Research Article |
Corresponding author: Osvaldo Villarreal ( osvaldovillarreal@gmail.com ) Corresponding author: Leonardo Delgado-Santa ( leonardodelgadosanta@gmail.com ) Academic editor: Adriano Kury
© 2023 Osvaldo Villarreal, Daniela Ahumada-C., Leonardo Delgado-Santa.
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:
Villarreal O, Ahumada-C. D, Delgado-Santa L (2023) Mapping the distribution of armored harvestmen (Opiliones, Laniatores) in Colombia: updated list of species, taxonomic contributions, and insight of diversity in protected areas. ZooKeys 1175: 223-284. https://doi.org/10.3897/zookeys.1175.102485
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Colombia is a biodiverse country with 1,486 protected areas covering almost 50 million hectares, yet little is known about the biodiversity they harbor, particularly in terms of harvestmen (Arachnida: Opiliones). This study provides a comprehensive updated summary of the armored harvestmen (Laniatores) species found in Colombia with a list of 173 nominal species, focusing on the Laniatores fauna found in protected areas and its diversity is detailed and analyzed. Maps with all records associated with ecoregions and protected areas in Colombia are presented. Additionally, three new Laniatores species are described here: Phalangodus andresi sp. nov. from the department of Cundinamarca, and Ventrifurca phallaina sp. nov. and Ampycella fortunata sp. nov. from the department of Valle del Cauca; and a new family assignment is proposed for Paraphalangodus Roewer, 1915, placing it in the family Nomoclastidae. Information available on Laniatores in the National System of Protected Areas is still scarce and promoting strategies to facilitate the regulatory procedures for collecting specimens in these areas and increasing investment in basic science projects, are suggested to improve the understanding and study of the Laniatores fauna and other invertebrates in Colombia. Finally, a chronicle and timeline set of figures of species of Laniatores from Colombia, described by various authors during three periods, is given.
Checklist, ecoregions, harvestmen, Neotropics, protected natural areas
Colombia is one of the most biodiverse countries in the world (
Since the publication of the New World Laniatores catalog by
The purpose of this paper was to provide an updated list of species and summarize the taxonomic changes and additions that occurred after 2003. Additionally, we aim to relate the distribution of Colombian species with the biogeographical areas proposed by WWF, discuss the presence of species in the country’s National System of Protected Areas (NSPA), and present the descriptions of two new cranaid species from the departments of Cundinamarca and Valle del Cauca as well as one new gonyleptid species from the department of Valle del Cauca.
The neotropical family Cranaidae has attracted attention from taxonomists in recent years; nevertheless, the definition of generic or suprageneric groups in this family remains unsatisfactory (
Only three works have analyzed the phylogenetic relationships within the family Cranaidae and the genus Phalangodus Gervais, 1842 has only been studied in a phylogenetic context in an analysis of the familial relationships of Gonyleptoidea (
Two species have been recorded from Colombia, belonging to the family Ampycidae, Ampycus telifer (Butler, 1873), and Licornus tama Villarreal & Kury, 2012 (
This paper describes three species: two new cranaid (Phalangodus and Ventrifurca) and one ampycid (Ampycella, including the first image of the male genitalia for the genus), collected in the departments of Cundinamarca in the Central Mountain Range in the Colombian Andes and the department of Valle del Cauca in Chocó Biogeographic region.
