PROGRAMA FONDECYT

INFORME FINAL

ETAPA 2013

COMISIÓN NACIONAL DE INVESTIGACION CIENTÍFICA Y TECNOLÓGICA

VERSION OFICIAL Nº 2

FECHA: 05/11/2014

Nº PROYECTO : 11110027 DURACIÓN : 3 años AÑO ETAPA : 2013 TÍTULO PROYECTO : LOCAL AND REGIONAL FACTORS AFFECTING THE FUNCTIONAL RICHNESS OF TOP-PREDATOR ASSEMBLAGES IN TEMPERATE FORESTS OF SOUTHERN SOUTH AMERICA.

DISCIPLINA PRINCIPAL : ECOLOGIA Y CIENCIAS AMBIENTALES GRUPO DE ESTUDIO : BIOLOGIA 1 INVESTIGADOR(A) RESPONSABLE : ARIEL ALEJANDRO FARIAS DIRECCIÓN : COMUNA : CIUDAD : Santiago REGIÓN : METROPOLITANA

FONDO NACIONAL DE DESARROLLO CIENTIFICO Y TECNOLOGICO (FONDECYT) Moneda 1375, Santiago de - casilla 297-V, Santiago 21 Telefono: 2435 4350 FAX 2365 4435 Email: [email protected] INFORME FINAL PROYECTO FONDECYT INICIACION

OBJETIVOS

Cumplimiento de los Objetivos planteados en la etapa final, o pendientes de cumplir. Recuerde que en esta sección debe referirse a objetivos desarrollados, NO listar actividades desarrolladas. Nº OBJETIVOS CUMPLIMIENTO FUNDAMENTO 1 To assess the probability of occurrence (phi) of TOTAL The three sampling seasons were successfully top-predator species (Mammalia: Carnivora, accomplished, surveying raptors and carnivores at Aves: Falconiformes and Strigiformes) at 23 localities (40 sampling areas, 67% above the sampling stations at insular and continental number originally planned). Then, the probability settings, in relation to land conversion. of occurrence (phi) was assessed for the 27 species recorded during the study. Occupancy estimation models were used for species with 7 or more positive records (i.e. recorded in 7 sampling points or more). Otherwise, logistic regression or naive estimations of phi (cf. MacKenzie et al. 2006) were used. 2 To quantify the functional similarity among TOTAL Functional similarity among species was assessed predator species in the regional pool and, to during the second year of the present study using assess the form of the corresponding SFR, and to a functional trait matrix built between 2012 and estimate the expected FR at surveyed sampling 2013. During the last year, field work was stations according to phi; and functional completed, and information about the probability similarity of predators. of occurrence of species at each sampling station was obtained. Combining this information with functional similarity, the expected values of functional richness for each sampling point was estimated by means of bootstrapping. 3 To test differences between the functional TOTAL Differences between the functional richness (FR) richness of local top-predator assemblages in of local top-predators assemblages in Chiloé and Chiloe and those in the continent. the mainland were assessed. As expected, FR was lower in the island, but differences, though statistically significant, were subtle. 4 To test whether the local top-predator TOTAL Contrasting the observed values of FR for Chiloé assemblages in Chiloe and in the continent show and the mainland against those predicted by the lower FR than expected for their expected species 95% CI for the species richness - functional richness and the SFR. richness association for the regional pool (SFR) shows no departure from random extinctions patterns. Thus, ecological filters seems no to be strongly affecting the functional richness of local top-predator assemblages. 5 To test the interaction between response of local TOTAL Expected FR values for local top-predator top-predator FR to land conversion and insularity. assemblages were regressed against principal components describing major changes in land cover in association to human disturbance and region (i.e. insularity). For two out of three principal components, interaction between the such component and region did not improved model performance; i.e. the hypothesis of more pronounced responses for insular assemblages than for the continental ones was not supported by these analyses. 6 To test the interaction between response of local TOTAL This goal was advanced during year 2012 using top-predator FR to species introduction, local S complete regional predator faunas and known and insularity. distribution of top-predator species, and concluded in 2014 after finishing field-data collection.

Otro(s) aspecto(s) que Ud. considere importante(s) en la evaluación del cumplimiento de objetivos planteados en la propuesta original o en las modificaciones autorizadas por los Consejos. RESULTS OBTAINED: For each specific goal, describe or summarize the results obtained. Relate each one to work already published and/or manuscripts submitted. In the Annex section include additional information deemed pertinent and relevant to the evaluation process. The maximum length for this section is 5 pages. (Arial or Verdana, font size 10).

