ArticlePublisher preview available

An Update of the Geographic Distribution of the Red-Mantled Saddle-Back Tamarin, Leontocebus lagonotus (Callitrichidae), in Ecuador

Authors:
To read the full-text of this research, you can request a copy directly from the authors.

Abstract and Figures

Understanding the geographic distributions of primates is necessary to ensure effective conservation strategies. Nonetheless, many gaps persist in information regarding the range limits of platyrrhines. Leontocebus lagonotus is no exception; it is one of the least studied primates in Ecuador and its geographic limits are poorly known. We obtained 296 records of its presence in Ecuador from field studies (between 1996 and 2020), museums, the literature, and databases. Of these, we validated 211 records and used 106 (excluding grouped points) to determine the potential distribution of this species using an ecological niche model (MaxEnt). The model suggested that the species’ distribution in Ecuador covers 64,028 km². Based on confirmed data, the extent of occurrence was 38,226 km², but after updating it with layers of remaining vegetation (2018), we determined that the current distribution is 32,643 km² (a 15% reduction). Our findings reduce the range proposed for the species in Ecuador, suggesting that areas north of the Napo River, the north-central area of Yasuní National Park, and the far eastern part of Waorani Ethnic Reserve were never part of the species’ range. We also identified the southern boundaries of its distribution, where the Paute-Upano and Cangaime-Morona rivers form a natural barrier. Its distribution in Peru possibly reaches the south of the Morona and Santiago rivers. We recommend a similar approach for other platyrrhines, particularly those under threat, for better implementation of conservation efforts.
This content is subject to copyright. Terms and conditions apply.
An Update of the Geographic Distribution
of the Red-Mantled Saddle-Back Tamarin,
Leontocebus lagonotus (Callitrichidae), in Ecuador
Diego G. Tirira
1,2,5
&Lidia Sánchez-Sánchez
3
&Sara Álvarez-Solas
4,5,6
Received: 14 December 2020 / Accepted: 15 April 2021/
#The Author(s), under exclusive licence to Springer Science+Business Media, LLC, part of Springer Nature 2021
Abstract
Understanding the geographic distributions of primates is necessary to ensure effective
conservation strategies. Nonetheless, many gaps persist in information regarding the
range limits of platyrrhines. Leontocebus lagonotus is no exception; it is one of the least
studied primates in Ecuador and its geographic limits are poorly known. We obtained
296 records of its presence in Ecuador from field studies (between 1996 and 2020),
museums, the literature, and databases. Of these, we validated 211 records and used
106 (excluding grouped points) to determine the potential distribution of this species
using an ecological niche model (MaxEnt). The model suggested that the species
distribution in Ecuador covers 64,028 km2. Based on confirmed data, the extent of
occurrence was 38,226 km2, but after updating it with layers of remaining vegetation
(2018), we determined that the current distribution is 32,643 km2(a 15% reduction).
Our findings reduce the range proposed for the species in Ecuador, suggesting that
areas north of the Napo River, the north-central area of Yasuní National Park, and the
far eastern part of Waorani Ethnic Reserve were never part of the speciesrange. We
also identified the southern boundaries of its distribution, where the Paute-Upano and
Cangaime-Morona riversform a natural barrier. Its distribution in Peru possibly reaches
the south of the Morona and Santiago rivers. We recommend a similar approach for
other platyrrhines, particularly those under threat, for better implementation of conser-
vation efforts.
Keywords Altitudinal range .Amazonia .Ecological niche model .Knowledge gaps .
Natural barriers .Rainforest
https://doi.org/10.1007/s10764-021-00221-7
Handling Editor: Joanna Setchell.
*Diego G. Tirira
diegotirira@gmail.com
Extended author information available on the last page of the article
Published online: 20 May 2021
International Journal of Primatology (2021) 42:600–617
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
... We considered both natural and anthropogenic barriers and filled gaps in our knowledge of this subspecies distribution. Model-based range maps are a promising tool that is currently being used to update the range distribution of an increasing number of species (Anderson, 2023;Garbino et al., 2015;Thorn et al., 2009;Tirira et al., 2021). ...
... The diagnostic characteristics used to distinguish the subspecies from their conspecific neighbors are summarized in Supporting Information: Table S2. When such direct confirmation was not possible, we followed Tirira et al. (2021) and used at least one of the following criteria: (i) data published in scientific literature; (ii) records carried out by experienced professionals; and (iii) records located unambiguously within the known subspecies' range. We excluded all records that did not meet at least one of these criteria. ...