Individuals of each species were photographed using a Leica M205C stereoscope attached to a Leica DFC450 digital camera, a Wild Heerbrugg stereoscope attached to a Nikon COOLPIX P900 and a Wild Heerbrugg microscope attached to a HAYEAR 2307 digital camera. The multiple resultant images at different focal planes were combined with Combine ZP Suite software (
Morphological terminology and patterns of taxonomic description follow
The first-order administrative divisions of Colombia (departments) are underlined. Maps were made using ArcGIS® 10.1 software (
Morphometric abbreviations are:
AL = maximum abdominal scutum length;
AW = maximum abdominal scutum width;
BaCh = basichelicerite length;
Cl = claw;
CL = carapace length;
ClPp = pedipalp claw;
CW = maximum carapace width;
DS = dorsal scutum;
DSL = dorsal scutum length;
Fe = femur;
FeL I = femur length I;
FeL II = femur length II;
FeL III = femur length III;
FeL IV = femur length IV;
IOD = inter ocular distance;
MS = macrosetae of penis;
Mt = Metatarsus; ;
Pp = pedipalps;
FePp = pedipalpal femur;
PaPp = pedipalpal patella;
TaPp = pedipalpal tarsus;
TiPp = pedipalpal tibia;
Ta = tarsus;
Ti = tibia;
TiL I = tibia length I;
TiL II = tibia length II;
TiL III = tibia length III;
TiL IV = tibia length IV;
VP = ventral plate. All measurements are in mm unless otherwise noted. The material studied is deposited in the arachnological collections of
Instituto de Ciencias Naturales (
A comprehensive list of all described Laniatores species occurring in Colombia was compiled, based on the bibliography published until April 2023, including all valid species of Laniatores recorded for Colombia. The family and superfamily classification follows
A list of all protected areas under the NSPA jurisdiction, which harbor records of Laniatores species, was compiled. Only areas with some form of public regulation for their protection were considered. For each protected area, the families and species of armored harvestmen recorded were listed (Table
Category | RUNAP | Family | Species |
---|---|---|---|
Regional Integrated Management Districts (RDIM) | Cuenca alta del Río Atrato | Manaosbiidae | Camelianus fuhrmanni |
de la cuenca alta del Río Quindío de Salento | Cranaidae | Allocranaus columbianus | |
Nomoclastidae | Quindina bella | ||
Stygnidae | Eutimesius ephippiatus | ||
Delta del Río Ranchería | Cranaidae | Cranaus albipustulatus | |
Paramo de Guargua y laguna Verde | Cosmetidae | Rhaucus serripes | |
Paramo de guerrero | Cosmetidae | Rhaucus quinquelineatus | |
Páramos de Guantiva y la Rusia | Cosmetidae | Rhaucus papilionaceus | |
Río Rubachoque y pantano de arce | Cosmetidae | Rhaucus vulneratus | |
San Miguel | Cranaidae | Megacranaus pygoplus | |
Sector Salto del Tequendama y Cerro Manjui | Agoristenidae | Muscopilio onod | |
Cosmetidae | Eulibitia maculata | ||
Rhaucus serripes | |||
Serranía de los Yariguies | Agoristenidae | Leptostygnus yarigui | |
Cosmetidae | Rhaucus papilionaceus | ||
Cranaidae | Phalangodus briareos | ||
Serrania de Perija | Agoristenidae | Avima troglobia | |
Avima venezuelica | |||
National Natural Parks (NNP) | Chingaza | Cosmetidae | Libitia bipunctata |
Paramillo | Agoristenidae | Avima tuttifrutti | |
Sierra de la macarena | Cosmetidae | Meterginus prosopis | |
Cranaidae | Phareicranaus angelicus | ||
Sumapaz | Cosmetidae | Eulibitia maculata | |
Rhaucus vulneratus | |||
Fissiphalliidae | Fissiphallius spinulatus | ||
Yaigoje Apaporis | Cosmetidae | Sibambea cincta | |
Regional Natural Park (RNP) | Los Besotes | Cosmetidae | Eucynorta quadripustulata |
Serrania del Perija | Cosmetidae | Eulibitia victoriae | |
Sisavita | Cosmetidae | Eulibitia helena | |
Civil Society Nature Reserve (CSNR) | La Palmita | Cosmetidae | Eulibitia chacuamarei |
National Protective Forest Reserve (NPFR) | Bosque Oriental de Bogotá | Cosmetidae | Libitia bipunctata |
Libitia cordata | |||
Rhaucus quinquelineatus | |||
Rhaucus vulneratus | |||
Fissiphalliidae | Fissiphallius sturmi | ||
Fissiphallius sympatricus | |||
Stygnidae | Phareus raptator | ||
Cuenca alta del Río Cali | Cranaidae | Holocranaus calus | |
Rio Meléndez | Cranaidae | Holocranaus longipes | |
Río Nare | Cranaidae | Holocranaus calcar | |
Rios Blanco y Negro | Cosmetidae | Libitia bipunctata | |
Stygnidae | Phareus raptator | ||
Regional Protective Forest Reserve (RPFR) | Laguna de pantano redondo y el nacimiento Río Susagua | Cosmetidae | Libitia bipunctata |
Montes de Oca | Cosmetidae | Eucynorta quadripustulata | |
Flora and Fauna Sanctuary (FFS) | Guanentá-alto río Fonce | Cosmetidae | Eulibitia clytemnestra |
Iguaque | Cosmetidae | Eulibitia maculata | |
Libitia iguaque | |||
Stygnidae | Jabbastygnus huttorum |
In the species list, we utilize two types of dashes: the n-dash (–), used to indicate the reference of the original description, and the m-dash (—) to introduce each new subsequent bibliographic reference following the original description. After each species name, the m-dash is placed to separate a new citation.