Objective 1: To assess the probability of occurrence (Ψ) of top-predator species (Mammalia: Carnivora, Aves: Falconiformes and Strigiformes) at sampling stations at insular and continental settings, in relation to land conversion. The completion of this objective comprises: (a) surveying carnivore and raptor presence in areas differing in the extent of land conversion and human intervention, (b) collecting landscape-scale environmental information for the surveyed areas, and (c) assessing the probability of occurrence of each species in relation to land conversion and landscape structure. The first part involved collecting information during field trips carried out between November 2011 and May 2014, at sampling areas representative of the variety of habitat types present at different localities. Within a given locality, sampling areas are separated by at least 1 km, and those from different localities have a minimum separation of 10 km. Overall, ca. 40 areas were surveyed for the occurrence of mammalian carnivores (Carnivora) and/or birds of prey (Falconiformes, Strigiformes). Between December 2011 and May 2014, camera traps were used to survey carnivore presence at 192 sample points distributed in 43 areas in 23 different localities in southern Coastal Ranges (Los Lagos and Los Rios Regions), Chiloé Island and Palena . In addition, information from a locality surveyed during a previous project was included in the database, totalizing 24 localities, 46 areas and 205 sample points. Eleven carnivore species were recorded (Table 1). With the only exception of the southern river otter (Lontra provocax), all species rendered enough information (i.e. nine or more sample points with positive records) to model their probability of occurrence using occupancy estimation models (OEM), thus allowing accounting for imperfect detection (MacKenzie et al. 2006). Camera traps did not record the southern river otter, but signs of presence (e.g. sprints, food remains) and reports by local people were common. Further, Sepulveda et al. (2007, Biological Conservation 140:329–338) reported a mean density of 0.25 indiv. km-1 (or 1 individual per 4000 m of river) for this mustelid. Thus we arbitrary assigned to each sample point a probability of occurrence of L. provocax equal to the total length of river and streams within the corresponding 200 m buffer divided by 4000 m. Noteworthy, the kodkod (Leopardus guigna) and the domestic dogs (Canis lupus familiaris) were the commonest carnivore species throughout our study area, followed by the chilla and Darwin’s foxes (Lycalopex griseus and L. fulvipes, respectively). A by-product of the present study was the discovery of a new population of the later species in the Coastal Ranges of Valdivia (Alerce Costero National Park, and Oncol Park), and more recently a new locality near the mouth of the Maullín river (Pacific coast, close to the city of , ). These records coincide with similar findings in the Valdivian Coastal Reserve by S. Silva-Rodriguez and M. Sepúlveda, and were jointly published in an article in Revista Chilena de Historia Natural, and presented at the 11º Mammalogical Congress held in Belfast (UK). Together, these new localities greatly expand the known distribution of this canid with consequences for its conservation status. Point counts were performed to survey birds of prey. Diurnal raptors were surveyed at 105 sampling points distributed over 24 areas and 14 localities, while the ocurrence of nocturnal raptors was assessed at 49 sample points in 19 areas and 10 localities. In the latter case, additional information from a previous project was added to the database, totalizing 66 sampling points and 23 areas. In summary, the caracaras Milvago chimango and Caracara plancus represented the commonest diurnal birds of prey, while the rufous legged owl (Strix rufipes) and the southern pigmy owl (Glaucidium nanum) were the two major nocturnal/crepuscular raptors. Only four diurnal raptors (M. chimango, C. plancus, Buteo albigula, and Falco sparverius) and two nocturnal raptors (G. nanum and S. rufipes) rendered enough information for occupancy estimation models. Several species were rarely recorded during the point-count sessions, but nonetheless detected when visiting each area. Thus, a number of casual observations were performed within the 200 m buffer areas around sampling points (see below), and this allowed estimating the probability of occurrence of these species by means of generalized linear models (family binomial, logit link function, i.e. logistic regression). Note that, given uncontrolled imperfect detection, the probabilities obtained in these cases are expected to underestimate actual occupancy. Finally, some species (i.e. Accipiter bicolor [= chilensis], F. femoralis, F. peregrinus and Geranoaetus melanoleucus) were too rarely recorded that and only naive estimations of their occupancy (i.e. number of positive sampling points divided by the total number of sample points, cf. MacKenzie et al. 2006) could have been obtained. Given that A. bicolor is known to be a forest specialist, its “naive” occupancy was estimated only considering areas with well-conserved native forests. Environmental information was obtained from digital cartography and pre-processed satellite images for a buffer of 200 m around each sampling point. In particular, digital maps of the last version of the Native Forest Inventory (http://www.conaf.cl) for Los Lagos and Los Ríos Regions were used to obtain information about the percentage of buffer`s area covered by forests, shrubs, grasslands and wetlands, as well as the relative representation of the different forest types, and the height of arboreal vegetation (as a proxy for maturity). An index of successional stage was also obtained considering the type of vegetation (i.e. from open/bare areas and grassland areas, to shrubs, to second-growth forests, and to old-growth forests), assigning scores ranging from 1 (disturbed/early succesional vegetation) to 3 (mature forests). In addition, the percent tree (i.e. > 5 m high woody vegetation) cover, the time since the last deforestation event, and the percent forest cover change was obtained from high-resolution consensus raster maps from the Global Forest Change 2000-2012 program, University of Maryland (http://earthenginepartners.appspot.com; Hansen et al. 2013, Science 342: 850–53). To assess the level of human intervention, the longitude of roads and vehicle paths within each 200-m buffer was obtained from MOP (i.e. Ministerio de Obras Públicas, Gobierno de CHile) digital maps and digitizing GoogleEarth images. Mean elevation in each buffer area was estimated using the 90 m Digital Elevation Model EartEnv-DEM90 (http://www.earthenv.org; Robinson et al. 2014, ISPRS J Photogram Remote Sens 87:57-67). Furthermore, a digital raster map of the DMSP-OLS intensity of stable night-lights (http://ngdc.noaa.gov) was used as a proxy of human density in rural areas. The longitude of rivers and streams was also quantified within each 200-m buffer. Principal component analyses (PCA) were performed on these environmental variables in order to reduce model complexity. First, a PCA was applied on the proportional representation of major habitat types (i.e. forest, shrubs, forests, wetlands, etc.), and another on the relative representation of major forest types dominated by different woody species, thus obtaining a reduced number of orthogonal environmental axes from otherwise redundant variables. Finally, these PCA axes and the remaining variables were summarized by a third PCA, whose major axes represent the main orthogonal gradients of change in land cover, and were used to assess the effects of land conversion on the probability of occurrence (i.e. occupancy: Ψ) of predator species. Figure 2 shows the contribution of different variables to the first two principal components. Overall, the first axis represents a gradient from altered habitats to mature forests, while the second discriminate between intervened habitats dominated by shrubs and those dominated by grasslands and with higher human intervention and density. Figure 1: First two axes of the final principal components analysis performed on environmental variables. Variables are: PTC: percent tree cover, PTCnc: net change in forest cover between 2000 and 20012 (negative values means deforestation while positive values represents recuperation of tree cover), SUCm: successional state index, ELEV: mean elevation, HGHT: vegetation height, CANE: percent cover of “canelo” (Drymis winteri) second-growth forests, HAB1: first axis of PCA performed on relative cover of main habitat types (positively correlate with the relative cover of forests), HAB2 second axis of the same PCA (positively associated with shrub cover y negatively with grassland cover), NLGHT: intensity of stable night light (a proxy of human density), ROAD: total length of road and vehicle paths.

