other members of the Order Umbraculida,
Umbraculum spp. are specialist predators on a
wide array of sponges (Willam 1984; Avila et al.
2018). Heterobranchs are well known for seques-
tering, transferring and even modifying metabo-
lites from their diet for defensive purposes
(Faulkner and Ghiselin 1983; Cimino et al. 2001).
These compounds may be released via mucus or
concentrated in the mantle dermal formations or
other glandular structures (Wägele et al. 2006a).
The only metabolites from U. umbraculum
known to date are two diacylglycerols and a fatty
acid ester probably produced by the sponge Geo-
dia cydonium in the Mediterranean where the
mollusk was collected (Cimino et al. 1988, 1989).
Until now, little is known about the ecology of
heterobranchs such as U. umbraculum, even
though its presence is recognized in the
Caribbean region. Information about habitat pref-
erences, food and reproduction patterns is scarce.
This note describes a recent finding of this mol-
lusk on a previously unreported habitat, which
may provide shelter during various stages of its
life cycle.
Habitat characteristics
A solitary specimen of the heterobranch mol-
lusk Umbraculum umbraculum was found on
March 1, 2018 at a Thalassia testudinum bed at
Taganga bay, a buffer area of the Tayrona Nation-
al Park, Colombian Caribbean (11° 16′ 16.1″ N-
74° 11′ 54.1″ W; Figure 1 A) at 3 m depth. The
area is affected by local coastal upwelling from
December to March. In these months, seawater
temperature may drop to 20-25 °C (Diaz-Pulido
and Garzon-Ferreira 2002; Bayraktarov et al.
2012). The seagrass bed where we found the
specimen was located on a muddy sand substrate
at the leeward side of the bay (Figure 1 B). We
carried out some preliminary evaluations to
assess the conservation state of this seagrass bed
in particular. In an area of 100 m2, we measured
parameters such as shoot density, growth rate and
overall biomass. We determined that this bed has
a rather low density (88 shoots m-2, each bearing
two to five short leaf blades, 15 cm long, growing
from a basal meristem). The calculated growth
rate was of 0.8 cm day-1, yielding an overall bio-
mass of 5.04 g m-2 and reaching a productivity of
0.15 g m2 day-1. These biological features, togeth-
er with rather intense tourist activity in the area,
and ecosystem risk analysis (Bland et al. 2016)
allow us to consider that this seagrass bed is in a
poor conservation state, and possibly in Critical
Risk of collapse according to IUCN categories.
Specific habitat preferences for U. umbracu-
lum have not been well documented to date. The
species has been only reported at shallow sandy
bottoms in Greece (Wägele et al. 2006b; Sankar
et al. 2011). In Colombia, a specimen (Catalog
number INV MOL-1595; MAKURIWA-Marine
Natural History Museum of INVEMAR;
http://siam.invemar.org.co/buscador) was collect-
ed on soft bottoms (70 m depth) at Cabo de la
Vela (Marcus and Marcus 1967) in the upwelling
area of the Guajira (12° 12′ 15.7″ N-72° 10′ 59.4″
W) and also seen at Tayrona National Park (Ardi-
la et al. 2007).
To the best of our knowledge, there are no pre-
vious reports of U. umbraculum thriving in Tha-
lassia testudinum beds. As with other hetero-
branchs, U. umbraculum might gain protection
from predation among the seagrass blades and
may also find suitable food sources, once, in our
field evaluations, we found several specimens of
Agelas spp. and other sponges. Additionally, the
animal observed was in reproductive mode since
upon collection it released copious amounts of
sperm (Figure 1 C and 1 D), which suggest that
U. umbraculum uses the upwelling season (Janu-
ary to March) to migrate to shallow water and
reproduce as others mollusks do at Taganga Bay
such as Octopus hummelincki (Adam, 1936) and
Aplysia dactylomela (Rang, 1828) (Jürgen Guer-
rero-Kommritz, Pers. Observ.).
Habitat and water quality in Taganga bay have
diminished over the last four decades. The bay is
130 MARINE AND FISHERY SCIENCES 33 (1): 129-133 (2020)