Natural protected areas abbreviations: Civil Society Nature Reserve (CSNR); Flora and Fauna Sanctuary (FFS); National Protective Forest Reserve (NPFR); Regional Natural Park (RNP); Regional Protective Forest Reserve (RPFR); National Natural Parks (NNP); Regional Integrated Management Districts (RDIM).
Order Opiliones Sundevall, 1833
Suborder Laniatores Thorell, 1876
Phalangodus anacosmetus Gervais, 1842 (type species); Phalangodus briareos Villarreal & García, 2016; Phalangodus andresi sp. nov.; Phalangodus cottus Villarreal & García, 2016; Phalangodus gyes Villarreal & García, 2016; Phalangodus kuryi Villarreal & García, 2016; Phalangodus palpiconus (Roewer, 1943).
See
• Holotype: ♂ (
Phalangodus andresi sp. nov. can be distinguished from all other species of the genus except P. palpiconus by the (1) presence of conspicuous granulation of mesotergal areas I –IV, lateral borders of dorsal scutum, ocularium and posterior region of the carapace (Figs
Phalangodus andresi sp. nov. Male holotype (
Phalangodus andresi sp. nov. Male holotype (
Measurements of body and appendages. Holotype ♂ (
Male holotype (
Venter. Coxa I with a row of large tubercles of different sizes; II longer than I and III, with two median rows of low tubercles, the anterior one more conspicuous; III densely covered with irregular rows of small tubercles and with the posterior border sigmoid; IV strongly backward, with a median row of tubercles in the medium area and lateral border, and small tubercles densely distributed. Stigmatic area with a row of small tubercles on posterior border and minute granules sparsely distributed. Stigmata large, oval, and oblique. Free sternites with a row of small granules.
Chelicerae
(Figs
Pedipalps
(Figs
Legs
(Figs
Penis
(Fig.
Coloration (in alcohol)
(Figs
Female (
Ovipositor. Dorsal lobes (dl) and ventral lobes (vl) rounded, with four and two pairs of large, acuminated, single-tipped setae, respectively. The dl with three pairs of dorsal setae (ds) distally located and one pair basally located. Lateral region of the ovipositor with one pair of dorso-lateral setae (dls).
Known only from the type locality.
The species is named in honor of our colleague and friend, the arachnologist Andrés F. García, who has greatly enriched the field’s knowledge of Opiliones in Colombia and described the vast majority of species within the genus Phalangodus; moreover, he was the collector of the type series for this species.
Ventrifurca abnormis (Roewer, 1932); Ventrifurca albipustulata Roewer, 1913 (type species); Ventrifurca caffeinica Villarreal, Kury & Pinto-da-Rocha, 2015; Ventrifurca dybasi (Goodnight & Goodnight, 1947); Ventrifurca phallaina sp. nov.
• Holotype: ♂ (
Ventrifurca phallaina sp. nov. can be distinguished from V. abnormis by the scarce ornamentation of the mesotergal areas I to III; also, can be distinguished from all other species of the genus by the ornamentation pattern of the yellow tubercles on dorsal scutum, restricted to the lateral of carapace and posterolateral portion of DS (Figs
Ventrifurca phallaina sp. nov., male paratype (
Measurements of body and appendages. Holotype: (
Male holotype (
Venter
(Figs
Chelicerae
(Figs
Pedipalps
(Figs
Legs
(Figs
Penis
(Fig.
Ventrifurca phallaina sp. nov., male paratype (
Coloration (in alcohol)
(Fig.
Female (
Known only from the type locality.
Phallaina is a Greek word that means whale. It is used in apposition as a reference to the humpbacked shape of the species in lateral view.