... We used all confirmed records to establish the subspecies' elevation range. A polygon representing the subspecies EOO was created using a convex hull function that encompassed all confirmed occurrence records (i.e., IUCN extent of occurrence; Anderson, 2023;Tirira et al., 2021) surrounded by a buffer of approximately 1.5°. This polygon was considered to be the potential area of dispersal for the subspecies ( Figure 1) and was used as the model calibration area. ...
Article
Saimiri cassiquiarensis cassiquiarensis (Cebidae) is a primate subspecies with a wide distribution in the Amazonian region of Brazil, Colombia, and Venezuela. However, the boundaries of its geographic range remain poorly defined. This study presents new occurrence localities for this subspecies and updates its distribution using a compiled data set of 140 occurrence records based on literature, specimens vouchered in scientific collections, and new field data to produce model‐based range maps. After cleaning our data set, we updated the subspecies' extent of occurrence, which was used in model calibration. We then modeled the subspecies' range using a maximum entropy algorithm (MaxEnt). The final model was adjusted using a fixed threshold, and we revised this polygon based on known geographic barriers and parapatric congeneric ranges. Our findings indicate that this subspecies is strongly associated with lowland areas, with consistently high daily temperatures. We propose modifications to all range boundaries and estimate that 3% of the area of occupancy (AOO, as defined by IUCN) has already been lost due to deforestation, resulting in a current range of 224,469 km ² . We also found that 54% of their AOO is currently covered by protected areas (PAs). Based on these results, we consider that this subspecies is currently properly classified as Least Concern, because it occupies an extensive range, which is relatively well covered by PAs, and is currently experiencing low rates of deforestation.
... The Maxent model, which is based on niche theory, examines habitat characteristics using a set of species occurrence points and environmental variables (Phillips and Dudík 2008). The model has been regularly employed in research on possible mammalian habitats (Su et al. 2021;Sun et al. 2021;Tirira et al. 2021;Kufa et al. 2022). The model has the potential to contribute to biological conservation in two ways. ...
Article
Full-text available
The golden snub-nosed monkey (GSNM), Rhinopithecus roxellana, is an endangered species on the IUCN Red List, and the Yuhe National Nature Reserve in Gansu is one of its principal habitats. The GSNM’s protection and management rely heavily on predicting its probable suitable habitat. The Maxent model was used to examine the habitat suitability of GSNM in the Yuhe Nature Reserve and surrounding areas. Infrared cameras used to monitor GSNM in 2019–2020 provided the model with data. Through analysis and screening, 23 distribution sites of GSNM and five environmental variables were included in the final model. The findings revealed that the Yuhe Nature Reserve’s area of appropriate habitat for GSNM was 248.43 km2, accounting for 52.79 percent of the reserve’s total area and that this was concentrated in the core zone. The Maxent model was optimized using the Kuenm package, and the resulting value reached an exceptional level of 0.948. A Jackknife test revealed that the mean diurnal range was the most important environmental factor affecting the distribution of GSNM (45.84%). Finally, the planning of the reserve was generally in line with the predictions, and the functional zoning could be altered accordingly. We advised extending the reserve southward based on the study’s findings, while strengthening the supervision of marginal areas of the reserve.
Article
Full-text available
Biological invasions are one of the greatest existing threats to biodiversity. Invasive species can cause economic and environmental damage. Callithrix penicillata is naturally found in the Brazilian savanna and Caatinga. Its introduced populations have become a conservation problem due to its high occupancy potential, native fauna predation, competition with native primates, congeners and hybridization. We used Species Distribution Modeling (SDM) through the Maxent software in this study in order to identify areas with a higher probability of C. penicillata occurrence. The AUC value was close to 1 (AUC=0.966), with a curve value close to 1. Through the Jackknife test we observed that temperature seasonality was the variable most related to distribution (AUC=0.86), which agrees with other studies that show climatic variables influencing primate distribution. The Atlantic Forest in the Southeast and South regions of Brazil was indicated as susceptible to invasion by C. penicillata. The marmoset C. penicillata has become a successful invader of Atlantic Forest areas, causing depreciation in many native species and other problems. However, biological invasions might be mitigated or even extinguished through successful interventions and management.
