halogenated phenols were detected in at least one of the turtles, and concentrations were low (often <200 pg/g wet mass). The presence of halogenated phenols in sea turtles is a novel discovery; their concentrations were higher than most man-made POPs, suggesting that the source of most of these compounds was likely natural (produced by the algal turtle diet) rather than metabolites of man-made POPs. None of the compounds measured increased in concentration with increasing prevalence of FP across the four groups of turtles, suggesting that these 164 compounds are not likely primary triggers for the onset of FP. However, the stranded, severely tumored, emaciated turtle group (n=14) had the highest concentrations of POPs, which might suggest that mobilization of contaminants with lipids into the blood during late-stage weight loss could contribute to the progression of the disease. Taken together, these data suggest that POPs are not a major co-factor in causing the onset of FP.
Article
Full-text available
Green turtle fibropapillomatosis (GTFP), characterized by multiple benign fibroepithelial tumors on the skin and eyes, has become a growing threat to green turtle Chelonia mydas populations worldwide. The cause of GTFP is unknown, but a viral etiology is suspected. This study investigated whether GTFP could be experimentally transmitted to young captive-reared green turtles using cell-free fibropapilloma extracts prepared from free-ranging turtles with spontaneous disease. Turtles raised from eggs collected from 4 separate clutches in the wild were assigned to 4 experimental groups and 1 control group. For each experiment a crude homogenate (33% w/v) was prepared from fibropapillomas removed from a free-ranging turtle with spontaneous disease. The crude tumor homogenates were freeze-thawed and centrifuged to yield cell-free extracts that were used (both filtered and unaltered) for inoculation. Recipients were inoculated by intradermal injection or by scarification; control turtles were not treated but were housed with treated turtles. Fibropapillomas developed in all 12 turtles receiving 3 of the 4 tumor extracts, and were first detected between 15 and 43 wk post inoculation. Both filtered and unfiltered tumor extracts successfully induced tumor development. During the 10 and 12 mo monitoring periods, fibropapillomas did not develop in control turtles or in any turtles inoculated with the fourth tumor extract. Although 2 sets of experiments were performed 8 wk apart, most of the tumors in both sets became evident simultaneously after water temperatures rose. Experimental tumors were histologically indistinguishable from spontaneous fibropapillomas found in free-living turtles but lacked evidence of endoparasites. Scattered foci of epidermal degeneration were found in most sections of experimentally induced fibropapillomas and within some sections taken from donor turtles. Electron microscopy revealed virus-like particles conforming in size, morphology, and intranuclear location with herpesvirus. Negative-staining electron microscopy of transmission-positive tumor extracts failed to demonstrate intact virus particles. This study demonstrates that the etiology of GTFP is an infectious filterable subcellular agent. The herpesvirus identified in this study is 1 possible candidate for the etiology of GTFP.
Article
The current species extinction crisis is being exacerbated by an increased rate of emergence of epizootic disease. Human-induced factors including habitat degradation, loss of biodiversity, and wildlife population reductions resulting in reduced genetic variation are accelerating epizootic disease emergence. Novel, efficient and effective approaches are required to combat these epizootic events. Here, we present the case for the application of human precision medicine approaches to wildlife medicine in order to enhance species conservation efforts. We consider how the precision medicine revolution, coupled with the advances made in genomics, may provide a powerful and feasible approach to identifying and treating wildlife diseases in a targeted, effective and streamlined manner. A number of case studies of threatened species are presented which demonstrate the applicability of precision medicine to wildlife conservation, including sea turtles, amphibians and Tasmanian devils. These examples show how species conservation could be improved by using precision medicine techniques to determine novel treatments and management strategies for the specific medical conditions hampering efforts to restore population levels. Additionally, a precision medicine approach to wildlife health has in turn the potential to provide deeper insights into human health and the possibility of stemming and alleviating the impacts of zoonotic diseases. The integration of the currently emerging Precision Medicine Initiative with the concepts of EcoHealth (aiming for sustainable health of people, animals, and ecosystems through transdisciplinary action-research) and One Health (recognising the intimate connection of humans, animal, and ecosystem health and addressing a wide range of risks at the animal-human-ecosystem interface through a coordinated, collaborative, interdisciplinary approach) has great potential to deliver a deeper and broader interdisciplinary-based understanding of both wildlife and human diseases. This article is protected by copyright. All rights reserved.