Ampycella frizzellae (Mello-Leitão, 1942); Ampycella spiniventris Roewer, 1929 (type species); Ampycella fortunata sp. nov.
Outline of DS type alpha; four mesotergal areas well defined and unarmed; DS with small yellowish tubercle on the lateral margins (Fig.
• Holotype: ♂ (
Ampycella fortunata sp. nov. can be distinguished from the other two species of the genus by the size ratio between the spines on the free tergites: spine on free tergite II larger than the spine on free tergite III (Figs
Measurements of body and appendages. Holotype: (
Male holotype (
Venter
(Figs
Chelicerae
(Fig.
Pedipalps
(Figs
Legs
(Figs
Penis
(Fig.
Coloration (in alcohol)
(Fig.
Female (
Known only from the type locality.
fortunata is a Latin word that means happy, lucky, and blessed. It is used in reference to the meaning of the name of the type locality Buenaventura.
Among the known genitalia, only Licornus tama Villarreal & Kury, 2012 and Hernandarioides plana F.O. Pickard-Cambridge, 1905 have an elongated ventral plate. However, both genera have a subtle distal cleft in the distal border of the VP, which is not the typical deep cleft seen in the subfamily (e.g., Hexabunus Roewer, 1913, Hutamaia Soares & Soares, 1977, Thaumatocranaus Roewer, 1932). Ampycella fortunata sp. nov. shares the presence of an elongated ventral plate, but it is unique in not having a distal cleft. Additionally, a pair of large, apically pointing MS-D is observed in Ampycella fortunata, which is also observed in some of the genera whose genitalia is known (e.g., Hexabunus, Hernandarioides Pickard-Cambridge, 1905).
Only those species described, registered, or modified after 2003 are provided with a detailed logonymy here. For the remaining species, refer to the catalog by
Infraorder Grassatores Kury, 2002
Incertae sedis
Cleombrotus minutus Sørensen, 1932
Distribution. Unknown department.
Philacarus samoides Sørensen, 1932
Distribution. Unknown department. Originally cited from Ecuador, but
Remarks. Nueva Granada was a historical region of northern South America. The Viceroyalty of New Granada (1717–1723, 1739–1810, 1815–1822) was a political and administrative entity established by Spain in the 18th century that encompassed a large part of the Andean region of South America, including present-day Colombia, Ecuador, Panama, and Venezuela. It was governed by a viceroy appointed by the Spanish crown. After gaining independence from Spain in 1819, the Republic of New Granada (1831–1858) was established as a sovereign state in the northern Andean region of South America, encompassing present-day mainly Colombia and Panama. The republic underwent various changes in its name and territorial boundaries.
Agoristenidae Šilhavý, 1973
Andrescava sturmi Roewer, 1963
Distribution. Huila. Magdalena Valley dry forests (NT0221).
Avima scabra (Roewer, 1963)
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Avima troglobia (Pinto-da-Rocha, 1996)
Trinella troglobia Pinto-da-Rocha, 1996: 321, figs 4, 8, 15, 16. —
Avima troglobia — Villarreal and Kury 2009: 3. —
Distribution. La Guajira. Cordillera Oriental montane forests (NT0118).
Remarks. The type locality for this species is the state of Zulia, in Venezuela. It was recorded from Colombia by
Avima tuttifrutti García & Pastrana-M, 2021
Avima tuttifrutti García & Pastrana-M, 2021: 2, figs 1–4.
Distribution. Córdoba. Northern Andean montane forest (NT0145).
Avima venezuelica Soares & Avram, 1981
Avima venezuelica Soares & Avram, 1981: 95. — Villarreal and Kury 2009: 67. —
Vima venezuelica — González-Sponga 1987: 543, figs 708–713.
Trinella venezuelica — Pinto-da-Rocha 1996: 323. —
Distribution. La Guajira. Cordillera Oriental montane forests (NT0118).
Remarks. The type locality for this species is the state of Zulia, in Venezuela. It was recorded from Colombia by
Avima wayuunaiki García, Vargas & Gutiérrez, 2022
Avima wayuunaiki
Distribution. La Guajira. Guajira-Barranquilla xeric scrub (NT1308).
Barinas guanenta García & Ahumada-C., 2022
Barinas guanenta García & Ahumada-C., 2022: 3, figs 1, 2, 4.