Finally, in order to account for spatial autocorrelation between neighbouring sample points, an auto-logistic (ai) term was included as a predictor variable: ai = Σ yj exp(-dij) , where yj represents the record history of the neighbour sample point j (i.e. 1 if the species of interest was recorded at least once, 0 otherwise) and dij is the distance between the focal point i and the neighbour point j (in km). Table 1 summarizes the best models describing the association between occupancy of predator species and landscape variable and land conversion. Note that in the present study the suggestion of MacKenzie et al. (2006) was followed, actually interpreting occupancy estimation at the selected spatial resolution as “habitat use”. True occupancy should be assessed with a spatial resolution lower than that of individual’s home range.

Table 1. Best models for the occurrence probability (i.e. occupancy: Ψ) of top-predators. The incidence of each species is shown as the proportion of sample points with one or more positive records; * species absent from Chiloé Island, their incidence was calculated only from sample points in the continent; ** species absent from Palena Province, points in this province were not considered in the calculation of incidence. VHght: vegetation height, LRoad: total road/path longitude (proxy of human intervention), ACor: autocorrelation term, PC1 and PC2: first and second principal components of the PCA, Lure: time since camera trap baiting (in days), %Grsl, %FRST and % SHRB: percent area covered by grasslands, forests and shrubs, respectively, Succ: succesional state, %TCov: percent tree cover, Vivib: visibility (position of the sample point), TFor1: first axis for the PCA applied on the relative cover of different forest types, Clim: bad weather, PBack: playback monitoring. Sign for negative effects are shown explicitli.

