Research Article |
|
Corresponding author: Juan Sebastián Moreno ( semoreno113@gmail.com ) Academic editor: João Farminhão
© 2025 Juan Sebastián Moreno, Angie Tatiana Herrera Cobo, Rubén Darío Palacio, Nicolas A. Hazzi.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Moreno JS, Herrera Cobo AT, Palacio RD, Hazzi NA (2025) Chronicle of a death foretold: Lepanthes nasariana (Orchidaceae, Pleurothallidinae), a newly described high-Andean orchid facing a worst-case climate change scenario. PhytoKeys 266: 219-240. https://doi.org/10.3897/phytokeys.266.161410
|
Newly discovered species are increasingly found to be threatened. For some, their formal description may already foretell their extinction, a phenomenon we here term the “Nasar Effect.” This phenomenon is inspired by the tragic fate of Santiago Nasar, the protagonist of Gabriel García Márquez’s Chronicle of a Death Foretold, whose impending death is known to everyone but himself. The Nasar Effect is particularly evident in climate-vulnerable ecosystems, where species may be projected for extinction based on dramatic climate-driven habitat loss. We illustrate the “Nasar Effect” through the description of a new orchid species, Lepanthes nasariana (Lepanthes subsect. Breves), endemic to the cloud forests and páramos of the Western and Central Andes of Colombia, between 2,800 and 3,600 m elevation. The species inhabits mossy branches in shaded, humid environments and is most similar to L. mefueensis, from which it differs by its oblong-lanceolate leaves, falcate petal lobes, and narrowly ovate lip blades with an inflexed appendix, among other characters. Based on its current extent of occurrence (27,502 km2) and area of occupancy (12,775 km2), L. nasariana is preliminarily assessed as Least Concern (LC) following the IUCN Red List guidelines. However, species distribution models projected to 2090 under the SSP5–8.5 scenario indicate a 96% loss of suitable habitat, which would qualify the species as Critically Endangered (CR) under Criterion A3(c). Without immediate and concerted global efforts to mitigate emissions, L. nasariana exemplifies the potential fate of many species described from climate-vulnerable ecosystems, such as the high Andean mountains, where they may already be on a predestined short path to extinction.
Biodiversity loss, conservation strategies, endemism, extinction risk, habitat fragmentation, habitat suitability, high-emission scenarios, montane ecosystems
The ongoing human-caused planetary crisis is driving an unprecedented rate of biodiversity loss, threatening ecosystems and the balance of life on Earth (
Climate change impacts on mountain ecosystems extend far beyond rising temperatures, triggering a cascade of ecological disruptions. These include shifts in precipitation patterns, altered hydrological cycles, and reduced cloud cover (
Ultimately, climate change patterns pose a severe threat to the survival of highly specialized mountain species, exacerbating the biodiversity crisis in these ecosystems. This is particularly concerning in the tropical Andes, one of the most biodiverse regions on the planet, exhibiting high levels of endemism and species turnover (
Climate change can also disrupt critical phenological events, leading to mismatches between flowering periods and pollinator activity (
Lepanthes Sw. is not only one of the most diverse genera of orchids but is also considered a megadiverse plant genus globally, with 1,196 described species (
In this study, we describe a newly discovered species of Lepanthes with a narrow distribution in high-elevation cloud forests and páramo ecosystems of the Western and Central Cordilleras of the Colombian Andes. We apply species distribution models (SDMs) to assess its current and potential future distribution under different climate change scenarios. Based on these analyses, we use IUCN Red List criteria to evaluate its present and projected conservation status (