Distribution. Santander. Magdalena Valley montane forests (NT0136).
Barinas piragua Ahumada-C. & García, 2020
Barinas piragua Ahumada-C. & García in
Distribution. Bolívar, La Guajira, Magdalena. Magdalena-Urabá moist forests (NT0137), Guajira-Barranquilla xeric scrub (NT1308), and Amazon-Orinoco-Southern Caribbean mangroves (NT1401).
Leptostygnus leptochirus Mello-Leitão, 1940
Leptostygnus leptochirus Mello-Leitão, 1940: 306. — Soares 1945: 383. — Soares et al. 1992: 7. — Kury 1993: 129, figs 1–6. —
Distribution. Norte de Santander. Catatumbo moist forests (NT0108).
Leptostygnus yarigui García & Villarreal, 2020
Leptostygnus yarigui García & Villarreal, 2020: 7, figs 3–6, 8, 9.
Distribution. Santander. Magdalena Valley montane forests (NT0136).
Muscopilio onod Villarreal & García, 2021
Muscopilio onod Villarreal & García, 2021: 157, figs 1–10.
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Nemastygnus ovalis Roewer, 1929
Nemastygnus ovalis Roewer, 1929: 277, fig. 44. —
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Paravima lokura García & Villarreal, 2023
Paravima lokura García & Villarreal, 2023: 420, figs 5, 6, 18.
Distribution. Norte de Santander. Cordillera Oriental montane forests (NT0118).
Paravima magistri García & Villarreal, 2023
Paravima magistri García & Villarreal, 2023: 424, figs 7, 8, 18, 19G.
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Sabanilla ornata Roewer, 1913
Distribution. Atlántico. Guajira-Barranquilla xeric scrub (NT1308).
Vima panita García & Kury, 2020
Vima panita García & Kury, 2020: 71, figs 5–8.
Distribution. Caquetá. Napo moist forests (NT0142)
Ampycella fortunata sp. nov.
Distribution. Valle del Cauca. Chocó-Darién moist forests (NT0115).
Ampycus telifer (Butler, 1873)
Gonyleptes telifer Butler, 1873: 116, figs 3, 4.
Itequahy ensiferus Mello-Leitão, 1949: 29, fig. 9.
Ampycus telifer — Simon 1879: 241. — Roewer 1913: 49, fig. 18; 1923: 411, fig. 506. — Mello-Leitão 1923: 117; 1932: 208, fig. 119. — Goodnight and Goodnight 1943: 10. — Soares and Soares 1954: 234. —
Distribution. Amazonas. Solimões-Japurá moist forests (NT0163).
Remarks. The type locality of this species is in the state of Amazonas, in Brazil. It was recorded for Colombia by
Licornus tama Villarreal & Kury, 2012
Licornus tama Villarreal & Kury, 2012: 73, figs 1–19. —
Distribution. Meta. Apure-Villavicencio dry forests (NT0201).
Remarks. The type locality for this species is the state of Táchira, in Venezuela. Recorded for Colombia by
Thaumatocranaus magnificus Hara, Bragagnolo & Pinto-da-Rocha, 2017
Thaumatocranaus magnificus
Distribution. Amazonas. Caqueta moist forests (NT0107).
Thaumatocranaus splendidus Hara, Bragagnolo & Pinto-da-Rocha, 2017
Thaumatocranaus splendidus
Distribution. Amazonas. Solimões-Japurá moist forests (NT0163).
Cosmetus acanti Medrano, Kury & Martínez, 2021
Cosmetus acanti
Distribution. Chocó. Chocó-Darién moist forests (NT0115).
Cosmetus villarreali Medrano, Kury & Martínez, 2021
Cosmetus villarreali
Distribution. Chocó. Chocó-Darién moist forests (NT0115).
Cynorta calcarapicalis Roewer, 1912
Distribution. Bolívar (type locality) and Cundinamarca. Sinú Valley dry forests (NT0229) and Magdalena Valley montane forests (NT0136).
Cynorta clavipus Roewer, 1928
Distribution. Unknown department.
Cynorta clunipecten Roewer, 1947
Distribution. Unknown department.
Remarks.
Cynorta dariensis Roewer, 1925
Distribution. Chocó. Chocó-Darién moist forests (NT0115).
