
New insights on Chromatopelma
41
estado Falcón, between the towns of Acurigua and El Paso
(Bermúdez 2022), which lies within the Lara-Falcón dry
forests ecoregion (Fig. 4). is record is not very far away
from the aforementioned record from municipio Miran-
da, estado Falcón (Figs. 2-4), but it does represent a very
important record insofar as it demonstrates that C. cya-
neopubescens occurs at least in part in the northern part of
the Lara-Falcón dry forest. us, C. cyaneopubescens seems
not to be endemic to the Paraguaná xeric scrub ecoregion.
Nonetheless, both ecoregions are characterised by a dry
climate, indicating this is an important aspect of the habi-
tat requirements of this species.
Two records of adult males from the Península de Para-
guaná also provide the rst data for the dates of the breed-
ing season of C. cyaneopubescens. One male was observed
on 15th April 2021(Nunes 2021). e later record (see
Fig. 1A) was made many years prior on 17th June 2008
(Boyce 2008). When considered together, this indicates
that the maturation of males occurs during April-June and
that this is the main part of the breeding season for C. cya-
neopubescens in the wild. Males might mature earlier or later
than this, and this should be investigated by future workers
(see below). Nonetheless, before the present study, nothing
was known of the dates at which adult males matured and
wandered in search of females in this taxon.
Interestingly, one observation assessed herein (Fig. 1C,
see also Table 1) is of a specimen found on a wooden chair4
in a house within the Natural Monument Montecano, San
José de Cocodite, also observed later on the same day by
the author RG-Z. is particular spider is well known to
be spotted in the house in question and is oen found on
the chair it was photographed on (Yenifer Revilla pers.
comm.), hence the silk seen on the chair. It is thus evident
this species can in part live in areas of human habitation if
not directly disturbed (i.e., here in a house within a nation-
al park, patrolled by park rangers) but this certainly does
not mean that the species as a whole can therefore adapt to
further human encroachment on its habitat (see below).
DISCUSSION
Despite being a small dataset of just 11 records (Ta-
ble 1), the iNaturalist data allowed us to advance our
knowledge of the distribution and habitat association of
C. cyaneopubescens. We can demonstrate that C. cyaneo-
pubescens is predominately distributed in the Paraguaná
xeric scrub ecoregion, as expected, but that it is also pres-
ent in the northern reaches of the Lara-Falcón dry forests
ecoregion. e record from west of Durigua, close to the
outskirts of Barquisimeto represents a range extension of
more than 200 kilometres south into mainland Venezuela.
Finally, the documentation obtained of two males provides
basic information on the months of the breeding season.
Notwithstanding this advance in information on C.
cyaneopubescens, knowledge gaps still exist. We can build
here upon the most precise former assessment of distri-
bution (Colmenares 2015). It is important to further
clarify how widely distributed this species is in the Lara-
Falcón dry forests ecoregion and whether it occurs in
other ecoregions of northwestern Venezuela. We do not
provide detailed ecological observations of its life history
(e.g., burrow construction, abundance, diet), as no direct
eldwork was commenced for this purpose for the pres-
ent work. Nonetheless, we direct the reader to the confer-
ence abstract of Marte (2012) who undertook such stud-
ies at the Monumento Natural Cerro Santa Ana, where
this species is known to occur. As of 2023, we are not
aware that this data was formally published in full yet. We
hope that it will be and that it can be used in conjunction
with the present work to build a fuller picture of the life
history of C. cyaneopubescens and better inform its con-
servation needs.
Some of the previously mentioned records are in Natu-
ral Monuments Montecano (one, Fig. 5) and Cerro Santa
Ana (two, Fig. 6), in the Península de Paraguaná, which
are National Protected Areas. However the rest of the
observations (ve elsewhere within the Península de Para-
guaná, three outside of it) in areas that are not protected
by national law. We suggest that further legal protections
for this species in those other areas be considered, to pro-
mote the protection of this species in its natural habitat.
e fact that 9 out of 11 records are from the Península
de Paraguaná reinforces that this is probably the most im-
portant stronghold of this species, and it thus represents
an important agship species for the region and Venezuela
as a whole.
An analysis of the extent of urbanisation (Fig. 7, 8, 10)
or lack thereof (Fig. 9) and summarising the total number
of settlements of all sizes (Figs. 12-15) show that the habi-
tat of at least one locality is under threat. Namely, habitat
in the neighbourhood ‘Sur La Paz’ in municipio Miranda,
estado Falcón, close to the boundaries of the Parque Na-
cional Médanos de Coro. Furthermore, increased expan-
sion of other areas (i.e., Figs. 11-14) could threaten other
local populations more broadly in Venezuela. is requires
further investigation and long-term monitoring. Given
4 It is clear that this species relies on wood for making retreats in the wild (see above), so this could be a factor in why a specimen indoors placed web-
bing on a wooden chair.