Descriptions and drawings were prepared from living specimens and flowers preserved in 70% ethanol. Vegetative structures were measured from dried material, and reproductive structures from spirit material. Digital images were taken with a Nikon D750 camera and a 105 mm f/2.8 macro lens. Sketches from specimens were digitized and used to create a draft template in Adobe Photoshop® CS6. A digital composite line drawing was then made (lines and stippling) using the Procreate illustration application on an iPad 6th-generation tablet computer (
A total of nine records were obtained for the new species, along with specimens consulted from the following herbaria: AMES, CAUP, COL, CUVC, HUA, JAUM, JBB, TOLI, and VALLE. These records provided the data used to model the species’ distribution. Environmental data were retrieved from the WorldClim database (https://www.worldclim.org;
The distribution of the new species was estimated using the Maxent algorithm (
To assess the conservation status of the new Lepanthes species, we applied IUCN Red List criteria A and B (
For Criterion A, which evaluates population reductions based on past, present, or projected declines, we used species distribution models (SDMs) to estimate habitat loss over time. Projections were calculated to 2090 under two climate scenarios (SSP2–4.5 and SSP5–8.5). Although the strict application of Criterion A requires declines to be measured over three generations or 10 years (whichever is longer, up to 100 years), generation length is currently unknown for Lepanthes nasariana and most related miniature orchids. We therefore used habitat reduction as a precautionary proxy for population reduction, as recommended in the IUCN Red List Guidelines and in line with
For Criterion B, we estimated the current extent of occurrence (EOO) and area of occupancy (AOO) using the ConR package in R (
We note that our extinction risk analyses based solely on SDMs do not meet the methodological standards required for a formal assessment under Criterion E, which is typically based on population viability analyses (PVAs) or coupled habitat–population models. Consequently, results from such analyses are presented here as an exploratory evaluation of climate-driven risk, but not as a formal application of Criterion E under the Red List framework.
All spatial analyses were conducted using ArcGIS Pro 2.8 (Esri, Redlands, CA, USA) and R 4.1.0 (
Colombia • Valle del Cauca: Municipio de Cali, Vereda Peñas Blancas, PNN Farallones de Cali, Minas del Socorro, Quebrada La Española, 3115 m, 29 January 2020, R. Galindo-T, A. Fierro, G. Rodríguez, and M. Espitia 1473 (holotype: CUVC; isotype: CUVC).
Lepanthes nasariana J.S.Moreno & Hazzi. A. Habit; B. Flower; C. Dissected perianth showing the dorsal sepal, lateral sepals, petals, and lip; D. Lip, column, and ovary (lateral view); E. Lip: left, dorsal view in natural position with the anther cap; right, expanded view showing the laminae, body, and connectives; F. Anther cap and pollinia: left, dorsal view of anther cap; right, ventral view showing its attachment surface and paired pollinia. Drawing by J.S. Moreno.
The new species is most similar to Lepanthes mefueensis Luer & R.Escobar, but it can be distinguished mainly by its succulent, oblong-lanceolate leaves (vs. elliptic leaves); transversely bilobed petals with both lobes narrowly triangular, falcate, and a marginal triangular midlobe (vs. lobes narrowly oblong); and the lip with blades narrowly ovate with a filiform and pubescent inflexed appendix (vs. ovate blades and a filiform, reflexed appendix).
Plants small in size, epiphytic, caespitose, up to 4.5–5.0 cm tall; roots slender, flexuous, filiform, 0.5 mm in diameter. Ramicauls slender, tight, suberect 18–23 mm long, enclosed by 4–5 acuminate, furrowed, and microscopically pubescent lepanthiform sheaths, with a dilated, ciliate ostia. Leaves purple abaxially, coriaceous, succulent, oblong-lanceolate, 15.7–20.3 × 3.3–4.7 mm, apex emarginate with an abaxial apiculum in the middle, base cuneate, contracted into a petiole 2–3 mm long. Inflorescence a congested, distichous raceme, 12–20 successively many-flowered, up to 18 mm long, including the pseudopeduncle of each multi-flowered coflorescence, held appressed to the abaxial surface of the leaf by a filiform, terete pseudopeduncle, 3 mm long, borne near the