Cynorta lateralis Roewer, 1928
Distribution. Chocó. Chocó-Darién moist forests (NT0115).
Cynorta maculorum Goodnight & Goodnight, 1943
Distribution. Unknown department.
Cynorta rorida Roewer, 1928
Distribution. Chocó. Chocó-Darién moist forests (NT0115).
Cynorta simplex Roewer, 1928
Distribution. Unknown department.
Cynortellina lineata Roewer, 1915
Distribution. Tolima (without a specific locality).
Cynortosoma reticulatum Roewer, 1947
Distribution. Tolima (without a specific locality).
Erginulus australis (Roewer, 1916)
Distribution. Unknown department.
Eucynorta quadripustulata (Simon, 1879)
Cynorta quadripustulata Simon, 1879: 196.
Eucynorta quadripustulata — Roewer 1912: 55. —
Distribution. Atlántico, Bolívar, Cesar, La Guajira, Magdalena. Amazon-Orinoco-Southern Caribbean mangroves (NT1401), Guajira-Barranquilla xeric scrub (NT1308), Magdalena-Urabá moist forests (NT0137), Cordillera Oriental montane forests (NT0118) and Sinú Valley dry forests (NT0229).
Eucynorta venosa Roewer, 1928
Distribution. Chocó. Chocó-Darién moist forests (NT0115).
Eucynortella orbicularis Roewer, 1947
Distribution. Unknown department.
Remarks.
Eucynortula ypsilon Roewer, 1925
Distribution. Chocó. Chocó-Darién moist forests (NT0115).
Eulibitia castor Medrano & Kury, 2017
Eulibitia castor Medrano & Kury, 2017: 8, figs 5–7, 34.
Distribution. Boyacá. Cordillera Oriental montane forests (NT0118).
Eulibitia chacuamarei Pinzón, Damron & Pinto-da-Rocha, 2021
Eulibitia chacuamarei
Distribution. Casanare. Llanos (NT0709).
Eulibitia clytemnestra Medrano & Kury, 2017
Eulibitia clytemnestra Medrano & Kury, 2017: 12, figs 8–10, 33.
Distribution. Santander. Magdalena Valley montane forests (NT0136).
Eulibitia ectroxantha (Mello-Leitão, 1941)
Brachylibitia ectroxantha Mello-Leitão, 1941: 166, fig. 1.
Cynorta ectroxantha — Goodnight and Goodnight 1953: 38.
Platymessa ectroxantha — Medrano and Kury 2016: 57. — Tagged as species inquirenda.
Eulibitia ectroxantha —
Distribution. Boyacá. Northern Andean páramo (NT1006) and Magdalena Valley montane forests (NT0136).
Eulibitia helena Medrano & Kury, 2017
Eulibitia helena Medrano & Kury, 2017: 17, figs 11–14, 34.
Distribution. Norte de Santander. Cordillera Oriental montane forests (NT0118).
Eulibitia h-inscriptum (Mello-Leitão, 1941)
Platymessa h-inscripta Mello-Leitão, 1941: 167, fig. 2.
Platymessa nigrolimbata Mello-Leitão, 1941: 168, fig. 3. — B. Soares 1945: 344.
Cynorta h-inscripta — H. Soares 1970: 325.
Platymessa h-inscriptum — Kury and Alonso-Zarazaga 2011: 51. — Medrano and Kury 2016: 58, figs 1–29.
Eulibitia h-inscriptum —
Distribution. Boyacá and Santander. Magdalena Valley montane forests (NT0136) and Northern Andean páramo (NT1006).
Eulibitia leda Medrano & Kury, 2017
Eulibitia leda Medrano & Kury, 2017: 22, figs 15–18, 33.
Distribution. Santander. Magdalena Valley montane forests (NT0136).
Eulibitia maculata Roewer, 1912
Eulibitia maculata Roewer, 1912: 17, pl. 1, fig. 1. — Roewer 1923: 298, fig. 320. — Sørensen in Henriksen 1932: 389. — B. Soares 1945: 343. — Weidner 1959: 122. — Pinto-da-Rocha and Hara 2011: 2. —
Libitia (Messa) castanea Sørensen in Henriksen, 1932: 415.
Paramessa castanea — Mello-Leitão 1933: 109.