Species incidence Estimation form Best model

CANIVORA Felis catus 0,06 Occupancy Model Ψ(VHght,LRoad) p(·) Leopardus guigna 0,46 Occupancy Model Ψ(ACor) p(Lure) Puma concolor 0,13 * Occupancy Model Ψ(PC2,ACor) p(Lure) Canis lupus familiaris 0,33 Occupancy Model Ψ(%Grsl,LRoad,ACor) p(Lure) Lycalopex culpaeus 0,07 * Occupancy Model Ψ(ACor) p(Lure) Lycalopex fulvipes 0,18 ** Occupancy Model Ψ(PC2,ACor) p(Lure) Lycalopex griseus 0,22 * Occupancy Model Ψ(%Grsl,ACor) p(Lure) Conepatus chinga 0,05 * Occupancy Model Ψ(VHght) p(·) Galictis cuja 0,05 Occupancy Model Ψ(Succ) p(·) Neovison vison 0,09 * Occupancy Model Ψ(Succ,ACor) p(·) Lontra provocax -- Arbitrary Estimation FALCONIFORMES Accipiter bicolor [= chilensis] 0,01 Naive Estimation Falco sparverius 0,10 Occupancy Model Ψ(%TCov) p(Visib) Falco femoralis 0,01 Naive Estimation Falco peregrinus 0,03 Naive Estimation Elanus leucurus 0,03 Logistic Regression Ψ(-PC1,ACor) Circus cinereus 0,01 Logistic Regression Ψ(%Grsl,ACor) Buteo albigula 0,07 Occupancy Model Ψ(TFor1,ACor) p(PBack) Buteo polyosoma 0,04 Logistic Regression Ψ(·) Buteo ventralis 0,04 Logistic Regression Ψ(·) Geranoaetus melanoleucus 0,02 Naive Estimation Milvago chimango 0,50 Occupancy Model Ψ(-PC1,-PC2,ACor) p(Clim,Visib) Caracara plancus 0,13 Occupancy Model Ψ(PC2,ACor) p(·) STRIGIFORMES Asio flammeus 0,02 Logistic Regression Ψ(-VHght) Glaucidium nanum 0,33 Occupancy Model Ψ(%Frst,-%Shrb,ACor) p(Clim,Visib) Strix rufipes 0,44 Occupancy Model Ψ(ACor) p(·) Tyto alba 0,08 Logistic Regression Ψ(PC2,ACor)

Objective 2: To quantify the functional similarity among predator species in the regional pool and, to assess the form of the corresponding SFR, and to estimate the expected FRic at surveyed sampling stations according to Ψ; and functional similarity of predators.

This objective was partially advanced in 2012, when the functional trait matrix was compiled and the SFR relationship for the entire regional assemblage was assessed (see details in Informe de Avance, 2da etapa). Now, it was completed by using occupancy models to assess the probability of occurrence of each species in each sample point, and then to estimate, by means of bootstraping, the expected species richness and functional richness (Fig. 1a,b). Functional richness (FRic) was estimated using the minimum convex hull volume algorithm proposed by Villéger et al. (2008, Ecology 89:2290-2301), which assess the multivariate volume in functional trait space that involves all the species in the assemblage.

Objective 3: To test differences between the functional richness of local top-predator assemblages in Chiloe and those in the continent.

Differences between the functional richness (FRic) of local top predators in Chiloé Island and the two continental regions were assessed by regressing FRic against species richness (S) and regions as factors. Overall, we detected significantly lower FRic values for sampling points in Chiloé than for the other two areas, according to the Hypothesis H1 (see ANOVA table below and Fig 2).

