This note provides two pieces of novel information. Before our observations, Dromiciops gliroides had never been recorded in pine plantations. These observations were conducted in pine stands with dense (>20%) understory. Our observations also expanded the known distribution of the species 35 Km to the North (previous limit was Los Ruiles National Reserve 35°50’S 72°30’W [17]). The latter agrees with the predictions by Martin [20] whose models give a 1–10% probability of presence of monito del monte between 34–36°S in the Coastal Range of Central Chile.
Although monitos del monte were recorded unfrequently in our studies (0.09% of all captured small mammals), our results show that D. gliroides has been able to persist in an extremely altered environment. Also, the fact that we set up the traps on the ground and used a bait that is not particularly attractive to the species [11], suggests that we might have underestimated the abundance of the species.
The low abundance of D. gliroides in pine plantations is likely due to their simple vertical structure, which reduces their ability to climb and move through the foliage. Althouth some pine stands have well developed understories, bamboo (Chusquea spp.) thickets are uncommon in these artificial forests (average (SE), 267.3 (123,6) m3 foliage/ha, Uribe, unpublished data). This might favour the limited use of pine stands by monitos del monte, as these plants have been considered a key component of the species’ breeding habitat, because of their importance for the construction of nests [1, 11]. Other key elements as ferns and vines are also uncommon in pine plantations. Fonturbel et al. [9] recorded D. gliroides at similar rates in native forests and Eucalyptus plantations, but in this unusual case, due to a lack of management, this stand had a rich native understory.
The native forest fragments studied by us had a much higher abundance of bamboos (average (SE), 1312.8 (540.6) m3 foliage/ha, Uribe, unpublished data) than pine stands, and, coincidentally, the capture rate of D. gliroides was an order of magnitude higher than that of plantations. However, this rate showed a significant variation among sites and campaigns, with 80% of the individuals captured in just one session in a plot of approximately 2 ha. We cannot begin to explain this aggregation of individuals by any evident factor associated to the habitat characteristics. In fact, this particular fragment had a below-average Chusquea cover (936 m3 foliage/ha). Also, the land use composition of San Pedro-Las Cañas was similar to the rest of the landscapes (19% native forest and 70% pine plantation, vs an average (SE) of 23.5 (3.6) and 66.4 (4.9), respectively, Table 1). However, there is one anecdotal observation about this record that is worth mentioning. During the days in which we captured these animals, the neighboring plantations were being cut. We can only speculate on a transient aggregation of monitos in the native forest, while escaping from the timbering operations taking place in the nearby plantations. A study conducted by us in the area [21] showed no such effect for the rodent Abrothrix longipillis, as most individuals died crushed by the machinery because of their tendency to hide under the forest litter when in danger. However, a more mobile animal such as D. gliroides, that usually climbs trees for protection (authors’ pers. obs), will likely try to abandon the tree harvesting area. Testing this hypothesis would be very important to understand the mechanisms affecting the long term persistence of this species in pine plantation landscapes. The available information is not sufficient to determine whether the presence of D. gliroides in landscapes dominated by pine plantations is a sign of some level of adaptation to this novel ecosystem (with its inherent disturbance regime [22]) or if it is only due to the “extinction debt” (i.e. populations are slowly declining towards extinction, [23]). However, the history of this region tends to favor the first explanation. For example, most plantations in this region of Chile are in their second or third 20-year rotation, which means that several generations of monitos have been born in these landscapes since the major transformations took place. Also, in the 1950’s approximately a 45% of the landscape in the coastal range of South Central Chile was already transformed into agriculture [24, 25], whereas the current proportion of “open” land uses in this region is approximately 21% [26]. This means that the present landscape might be more favorable to forest specialists such as D. gliroides, who might avoid moving through non forested habitats [10].
In any of the latter cases, management of pine plantations has the potential to influence a significant proportion of D. gliroides populations. Two main issues that should be addressed are the potential transformation of pine plantations into breeding habitat for the species, via the improvement of the understory [27], and the enhancement of the role of pine plantations as connectors for populations living in native forest fragments. Specific management recommendations will likely arise after more detailed information on the species’ ecology is obtained.
Recently, D’Elia et al. [28] proposed a division of D. gliroides into three different species. Should this new classification be adopted, our observations would then correspond to the northern species, D. bozinovici. The fact that a significant portion of this taxon’s distribution range is dominated by pine plantations would make our observations even more relevant.
