Journal of Threatened Taxa |
www.threatenedtaxa.org | 26 June 2023 | 15(6): 23452–23454
ISSN 0974-7907
(Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.8336.15.6.23452-23454
#8336 | Received 22
December 2022 | Final received 30 May 2023 | Finally accepted 10 June 2023
War prompts distress symptoms in
Israeli Blind Snake
Shahar Dubiner
1 , Shai Meiri 2. & Eran Levin 3
1,2,3 School of Zoology, Faculty of
Life Sciences, Tel Aviv University, 6997801, Israel
2 The Steinhardt Museum of Natural
History, Tel Aviv University, 6997801, Israel.
1 dubiner@mail.tau.ac.il
(corresponding author), 2 uncshai@gmail.com, 3 levineran1@gmail.com
Editor: S.R. Ganesh, Kalinga Centre for Rainforest
Ecology, Shivamogga, India. Date of
publication: 26 June 2023 (online & print)
Citation: Dubiner, S., S. Meiri & E. Levin (2023). War prompts distress symptoms in
Israeli Blind Snake. Journal of Threatened Taxa 15(6): 23452–23454. https://doi.org/10.11609/jott.8336.15.6.23452-23454
Copyright: © Dubiner et al. 2023. Creative Commons Attribution 4.0
International License. JoTT allows unrestricted use, reproduction, and
distribution of this article in any medium by providing adequate credit to the
author(s) and the source of publication.
Funding: SD was supported by the Azrieli Graduate Studies Fellowship.
Competing interests: The authors declare no competing interests.
Case study
The effects of armed conflict on
wildlife are an often sidelined consequence of war. The rare studies on this
subject mainly deal with population declines caused by bombs & chemicals,
habitat alteration (both collateral & strategic), increase in exploitation
by displaced people, and decrease in enforcement (reviewed in Gaynor et al.
2016). Behavioral reactions to sudden noises of military origin were studied in
endotherms (Weisenberger et al. 1996; Krausman et al. 1998; Maier et al. 1998, Conomy et al. 1998; Goudie & Jones 2004), but all
focused on aircraft engines, not blasts, only two studies included
physiological indices of stress, such as heart rate (Weisenberger
et al. 1996) and more recently, in a lizard, blood corticosterones
(Kepas et al. 2023). Study of reptiles’ reaction to
anthropogenic noise in general is minimal (Shannon et al. 2016).
On 11 May 2021, following recent
tensions and violent events in Jerusalem, hundreds of rockets were fired into
Israel, including Tel Aviv, where our laboratory is located. Most rockets were
intercepted, some hit their targets, in both cases producing thunderous
explosions. Six hours later, another bombardment was fired. Throughout that
time, we were conducting unrelated measurements of the metabolic rate of a Syrian
Blind Snake Xerotyphlops syriacus, which resulted in a coincidental
documentation of its physiological response to the rocket barrages.
Xerotyphlops syriacus (Jan, 1864) is a nocturnal and
fossorial blind snake of the family Typhlopidae
inhabiting Lebanon, Syria, Jordan, Israel, the Palestinian Territories, and
Egypt (Bar et al. 2021). The individual we investigated was caught in Tel Aviv
University (under permit #2021/42720 from the Nature and Parks Authority). It
was kept in a terrarium with moist earth but no food to ensure a
post-absorptive state during the study. After a week it was placed in a 50 ml
metabolic chamber connected to a LICOR LI-7000 CO2/H2O analyzer (LICOR,
Lincoln, NE, USA) which was kept dark and at a stable 20⁰C. Dry air flowed
through the chamber at 50 ml/min, whereupon exiting CO2 was
measured. An empty identical chamber was used to calibrate baseline gas levels,
to which measurement automatically switched for 15 minutes at pre-programmed
intervals, without affecting the airflow or any other aspect of the chamber
housing the snake. An hour after the first measurement, a second was made using
the same protocol except for temperature, which was cooled down to 12⁰C. The
snake was rehydrated when the experiment ended, and released the following day
back where it was found. We analyzed the data with Expedata
1.9.20, using the baseline to correct drift and shift. Measurements were
conducted under ethics permit #18616 from the TAU Ethics Committee. Sunset was
at 1929 h, and the room and surrounding floor were empty of people by the
beginning of this recording. Everything was pre-programmed to run automatically
so we could see real-time results from afar.