Table 2. ANOVA results d.f. SS MS F P Richness 1 0.0677 0.0677 1.188 < 0,0001 *** Region 2 0.0017 0.0009 15 4,95E-07 *** Residuals 331 0.0189 0.0001

However, a visual inspection of residuals of the association between FRic and S (Fig. 1c) show that differences, though significant, are subtle. In addition, such differences are not explained by difference in species richness due to poorer assemblages in the island (Fig. 2d). Thus, the lower than expected FRic in Chiloé may result either from local environmental filters or due to a more functionally homogeneous species pool in the island. Analyses performed during 2012 (see Informe de Avance, 2da etapa) support the second possibility, showing that while the SFR association for Palena Province and Coastal Range emulate that for the entire top-predator assemblage of southern Chile, the same association in Chiloé reach lower FRic value for comparable taxonomic richness levels due to the absence of several carnivore species (e.g. the puma, Puma concolor).

Figure 2. Association between functional richness and species richness for the top-predator assemblage of southern Chile. The continuous grey line in a and b represents the expected “species richness – functional richness” association (SFR), and the segmented lines are the corresponding 95% confidence limits. Figure b represents a zoom of figure a for the area of interest; and coloured points shows de origin of data according to colours in the boxplots in c and d.

Objective 4: To test whether the local top-predator assemblages in Chiloe and in the continent show lower FRic than expected from their S and the SFR.

This objective was completed by comparing the values of FRic predicted for each sample point against predictions from the SFR association. More specifically, we assessed whether such values fall outside the 95% confidence limit for the SFR. From Fig. 2a,b it is clear that the predicted FRic values fall entirely within such confidence interval. Then, there is not support to Hypothesis H2 of functional filters acting on local assemblages.

Objective 5: To test the interaction between response of local top-predator FR to land conversion and insularity.

FRic was regressed against each of the principal components obtained from the final PCA analisis perfomed on the environmental variables. The corresponding ANOVA tables show that only for the second principal component exists a significant interaction with region (Table 3). However, in this model the parameter corresponding to the interaction between PC2 and Chiloé Island was not significant. Thus, these results suggest that functional richnes does not respond more abruptly in Chiloé island, thus not supporting Hypotesis H3.

Table 3. ANOVA results (a) d.f. SS MS F P PC1 1 0.001382 0.0013818 57.131 0.0174 Region 2 0.006705 0.0033527 138.620 1.66e-06 PC1 x Region 2 0.000642 0.0003208 13.263 0.2669 Residuals 329 0.079573 0.0002419

(b) d.f. SS MS F P PC2 1 0.000000 0.0000001 0.0005 0.9819 Region 2 0.006483 0.0032417 13.3937 2,56E-03 PC2 x Region 2 0.002191 0.0010956 4.5268 0.0115 Residuals 329 0.079627 0.0002420

Table 4. Estimates of parameters for the lineal model relating FRic and PC2: FRic = b0 + b1 PC2 + b2 Chiloé + b3 Palena + b4 PC2 x Chiloé + b5 PC2 x Palena

Estimate Std. Error t value P

b0 0.081 0.0014336 56.647 < 2e-16

b1 -0.003 0.0013543 -2.116 0.03511

b2 -0.004 0.0020274 -2.150 0.03228

b3 0.005 0.0023715 2.278 0.02338

b4 -0.0006 0.0023125 -0.267 0.78982

b5 0.005 0.0020497 2.660 0.00819

Objective 6: To test the interaction between response of local top-predator FRic to species introduction, local S and insularity.

Finally, we assessed the existence of regional differences in the impact of introduced species on the functional richness of local top-predator assemblages. First, the bootstrapped FRic values for each simulated local assemblages were recalculated, and then subtracted to the corresponding original values. Then, the resulting difference was used as an indicator of the impact of introduced species, which was regressed against species richness and regions as factors. Contrary to predictions derived from the Hypothesis H4, there was no effect of regions or their interaction with species richness on the impact of introduced species on FRic

Table 5. ANOVA results. d.f. SS MS F P S 1 0.0187040 0.0187040 1029.2373 <2e-16 Region 2 0.0000603 0.0000302 16.593 0.1919 R x Region 2 0.0000422 0.0000211 11.610 0.3144 Residuals 329 0.0059788 0.0000182

Conclusion

Local top-predator assemblages in Chiloé island tend to show lower functional richness than those in the mainland. This seems to be directly associated to a higher level of functional redundancy in the island than in the continent. In turn, no support to hypotheses about the effects of local environmental filters was obtained. OTHER ACHIEVEMENTS OF THE PROJECT: - Research visit(s) to other institution(s). - Outreach activities related to the project’s main topic. - Any other contribution, not addressed elsewhere, that you consider important. The maximum length for this section is 1 page. (Arial or Verdana, font size 10).