Article
Full-text available
Owing to climate change, species’ geographical distribution may be extended, reduced or displaced in the future. Across species’ ranges, novel climate conditions may also expose species to thermal conditions for which they are not adapted. Migration toward more suitable climates will, however, only be possible if species are able to keep pace with climate change. Here, we analyze different metrics to predict the impacts of climate change on the distribution of Amazon primates. We found that this iconic group will be exposed to novel climate conditions in a large portion of their territories and most species might not be able to track their preferred environmental conditions, even when their range is forecasted to expand. Remaining future populations are expected to become fragmented and to occupy sub-optimal conditions at the periphery of their projected bioclimatic envelopes. Our results suggest that climate change may have unprecedented impacts on Amazon biodiversity, especially for species with low dispersal ability, such as primates. In addition to deforestation, hunting, and disease spread, climate change is likely to add up to conservation-defying feedbacks for Amazon primate populations’ fitness and resilience dynamics.
Article
Full-text available
Effective conservation strategies need to be created based on accurate and updated data on the distribution and conservation status of the species of concern. Not surprisingly, the most diverse countries which are currently facing the greater threats, tend to be those with the greatest lack of information. This is the case for Ecuador, where deforestation rates have been extremely severe, especially in the coastal region, where less than 10% of its original forest cover remains. Given the fact that primates rely on habitat connectivity for their survival, it is crucial to understand the impact of threats to their populations. To obtain data on the current distribution of the four primates known to inhabit western Ecuador, several organizations worked together to conduct the first primate census in coastal Ecuador from October 2016 to March 2017. Teams of 2−5 people walked existing trails and recorded both visual and auditory detections. We also conducted semi-structured interviews to members of local communities to complement field data. We surveyed 83 locations, and recorded 260 independent detections, along more than 300 km of trails, The four species known to occur in the region were detected: the Ecuadorian mantled howler Alouatta palliata aequatorialis; the Brown-headed Spider Monkey Ateles fusciceps; the Ecuadorian White-fronted Capuchin Cebus aequatorialis, and the Colombian White-faced Capuchin Cebus capucinus capucinus. Two other species, Aotus sp. and Saimiri sp., were mentioned during the interviews. This project is a clear example of what can be achieved when different organizations unify their efforts towards a single goal that provides the basis for future research, and suggests specific conservation measures to improve the conservation status of the primates.
Chapter
Full-text available
An overview on the presence and distribution of the family Callitrichidae (Primates) in Ecuador. I analyzed 488 records belonging to the four species of Callitrichidae recorded in Ecuador to know the historical overview, and distribution limits in the country. Gaps are discussed and necessary studies are proposed to reduce the shortcomings identified. I excluded information considered incorrect, although in most cases it has been mentioned. In summary, there are relevant gaps in knowledge of the distribution of the four species. To Cebuella pygmaea the southern and western boundaries are unknown. Leontocebus lagonotus is the species with more gaps; the available information is confusing in its eastern, northwestern, western and southern boundaries. On Leontocebus nigricollis not their western distribution limits are known and there are controversial records on the south side of the Napo River. For Leontocebus tripartitus its southern and western boundaries are unknown, and there are some unexpected records along Aguarico River, on the north side of the Napo River. I also commented on the likely presence of Callimico goeldii in Ecuador.
Article
The mechanisms that underlie the diversification of Neotropical primates remain contested. One mechanism that has found support is the riverine barrier hypothesis (RBH), which postulates that large rivers impede gene flow between populations on opposite riverbanks and promote allopatric speciation. Ayres and Clutton-Brock (1992) demonstrated that larger Amazonian rivers acted as barriers, delineating the distribution limits of primate species. However, profound changes in taxonomy and species concepts have led to the proliferation of Neotropical primate taxa, which may have reduced support for their results. Using the most recent taxonomic assessments and distribution maps, we tested the effect of increasing river size on the similarity of opposite riverbank primate communities in the Amazon. First, we conducted a literature review of primate taxonomy and developed a comprehensive spatial database, then applied geographical information system to query mapped primate ranges against the riverine geography of the Amazon watershed to produce a similarity index for opposite riverbank communities. Finally, we ran models to test how measures of river size predicted levels of similarity. We found that, almost without exception, similarity scores were lower than scores from Ayres and Clutton-Brock (1992) for the same rivers. Our model showed a significant negative relationship between streamflow and similarity in all tests, and found river width significant for the segmented Amazon, but not for multiple Amazon watershed rivers. Our results support the RBH insofar as they provide evidence for the prediction that rivers with higher streamflow act as more substantial barriers to dispersal, and accordingly exhibit greater variation in community composition between riverbanks.