apex of the ramicaul; floral bracts purple, conical, acuminate, minutely verruculose, 0.5–0.7 mm long; pedicels terete, up to 1 mm long. Ovary terete, costate, sparsely verrucose, up to 0.7 mm long. Flowers with burgundy dorsal sepals with saffron margins, the lateral sepals saffron, slightly tinged with light burgundy along the midvein; petals with a vermilion upper lobe and saffron lower lobe with the apex tinged with light burgundy; lip blades crimson, degrading to saffron towards the apex, column crimson degrading to white near the apex. Dorsal sepal ovate, acuminate, denticulate, apex reflexed, 3-veined, carinate, 2.6–2.7 × 1.4–1.5 mm, connate to the lateral sepals for 0.5 mm. Lateral sepals ovate, acuminate, denticulate, oblique, slightly attenuate, 1-veined, 2.5–2.6 × 0.9–1.0 mm, connate for 1 mm. Petals transversely bilobed, lobes narrowly triangular, falcate, ciliate, microscopically pubescent, obtuse, 0.5–0.6 × 1.4–1.6 mm, with a filiform marginal triangular midlobe. Lip bilaminate, microscopically pubescent; blades narrowly ovate, acute, bases rounded, 0.88–0.90 × 0.24–0.31 mm, supported by cuneate connectives from near the base; body broad, adnate to the base of the column; sinus obtuse, with a filiform, oblong, pubescent, inflexed appendix, emerging from the base of the main structure, concealed in dorsal view and visible only in lateral view. Column terete, dilated, with the stigma bilobed with oblong lobes, 0.9–1.0 mm long, anther dorsal, stigma ventral. Anther cap cordate, cucullate, 0.2 mm wide. Pollinia 2, yellow, pyriform, narrowly obovoid, 0.4 mm long.
The specific epithet nasariana refers to Santiago Nasar, the protagonist of the novel “Chronicle of a Death Foretold” by Colombian author Gabriel García Márquez. The name was chosen in allusion to the character’s tragic fate—unaware of the threats around him, he is doomed to die prematurely. This mirrors the situation of the newly described species: although it may appear stable today, its extinction is predicted in the near future. The species is expected to undergo a “foretold death” due to the increasing frequency and intensity of extreme climatic events, driven by anthropogenic acceleration of climate change. While climate has always fluctuated naturally, it is the unprecedented speed and magnitude of current shifts—caused by human activity—that now pose a critical threat to biodiversity.
The species occurs in high Andean forests and páramos of the Western and Central Andes, extending toward the Colombian Massif. It thrives in highly humid forests with small-statured trees near streams, often dominated by abundant moss. These forests are characterized by tree species such as Brunellia goudotii Tul., Hesperomeles ferruginea (Juss. ex Pers.) Benth., Myrcianthes rhopaloides (Kunth) McVaugh, Weinmannia pubescens Kunth, and Weinmannia rollottii Killip. Co-occurring epiphytic orchids commonly found in these habitats include Lepanthes intonsa Luer, Fernandezia myrtillus (Rchb.f.) Garay & Dunst., Gomphichis altissima Renz, and Epidendrum restrepoanum A.D.Hawkes
Colombia • Valle Del Cauca: Municipio de Pradera, Finca La Esperanza, sobre camino ceja que conduce al páramo de las Tinajas, 3482 m, Jul 2018, G. Reina, I. Nicholls & H. Arenas 2651 (CUVC); • Cauca: Municipio de Puracé, Corregimiento de Paletará, vía Paletará – Isnos, PNN Puracé, 3100 m, July 2024, A. Zuluaga & J.S. Moreno 6347 (CUVC); Municipio de Totoró, Corregimiento de Gabriel López, 3110 m, March 2016, J.S. Moreno & A. Erazo 260 (CAUP); • Caldas: Municipio de Riosucio, Arroyo Hondo, bosque de la truchera de los Alpes vía Jardín–Andes, 2800 m, October 2021, T. Arias, S. Vieira, E. Restrepo & D. Cadavid 711 (CUVC); • Quindío: Municipio de Salento, cerca de las Crestas de Salento, predio privado, 2900 m, October 2024, E. Restrepo & S. Styles 296 (JBB); • Tolima: Municipio de Roncesvalles, Yerbabuena, 3366 m, November, 2018 M. Rincón & J.S. Moreno 2350 (TOLI).
Colombia. Antioquia: Municipio de Urrao, Páramo de Frontino, 3413 m, August 2021, S. Vieira & E. Dominguez (Photo!); Municipio de Urrao, Alto del Diablo, 3584 m, November 2020, S. Vieira & E. Dominguez (Photo!).