At 2047 h, concurrently with the
explosion of the first round of rockets, we witnessed a sharp change in the gas
exchange pattern (Figure 1), from the usual smooth pattern to a series of rapid
peaks. The amplitude of the peak at the first explosion was 2.8 times the
maximum pre-explosion peak. Eleven sharp CO2 peaks in the span of
200 seconds (5.88-fold the prior frequency) instantly followed the penultimate
rocket round, which hit nearest to the laboratory. In the last round we
measured only the first seconds, because of the automatic switch to the
baseline channel, but the start of a rise in CO2 is detectable.
Between the end of the rocket barrage (2116 h) and the predetermined end of the
measurement (2300 h), O2 uptake returned to basal levels but
respiration rates stayed high. During the second measurement that night, with
colder temperature, we witnessed two respiration peaks of starting at 0251 h
and 0301 h (Figure 2). Each of these peaks, concurrent with the two new rounds
of explosions, had an amplitude three times higher and a total area tenfold
above the average for peaks in the hour before.
We interpret the change in gas
exchange patterns of X. syriacus as a response
to the explosions outside. While the physiological symptoms of fear and
distress in reptiles are difficult to confirm (Lambert et al. 2019), relaxed
breathing is usually taken as an indicator of well-being in reptiles (Warwick
et al. 2013) and other animals (Carstens & Mober
2000). Nearly every round of rockets was followed by a sharp peak in gas
exchange, too closely matched to be dismissed as a coincidence. The overall
metabolic rate was not higher after the explosions ended but breathing changed
to high frequency bouts of unusually high, interspaced peaks, which persisted
for hours. This response was exhibited by a blind snake with no external ears,
inside a sealed, padded chamber, within an incubator located in a closed,
windowless second-floor room of a concrete building. Animals in nature are much
less shielded from the sound of explosions and the ensuing destruction.
Wildlife is understandably not the focus when politics descend into violence,
but is doubtlessly also grievously affected.
For
figures - - click here for full PDF
References
Bar, A., G. Haimovitch & S. Meiri (2021). Field Guide to Reptiles and
Amphibians of Israel. Edition Chimaira, 512 pp.
Carstens, E.
& G.P. Moberg (2000). Recognizing pain and distress in laboratory animals. ILAR Journal
41(2): 62–71.
Conomy, J.T., J.A. Dubovsky,
J.A. Collazo & W.J. Fleming (1998). Do black ducks and wood ducks
habituate to aircraft disturbance? The Journal of Wildlife Management
62: 1135–1142.
Goudie, R.I.
& I.L. Jones (2004). Dose-response relationships of harlequin duck behaviour
to noise from low-level military jet over-flights in central Labrador. Environmental
Conservation 31(4): 289–298.
Kepas, M.E., L.O. Sermersheim,
S.B. Hudson, A.J.J. Lehmicke, S.S. French & L.M. Aubry (2023). Behavior, stress and metabolism of a parthenogenic
lizard in response to flyover noise. Frontiers in Amphibian and Reptile
Science 1(1129253): 1–13. https://doi.org/10.3389/famrs.2023.1129253
Krausman, P.R. (1998). The effects of aircraft noise on
pronghorn and other species: an annotated bibliography (No. 14). US Geological
Survey, Cooperative Park Studies Unit, School of Renewable Natural Resources,
University of Arizona.
Lambert, H.,
G. Carder & N. D’Cruze (2019). Given the Cold Shoulder: A
review of the scientific literature for evidence of reptile sentience. Animals
9(10): 821.
Maier, J.A.,
S.M. Murphy, R.G. White & M.D. Smith (1998). Responses of caribou to
overflights by low-altitude jet aircraft. The Journal of Wildlife Management
62(2): 752–766. https://doi.org/10.2307/3802352
Shannon, G.,
M.F. McKenna, L.M. Angeloni, K.R. Crooks, K.M.
Fristrup, E. Brown & G. Wittemyer (2016). A synthesis of two decades of
research documenting the effects of noise on wildlife. Biological Reviews
91(4): 982–1005.
Warwick, C.,
P. Arena, S. Lindley, M. Jessop & C. Steedman (2013). Assessing reptile welfare using behavioural criteria. In Practice 35(3): 123–131.
Weisenberger, M.E., P.R. Krausman,
M.C. Wallace, D.W. De Young & O.E. Maughan (1996). Effects of simulated jet
aircraft noise on heart rate and behavior of desert ungulates. The Journal
of Wildlife Management 60(1): 52–61. https://doi.org/10.2307/3802039