During this study novel and relevant information about the conservation status and distribution of the Darwin’s fox (Lycalopex fulvipes) was obtained. This allowed the responsible investigator and the research team to participate as technical experts in different outreach activities oriented to the conservation and management of this species and the associated ecosystems during the last year:

July 9, 2013. INFORMATIVE DISSERTATION: “Nuevas localidades para el zorro de Darwin (Lycalopex fulvipes) en la Cordillera de la Costa de la Región de Los Ríos: antecedentes y perspectivas”. Presentation of new populations of Darwin’s fox to representatives of the National System of Protected Areas (SNASPE) and regional autorities. Edif. CONAF-Región de Los Ríos (Valdivia, Chile). November 19, 2013. WORKSHOP: “Reunión preparatoria Grupo de Trabajo Zorro Darwin Los Ríos”. Initial meeting towards the elaboration of a regional action plan for the conservation of the ecosystems of the Coastal Ranges of Los Ríos Region, with representatives and directors of the involved protected areas and the regional government. Edif. CONAF-Región de Los Ríos (Valdivia, Chile), . March 23, 2014. WORKSHOP: “Analisis de viabilidad y amenazas para el zorro de Darwin güiña y pudú en la Reserva Costera Valdiviana”. Technical advice for defining conservation objects, threats and prioritary actions in the Valdivian Coastal Reserve. Of. The Nature Conservancy (Valdivia, Chile). April 24, 2014. WORKSHOP: “Actualización de las iniciativas en pro de la conservación del Zorro de Darwin en Chile”. Coordination to enhance cooperation among the different organizations and researchers working with the problematic of Darwin’s fox conservation. Of. Parque Tantauco (Santiago, Chile). June 13, 2014. WORKSHOP: “Plan de recuperación, conservación y gestión del zorro de Darwin” (1st meeting). Technical advice to the Environment Ministry (MMA) for the develpoment of a national conservation/management action plan for the Darwin’s fox. Edif. MOP (Puerto Montt, Chile).

PRODUCTOS

ARTÍCULOS Para trabajos en Prensa/ Aceptados/Enviados adjunte copia de carta de aceptación o de recepción.

Nº : 1 Autor (a)(es/as) : Farias, AA.; Sepúlveda, MA.; Silva-Rodríguez, EA.; Eguren, A.; González D., Jordán, NI.; Ovando, E.; Stowhas, P.; Svensson, GL. Nombre Completo de la Revista : Revista Chilena de Historia Natural Título (Idioma original) : A new population of Darwin’s fox (Lycalopex fulvipes) in the Valdivian Coastal Range Indexación : ISI ISSN : Año : 2014 Vol. : 87 Nº : Páginas : 3 Estado de la publicación a la fecha : Publicada Otras Fuentes de financiamiento, si las hay : Wildlife Without Borders Program (U.S. Fish & Wildlife Service), Panthera Foundation

Envía documento en papel : si Archivo(s) Asociado(s) al artículo : 16_Farias_etal2014RCHN,NewPopLfulvipesValdivCoastRange.pdf http://sial.fondecyt.cl/index.php/investigador/f4_articulos/descarga/21158787/11110027/2013/60388/1/

Nº : 2 Autor (a)(es/as) : Farias AA., Svensson GL. Nombre Completo de la Revista : Journal of Mammalian Evolution Título (Idioma original) : Ecoregional vulnerability assessment for the functional richness of South American carnivorans (Mammalia: Carnivora) Indexación : ISI ISSN : Año : 2014 Vol. : Nº : Páginas : doi:10.1007/s10914-0 Estado de la publicación a la fecha : Publicada Otras Fuentes de financiamiento, si las hay :

Envía documento en papel : no Archivo(s) Asociado(s) al artículo : 17_Farias_Svensson2014JMammEvol,EcoregVulFRicSAmerCarniv(online_first).pdf http://sial.fondecyt.cl/index.php/investigador/f4_articulos/descarga/21158787/11110027/2013/60390/1/ OTRAS PUBLICACIONES / PRODUCTOS

Nº : 1 Autor (a)(es/as) : Vergara, PM; Rivera-Hutinel, A.; Farías, AA.; Cofré, H.; Samaniego, H.; Hahn, I. Título (Idioma original) : Aves y mamíferos del bosque Tipo de publicación o producto : Capítulo de Libro ISBN : Editor (es) (Libro o Capitulo de libros) :Donoso, C.; González, ME.; Lara, A. Nombre de la editorial /Organización : Ediciones Universidad Austral de Chile País : CHILE Ciudad : Valdivia Fecha : Agosto - 2014 Año : 2014 Vol. : Nº : Páginas : 207-234 Otras Fuentes de financiamiento, si las hay :