Lepanthes nasariana belongs to subgenus Lepanthes, section Lepanthes, subsection Breves
As stated in the diagnosis, L. mefueensis, a species of L. subsect. Breves restricted to the Cordillera Oriental of Colombia (Norte de Santander), is the most similar to L. nasariana. However, L. nasariana can be readily distinguished by its plants with succulent, oblong-lanceolate leaves, purple abaxially (vs. coriaceous, elliptic leaves, green abaxially); ramicauls shorter, enclosed by 4–5 acuminate, furrowed lepanthiform sheaths (vs. 7–9 long-ciliate sheaths with dilated ostia); and racemes congested and up to 18 mm long, borne appressed to the abaxial surface of the leaf (vs. shorter racemes, c. 5 mm long, borne behind the leaf). Floral morphology also provides clear diagnostic differences: dorsal sepal ovate, acuminate, denticulate, reflexed at the apex, 2.6–2.7 mm long (vs. elliptic, subacute to obtuse, abruptly acuminate, margins smooth, 2.75 mm long); lateral sepals ovate, acuminate, denticulate, 2.5–2.6 mm long (vs. glabrous, ovate, acute, 3 mm long); petals transversely bilobed with narrowly triangular, falcate, ciliate lobes and a small triangular midlobe (vs. transversely bilobed with narrowly oblong, obtuse, subequal lobes, without a midlobe); lip blades narrowly ovate, acute, with a filiform, pubescent, inflexed appendix hidden in dorsal view (vs. ovate blades with rounded ends, appendix filiform, reflexed, and exposed in dorsal view).
L. nasariana also shows affinity with L. trifurcata Luer & R. Escobar, another member of L. subsect. Breves, but L. nasariana has succulent, oblong-lanceolate leaves, 15–20 mm long (vs. coriaceous, ovate leaves, ca. 35 mm long); shorter ramicauls of 18–23 mm with 4–5 lepanthiform sheaths (vs. longer ramicauls of 50–60 mm with 7 sheaths); and congested racemes up to 18 mm long, appressed to the abaxial surface of the leaf (vs. subcongested racemes only 3–5 mm long, borne behind the leaf). Floral differences are equally marked: in L. nasariana, the dorsal sepal is ovate, denticulate, 2.6–2.7 mm long (vs. subelliptic, glabrous, 6.5 mm long); the lateral sepals are 2.5–2.6 mm long, ovate, denticulate, connate for 1 mm (vs. narrowly ovate, 6.5 mm long, margins denticulate, only barely connate at the base); the petals are transversely bilobed, with narrowly triangular, falcate lobes and a marginal triangular midlobe (vs. deeply trilobed, with three similar, diverging, narrowly triangular lobes, including a long central lobe 2 mm in length); and the lip has narrowly ovate blades with a filiform, pubescent, inflexed appendix concealed in dorsal view (vs. lobes deeply bifid, falcate, enclosing the column, with a recurved, external appendix visible dorsally).
The distribution model for Lepanthes nasariana exhibited high predictive performance, achieving an AUC_mean of 0.94 (SD = 0.042), well above random expectations. The model identified suitable habitat primarily in high montane and páramo ecosystems within the Central and Western Cordilleras of the Colombian Andes, at elevations of 2,500–3,200 m a.s.l. (Fig.
Current climate suitability model of Lepanthes nasariana J.S.Moreno & Hazzi, based on Maxent. A. Binary presence–absence map derived from the minimum training presence threshold, where red indicates areas predicted as suitable (presence = 1) and white indicates unsuitable areas (absence = 0); B. Continuous habitat suitability map showing logistic output values from 0 (unsuitable, dark green) to 1 (highly suitable, orange). White circles mark known occurrence records used to train the model.