Messatana castanea — Strand 1942: 398.
Distribution. Boyacá, Cundinamarca, and Tolima. Northern Andean páramo (NT1006) and Magdalena Valley montane forests (NT0136).
Eulibitia pollux Medrano & Kury, 2017
Eulibitia pollux Medrano & Kury, 2017: 34, figs 23–26, 31B, 34.
Distribution. Boyacá. Magdalena Valley montane forests (NT0136).
Eulibitia scalaris (Sørensen, 1932)
Libitia (Messa) scalaris Sørensen in Henriksen, 1932: 414.
Acromares lateralis Goodnight & Goodnight, 1943: 2, fig. 7. —
Messa scalaris — Mello-Leitão 1933: 112.
Messatana scalaris — Strand 1942: 398.
Eulibitia scalaris — Kury and Medrano 2017: 40, figs 27–30, 31A, 33.
Cynorta lateralis — Goodnight and Goodnight 1953: 38.
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Eulibitia victoriae (Pinzón-M. & Townsend, 2017)
Platymessa victoriae
Eulibitia victoriae — Kury et al. 2020: 14.
Distribution. Cesar. Cordillera Oriental montane forests (NT0118).
Flirtea alpha (Sørensen, 1932)
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Flirtea fusca (Sørensen, 1932)
Distribution. Unknown department.
Flirtea granulosa (Simon, 1879)
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Flirtea limbata (Sørensen, 1932)
Distribution. Unknown department.
Flirtea militaris (Simon, 1879)
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Flirtea tuberculata (Sørensen, 1932)
Distribution. Unknown department.
Flirtea ventricosa (Simon, 1879)
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Libitia bipunctata Sørensen, 1932
Libitia (Libitia) bipunctata Sørensen in Henriksen, 1932: 417.
Libitia bipunctata — Mello-Leitão 1933: 109. —
Libitiella bipunctata — Roewer 1947: 8, pl. 1, fig. 3.
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136), Cordillera Oriental montane forests (NT0118) and Northern Andean páramo (NT1006).
Libitia cordata (Gervais, 1844)
Cosmetus cordatus Gervais, 1844: 117, pl. 46, fig. 9.
Libitia cordata — Butler 1873: 115. — Simon 1879: 216. — Roewer 1912: 12; 1923: 293. — Mello-Leitão 1923: 108; 1932: 53; 1933: 109. —
Libitia (Libitia) cordata — Sørensen in Henriksen 1932: 419.
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136) and Northern Andean páramo (NT1006).
Libitia gandalf Medrano, Ázara & Kury, 2020
Libitia gandalf
Distribution. Meta. Cordillera Oriental montane forests (NT0118).
Libitia iguaque Medrano, Ázara & Kury, 2020
Libitia iguaque
Distribution. Boyacá. Northern Andean páramo (NT1006).
Metacynorta bella Roewer, 1963
Distribution. Putumayo. Napo moist forests (NT0142).
Meterginus affinis Roewer, 1963
Distribution. Putumayo. Napo moist forests (NT0142).
Meterginus flavicinctus (Gervais, 1842)
Distribution. Cundinamarca. Magdalena Valley dry forests (NT0221) and Magdalena Valley montane forests (NT0136).
Meterginus marginellus (Simon, 1879)
Distribution. Unknown department.
Meterginus marmoratus (Roewer, 1912)
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Meterginus obscurus (Sørensen, 1932)
Distribution. Unknown department.
Meterginus prosopis Roewer, 1912
Distribution. Cundinamarca, Meta, and Tolima. Magdalena Valley montane forests (NT0136) and Cordillera Oriental montane forests (NT0118).
Meterginus simonis (With, 1932)
Rhaucus (Erginus) simonis With in Henriksen, 1932: 350.
Meterginus simonis — Mello-Leitão 1933: 110. —
Distribution. Unknown department.
Meterginus togatus (Sørensen, 1932)
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Paecilaema altaspinulatum Goodnight & Goodnight, 1943
Distribution. Unknown department.
Paecilaema atroluteum Roewer, 1912
Distribution. Atlántico. Guajira-Barranquilla xeric scrub (NT1308).
Paecilaema contextum Roewer, 1928
Distribution. Unknown department.
Paecilaema distinctum Roewer, 1915
Distribution. Atlántico. