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Notes on the prevalence of Amphisbaena bassleri L. 1758 (Squamata, Amphisbaenidae) in a study of road ecology in the western Amazon, near Tena (Ecuador)

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The family Amphisbaenidae includes some of the least
studied and understood species of Squamata, mainly
due to their fossorial behaviour. In turn, this implies that
we have limited knowledge of the conservation status
of these species, and we cannot predict the responses of
these elusive animals to increasingly more common and
severe human-induced disturbances and habitat changes
(Vitt et al. 1998; Díaz et al. 2000, Kuhnz et al. 2005;
Huey et al. 2009; Hamer and McDonnel 2010).
Amphisbaena bassleri Linneaus, 1758 is distributed
across most of tropical South America (Vanzolini
2002; Lemos and Facure 2007; Nogueira-Costa et al.
2013) and is largely an under-studied species. There
are notes on its habitat preferences (e.g., Vanzolini
2002; Ribeiro et al. 2012), descriptions of its fossorial
behaviour (Vanzolini 2002; Lemos and Facure 2007),
and discussions of its taxonomy—with Vanzolini
(2002) recognizing five subspecies and Gans (2005)
considering these as separate species. Following Gans
2005, we will use the name A. bassleri, recognizing that
the synonym A. fuliginosa might be in use for the same
species in other regions of South America (Vanzolini
(2002).
Like most amphisbaenids, A. bassleri lives a
predominantly fossorial life, surfacing only occasionally
(Vanzolini 1951, 2002; Lemos and Facure, 2007). Lemos
and Facure (2007) hypothesized that fossoriality might
allow this species to occur in anthropogenic habitats,
as they would not be hindered by changes in above-
ground natural vegetation. We herein provide data on
the observations of 13 specimens of A. bassleri in an
anthropogenic habitat in Ecuador. Our observations
suggest that this species might be rather abundant, as
previously noted by Vanzolini (1951).
Our observations stem from two different localities.
First, from November 2014 until January 2017, we
registered 10 dead specimens of A. bassleri (Fig.1,
Table 1) on circa 750 m of road between -0.9572°S -
77.8606°W and -0.9506°S -77.8620°W, 585 m.a.s.l.,
near Universidad Regional Amazónica IKIAM in the
Amazon region (Napo Province) of Ecuador (three
of which were included in collection of the Gustavo
Orcés Museum of Natural History at the Escuela
Politecnica Nacional (MEPN) with vouchers MEPN-
18845-18847). We found these dead specimens in
the months of December and June-August, two of the
driest periods of the year in the area (averaging 200-300
mm precipitation / month; unpublished data for 2015-
2016 from Universidad Regional Amazónica IKIAM’s
meteorological station). Second, the day following a
major flooding (~2 m above ground at its peak level for
nearly 30 hours) on March 13, 2016, in an urban zone
of Tena, we found three dead A. bassleri, all within 2 m
from each other in a ~200 m2 private garden (-0.9911°S
-77.8101°W, 510 m a.s.l.). March usually is one of the
wettest months of the year in this region (>400 mm
of precipitation), but these extreme floods occur very
infrequently in the area (the last record dates back to
April of 2010). Although Amphisbaena sp. are usually
described as capable swimmers (e.g., Maschio et al.
2009), the three A. bassleri found in Tena seemed to
have drowned due to the flooding.
A. bassleri is not usually considered a rare or range-
restricted species (Carvajal-Campos and Rodríguez-
Guerra 2003), and we show that this species might
be even present in heterogeneous, human-altered,
landscapes. Mostly unnoticed due to their fossorial
habits, these animals might surface as a result of
floods (see similar observations by Teixeira Jr. et al.
2014). These notes on the ecology and behaviour of A.
Herpetology Notes, volume 10: 497-498 (2017) (published online on 14 September 2017)
Notes on the prevalence of Amphisbaena bassleri L. 1758
(Squamata, Amphisbaenidae) in a study of road ecology in the
western Amazon, near Tena (Ecuador)
Yntze van der Hoek1,* and Pablo Jarrín-V1
1 Universidad Regional Amazónica IKIAM, Vía Muyuna,
Kilómetro 7, Tena, Ecuador.
* Corresponding author email: yntze.vanderhoek@ikiam.edu.ec
Yntze van der Hoek & Pablo Jarrín-V
498
bassleri contribute to our understanding of the potential
impacts of road infrastructure expansion, and increased
frequency of flooding events, in the eastern Amazon
region of Ecuador.
Acknowledgments. We thank Dr. Ana Almendáriz, curator of
MEPN, for her help with the taxonomic identification of our
specimen. We would also like to thank all our students for their
collaboration in the roadkill project that generated some of the
A. bassleri records used in this study. In addition, thanks to Ed
Myers and two anonymous reviewers for providing comments
that enhanced the quality of this note.
References
Carvajal-Campos, A., Rodríguez-Guerra, A. (2013): Amphisbaena
bassleri. ReptiliaWebEcuador, Version 2013.0. Available at
http://zoologia.puce.edu.ec/vertebrados/reptiles/FichaEspecie.
aspx?Id=3047. Accessed 6 January 2017.
Díaz, J.A., Carbonell, R., Virgós, E., Santos, T., Tellería, J.L. (2000):
Effects of forest fragmentation on the distribution of the lizard
Psammodromus algirus. Animal Conservation 3: 235–240.
Gans, C. (2005) Checklist and bibliography of the Amphisbaenia of
the world. Bulletin of the American Museum of Natural History:
1–130.
Hamer, A.J., McDonnell, M.J. (2010): The response of herpetofauna
to urbanization: Inferring patterns of persistence from wildlife
databases. Austral Ecology 35: 568–580.
Huey, R.B., Deutsch, C.A., Tewksbury, J.J., Vitt, L.J., Hertz, P.E.,
Pérez, H.J.Á., Garland, T. (2009): Why tropical forest lizards
are vulnerable to climate warming. Proceedings of the Royal
Society B: Biological Sciences 276: 1939–1948.
Kuhnz, L.A., Burton, R.K., Slattery, P.N., Oakden, J.M. (2005):
Microhabitats and population densities of California legless
lizards, with comments on effectiveness of various techniques for
estimating numbers of fossorial reptiles. Journal of herpetology
39: 395–402.
Lemos, F.G., Facure, K.G. (2007): New record of Amphisbaena
fuliginosa (Squamata, Amphisbaenidae) for the Cerrado Biome,
in an area of extensive cattle ranching. Biota Neotropica 7:
https://dx.doi.org/10.1590/S1676-06032007000100031.
Maschio, G.F., da C. Prudente, A.L., Mott, T. (2009): Water
dispersal of Amphisbaena alba and Amphisbaena amazonica
(Squamata: Amphisbaenia: Amphisbaenidae) in Brazilian
Amazonia. Zoologia 26: 567-570.
Ribeiro, S.C., Roberto, I.J., Sales, D.L., Ávila, R.W., de Oliveira
Almeida, W. (2012): Amphibians and reptiles from the Araripe
bioregion, northeastern Brazil. Salamandra 48: 133–146.
Teixeira Jr, M., Vechio, F.D., Neto, A. M., Rodrigues, M. T. (2014):
A New Two-Pored Amphisbaena Linnaeus, 1758, from Western
Amazonia, Brazil (Amphisbaenia: Reptilia). South American
Journal of Herpetology 9: 62–74.
Vanzolini, P.E. (1951): Contributions to the knowledge of the
Brasilian lizards of the family Amphisbaenidae Gray, 1825.
6. On the geographical distribution and differentiation of
Amphisbaena fuliginosa Linné. Bulletin of the Museum of
Comparative Zoology 106:1–67.
Vanzolini, P.E. (2002): A second note on the geographical
differentiation of Amphisbaena fuliginosa L., 1758 (Squamata,
Amphisbaenidae), with a consideration of the forest refuge
model of speciation. Anais da Academia Brasileira de Ci�ncias
74: 609–648.
Vitt L.J., Avila-Pires, T., Caldwell, J.P., Oliveira, V.R. (1998): The
impact of individual tree harvesting on thermal environments
of lizards in Amazonian rain forest. Conservation Biology 12:
654–664.
Figure 1. Ventral (A) and dorsal (B) view of a ca. 31 cm long specimen of Amphisbaena bassleri L. 1758 (Squamata,
Amphisbaenidae) found dead on a road near Tena (Ecuador).
Accepted by Ariel Rodríguez
... usually expected, and can persist at least temporarily in areas with high levels of habitat alteration(van der Hoek & Jarrín-V, 2017;Maschio, Santos-Costa, & Prudente, 2016). Studies of time lags in population responses will be key to explain the true impact of human disturbances on this species in the long term.Fossorial species are likely to be disproportionally affected by road barriers(Sosa & Schalk, 2016), and we indeed found that the fossorial amphisbaenian Amphisbaena bassleri and the semi fossorial snake species Atractus collaris, Atractus elaps, and Atractus major represented 70% of all reptiles found during this study. ...
Presentation
We sampled and identified vertebrate tropical fauna threatened by road kills in Tena, Napo, Ecuador, Western Amazon. We mostly found herps and other small vertebrates during a 5 month initial study. We presented our work in the National Biology Conference in Ecuador. Presentamos nuestro trabajo en las Jornadas Nacionales de Biología 2015.
... usually expected, and can persist at least temporarily in areas with high levels of habitat alteration(van der Hoek & Jarrín-V, 2017;Maschio, Santos-Costa, & Prudente, 2016). Studies of time lags in population responses will be key to explain the true impact of human disturbances on this species in the long term.Fossorial species are likely to be disproportionally affected by road barriers(Sosa & Schalk, 2016), and we indeed found that the fossorial amphisbaenian Amphisbaena bassleri and the semi fossorial snake species Atractus collaris, Atractus elaps, and Atractus major represented 70% of all reptiles found during this study. ...
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