Currently, L. nasariana occupies an estimated 12,775 km2 of suitable habitat. However, under future climate scenarios, significant habitat loss is projected. By 2061–2080, the SSP2–4.5 scenario predicts a 52% reduction in suitable habitat, leaving only 6,125 km2. The SSP5–8.5 scenario projects an even more severe reduction of 79%, reducing the suitable habitat to 2,625 km2. Further into the future, by 2081–2100, the SSP2–4.5 scenario estimates a slight recovery to 5,825 km2 (a 54% reduction from the current extent), while the SSP5–8.5 scenario predicts an almost complete collapse, with just 525 km2 remaining—equivalent to a staggering 96% loss of suitable habitat compared to present conditions (Figs
Projected changes in the potential distribution of Lepanthes nasariana J.S.Moreno & Hazzi, under future climate scenarios. A. SSP2-4.5 scenario for 2070; B. SSP5-8.5 scenario for 2070; C. SSP2-4.5 scenario for 2090; D. SSP5-8.5 scenario for 2090. Blue indicates stable habitat, red indicates habitat loss. Each map represents the ensemble average of multiple GCMs under intermediate (SSP2-4.5) and high (SSP5-8.5) greenhouse gas emission pathways.
Uncertainty in the projections was quantified through coefficient of variation maps (Suppl. material
The current geographic distribution of Lepanthes nasariana reveals an extent of occurrence (EOO) of 27,502 km2 and an area of occupancy (AOO) of 12,775 km2. These values exceed the thresholds required to trigger Criterion B. Therefore, under current conditions, the species qualifies as Least Concern (LC).
Nonetheless, field observations indicate that L. nasariana is restricted to fewer than ten fragmented locations in the Western and Central Andes of Colombia. These populations are largely isolated and occur within forest remnants under anthropogenic pressure, including agriculture, cattle grazing, and forest degradation. While these conditions do not meet quantitative thresholds for Criterion B, they highlight the species’ ecological vulnerability and the need for monitoring and site-level protection.
Climate-based SDMs projected to 2090 under SSP2–4.5 and SSP5–8.5 indicate a drastic contraction in suitable habitat, with a range-wide loss of up to 96%, leaving only two small refugia (Puracé and Nevados National Parks). This projected reduction suggests that L. nasariana would meet thresholds for Critically Endangered (CR) under Criterion A3(c), which considers projected declines of ≥ 80% due to habitat loss. Given the lack of species-specific generation length data, these projections should be interpreted as precautionary, exploratory assessments rather than definitive categorizations under Criterion A.
In addition, stochastic risk analyses based on SDM outputs indicated a high probability of extinction within 100 years. However, because these analyses do not constitute formal population viability analyses (PVAs), they cannot be considered a valid application of Criterion E under the IUCN framework. Instead, they should be viewed as complementary evidence underscoring the urgency of conservation interventions in light of climate-driven habitat loss.
Presently, Lepanthes nasariana does not qualify as threatened under Criterion B, given its current EOO and AOO. However, climate projections indicate severe future habitat contraction, consistent with thresholds for CR under Criterion A3(c) when interpreted within a precautionary framework. While our extinction risk modeling cannot formally support Criterion E, it highlights the likelihood of future population collapse if climate trajectories follow high-emission pathways. Together, these findings emphasize the importance of proactive conservation action and frequent reassessment of the species’ status.