Envía documento en papel : no Archivo(s) Asociado(s) al artículo : 18_Vergara_etal2014Cap,AvesMamifBosque.pdf http://sial.fondecyt.cl/index.php/investigador/f4_otras_publicaciones/descarga/21158787/11110027/2013/16602/1/

Nº : 2 Autor (a)(es/as) : Vergara, PM.; Rivera-Hutinel, A.; Farías, AA.; Cofré, H.; Samaniego, H.; Hahn, I. Título (Idioma original) : ¿Cómo responden los animales del bosque a las perturbaciones antropogénicas? Tipo de publicación o producto : Capítulo de Libro ISBN : Editor (es) (Libro o Capitulo de libros) :Donoso, C.; González, ME.; Lara, A. Nombre de la editorial /Organización : Ediciones Universidad Austral de Chile País : CHILE Ciudad : Valdivia Fecha : Agosto - 2014 Año : 2014 Vol. : Nº : Páginas : 235-254 Otras Fuentes de financiamiento, si las hay :

Envía documento en papel : no Archivo(s) Asociado(s) al artículo : 19_Vergara_etal2014Cap,RespAvesMamifBosqueFragmentacion.pdf http://sial.fondecyt.cl/index.php/investigador/f4_otras_publicaciones/descarga/21158787/11110027/2013/16607/1/ CONGRESOS

Nº : 1 Autor (a)(es/as) : Farias, AA.; Svensson, GL. Título (Idioma original) : Presente y futuro de la diversidad funcional de ensambles de carnívoros del Cono Sur de Sudamérica Nombre del Congreso : XXV Jornadas Argentinas de Mastozoología y II Congreso Latinoamericano de Mastozoología País : ARGENTINA Ciudad : Buenos Aires Fecha Inicio : 06/11/2012 Fecha Término : 09/11/2012 Nombre Publicación : Año : Vol. : Nº : Páginas : Envía documento en papel : no Archivo Asociado : Farias25562713A.pdf http://sial.fondecyt.cl/index.php/investigador/f4_congresos/descarga/21158787/11110027/2013/94603/1/

Nº : 2 Autor (a)(es/as) : Farias, AA.; Silva-Rodríguez, EA.; Sepúlveda, MA.; Svensson, GL. Título (Idioma original) : Discovery of a new population of the critically endangered Darwin’s fox (Lycalopex fulvipes): range expansion and conservation implications Nombre del Congreso : 11th International Mammalogical Congress (IMC11) País : REINO UNIDO DE GB E IRLANDA DEL NORTE Ciudad : Belfast Fecha Inicio : 11/08/2013 Fecha Término : 16/08/2013 Nombre Publicación : Año : Vol. : Nº : Páginas : Envía documento en papel : si Archivo Asociado : Farias_et_al._Resumen_IMC111.pdf http://sial.fondecyt.cl/index.php/investigador/f4_congresos/descarga/21158787/11110027/2013/94605/1/

Farias_et_al_2013_IMC11_Darwins_fox.pdf http://sial.fondecyt.cl/index.php/investigador/f4_congresos/descarga/21158787/11110027/2013/94605/2/

Invoice_IMC11.pdf http://sial.fondecyt.cl/index.php/investigador/f4_congresos/descarga/21158787/11110027/2013/94605/3/ Nº : 3 Autor (a)(es/as) : Farias, AA.; Carrasco, GJ.; Fuentes, FS.; Glade, NS. Título (Idioma original) : Compensatory responses to deforestation of two owl species in southern South America temperate forests Nombre del Congreso : IX INTECOL País : REINO UNIDO DE GB E IRLANDA DEL NORTE Ciudad : Londres Fecha Inicio : 18/08/2013 Fecha Término : 23/08/2013 Nombre Publicación : Año : Vol. : Nº : Páginas : Envía documento en papel : si Archivo Asociado : Farias_et_al_Resumen_INTECOL.pdf http://sial.fondecyt.cl/index.php/investigador/f4_congresos/descarga/21158787/11110027/2013/94606/1/

Farias_etal_Poster_INTECOL.pdf http://sial.fondecyt.cl/index.php/investigador/f4_congresos/descarga/21158787/11110027/2013/94606/2/

Invoice_INTECOL2013_b.pdf http://sial.fondecyt.cl/index.php/investigador/f4_congresos/descarga/21158787/11110027/2013/94606/3/

TESIS/MEMORIAS

Nº : 1 Título de Tesis : Respuesta de ensambles de aves rapaces a cambios en la cobertura del bosque templado del sur de Chile Nombre y Apellidos del(de la) Alumno(a) : Nadia Medina Daza Nombre y Apellidos del(de la) Tutor(a) : Fabian Jaksic Andrade; Ariel Farias Piccolini Título Grado : Pregrado Institución : PONTIFICIA UNIVERSIDAD CATOLICA DE CHILE País : CHILE Ciudad : SANTIAGO Estado de Tesis : Terminada Fecha Inicio : 01/01/2012 Fecha Término : 04/07/2012 Envía documento en papel : no Archivo Asociado : 11110027_Inscripcion296NMedina.pdf http://sial.fondecyt.cl/index.php/investigador/f4_tesis_memorias/descarga/21158787/11110027/2013/49209/1/ Resumen_296_N_Medina.pdf http://sial.fondecyt.cl/index.php/investigador/f4_tesis_memorias/descarga/21158787/11110027/2013/49209/2/ 11110027_Aprobacion296NMedina.pdf http://sial.fondecyt.cl/index.php/investigador/f4_tesis_memorias/descarga/21158787/11110027/2013/49209/3/ Nº : 2 Título de Tesis : Uso de hábitat por especies comunes de aves rapaces (Falconiformes y Strigiformes) en agro-ecosistemas y bosques fragmentados del sur de Chile Nombre y Apellidos del(de la) Alumno(a) : Camila Contreras Alarcón Nombre y Apellidos del(de la) Tutor(a) : Fabian Jaksic Andrade; Ariel Farias Piccolini Título Grado : Pregrado Institución : PONTIFICIA UNIVERSIDAD CATOLICA DE CHILE País : CHILE Ciudad : SANTIAGO Estado de Tesis : Terminada Fecha Inicio : 01/01/2012 Fecha Término : 04/07/2012 Envía documento en papel : no Archivo Asociado : 11110027_Inscripcion296CContreras.pdf http://sial.fondecyt.cl/index.php/investigador/f4_tesis_memorias/descarga/21158787/11110027/2013/49210/1/ Resumen_296_C_Contreras.pdf http://sial.fondecyt.cl/index.php/investigador/f4_tesis_memorias/descarga/21158787/11110027/2013/49210/2/ 11110027_Aprobacion296CContreras.pdf http://sial.fondecyt.cl/index.php/investigador/f4_tesis_memorias/descarga/21158787/11110027/2013/49210/3/

Nº : 3 Título de Tesis : Evaluacion cuantitativa de la efectividad de aves rapaces como indicadores de la degradacion del bosque nativo del sur de Chile, mediante modelos de ocupación Nombre y Apellidos del(de la) Alumno(a) : Corina Pia Valencia Parada Nombre y Apellidos del(de la) Tutor(a) : Cristobal Briceño; Ariel Alejandro Farias Título Grado : Pregrado Institución : Universidad de Chile País : CHILE Ciudad : Santiago Estado de Tesis : En Ejecución Fecha Inicio : 15/01/2014 Fecha Término : 15/12/2014 Envía documento en papel : no Archivo Asociado : CertifPresentacionProyecto.pdf http://sial.fondecyt.cl/index.php/investigador/f4_tesis_memorias/descarga/21158787/11110027/2013/49790/1/

Nº : 4 Título de Tesis : Modelamiento de la distribución del zorro de Darwin Nombre y Apellidos del(de la) Alumno(a) : Kendra Melisa Ivelic Astorga Nombre y Apellidos del(de la) Tutor(a) : Fabian Jaksic; Ariel Alejandro Farias Título Grado : Pregrado Institución : Pontificia Universidad Catolica de Chile País : CHILE Ciudad : Santiago Estado de Tesis : Terminada Fecha Inicio : 01/02/2014 Fecha Término : 15/07/2014 Envía documento en papel : no Archivo Asociado :

Certificado_BIO295_K_Ivelic.pdf http://sial.fondecyt.cl/index.php/investigador/f4_tesis_memorias/descarga/21158787/11110027/2013/49791/2/