This study documents the discovery of Lepanthes nasariana, a narrowly distributed orchid species endemic to the highlands of the Colombian Andes, whose extinction risk is already alarmingly high. Our models project that under the high-emission SSP5–8.5 scenario, the species will lose approximately 96% of its current suitable climatic habitat by 2090, with remnant populations restricted to small climatic refugia in Nevados and Puracé National Natural Parks. Under present conditions, the species qualifies as Least Concern (LC), given its current extent of occurrence (27,502 km2) and area of occupancy (12,775 km2), which are well above thresholds for Criterion B. However, such a drastic future range contraction suggests that the species would meet thresholds for Critically Endangered (CR) under Criterion A3(c) when interpreted within a precautionary and exploratory framework, as these projections are based on habitat loss rather than generation-length-specific reductions. We refer to this phenomenon—where a species’ future viability is already severely compromised at the moment of its scientific description—as the “Nasar Effect,” inspired by “Chronicle of a Death Foretold” (
The case of L. nasariana illustrates a broader and increasingly common pattern in high-elevation tropical ecosystems. Global warming is projected to cause substantial range contractions in many high-Andean plants, particularly those restricted to páramos and upper montane forests. These ecosystems—among the most threatened in the Andes—are expected to undergo severe contraction or disappearance by the mid-21st century under multiple climate scenarios in Colombia (
Within orchids, the genus Lepanthes is emblematic of this vulnerability: approximately 70% of Colombian species are endemic and primarily restricted to montane regions (
From a conservation perspective, our results underscore the urgency of adopting integrated strategies that combine in situ and ex situ measures. Protecting and restoring suitable habitats, establishing ecological corridors to facilitate altitudinal migration, and identifying and safeguarding potential climate refugia are critical for high-Andean orchids and other vulnerable flora. Ex-situ measures such as seed banking, cultivation in botanical gardens, and research into reproductive biology, genetic diversity, and population dynamics will be vital for building resilience and adaptive capacity (
We recognize, however, that species distribution models (SDMs) have inherent limitations. As correlative models, they assume that current climate–distribution relationships will hold under future conditions and that climate is the dominant driver of distribution at the scales analyzed. They may not fully account for microclimatic heterogeneity, dispersal limitations, or biotic interactions (e.g., pollinators, mycorrhizal fungi), nor for non-climatic threats such as habitat destruction. Although we used continuous suitability models and downscaled climatic data to better reflect fine-scale variation in the Andes, caution is warranted when interpreting projections, particularly for species with highly specialized niches and few occurrence records (
In conclusion, Lepanthes nasariana exemplifies how newly discovered species in biodiversity hotspots can already be on a trajectory toward extinction due to climate change. Much like Santiago Nasar’s fate in García Márquez’s novel, the species’ projected decline appears inevitable under current trends—but unlike Nasar’s story, there is still time to act. The challenge for conservation biology is to apply the precautionary principle, prioritize conservation planning and modeling under realistic to worst-case climate trajectories, and implement targeted conservation actions before the “death foretold” becomes reality for L. nasariana and countless other high-Andean plants.
The authors thank Tatiana Arias, Eugenio Restrepo, Guillermo Reina, Gustavo Pisso, and Sebastián Viera for sharing distribution records of the species. Special thanks go to Robinson Galindo from Parques Nacionales Naturales de Colombia for supporting orchid research in the Farallones de Cali National Natural Park, whose collection served as the type specimen for the new species.
The authors have declared that no competing interests exist.
No ethical statement was reported.
AI-assisted writing support (ChatGPT, OpenAI) was used to improve the English grammar, structure, and clarity of the manuscript. All content was conceived, written, and verified by the authors, who take full responsibility for its accuracy and interpretation.
This research was funded by Fundación Ecotonos, Cali, Valle del Cauca, Colombia.
J.S. Moreno and N. Hazzi contributed equally to this work. They jointly conceived and wrote the manuscript. N. Hazzi led the species distribution modeling, with analytical support from A. Herrera. J.S. Moreno conducted the taxonomic description and the IUCN Red List assessment. R.D. Palacio contributed to refining and finalizing the manuscript and to the development of the conceptual framework referred to as the “Nasar Effect.”
Juan Sebastián Moreno https://orcid.org/0000-0003-4325-1232
Angie Tatiana Herrera Cobo https://orcid.org/0009-0005-1100-9056
Rubén Darío Palacio https://orcid.org/0000-0001-9029-3094
Nicolas A. Hazzi https://orcid.org/0000-0002-7657-8963
All of the data that support the findings of this study are available in the main text or Supplementary Information.
Supplementary figure S1
Data type: jpg
Explanation note: Uncertainty in ecological niche models for Lepanthes nasariana J.S.Moreno & Hazzi under current and future climate scenarios, based on the coefficient of variation (CV) across 15 Maxent replicates. Green indicates higher uncertainty, while blue indicates greater model agreement. A SSP2-4.5 scenario for 2070 B SSP5-8.5 scenario for 2070 C SSP2-4.5 scenario for 2090 D SSP5-8.5 scenario for 2090.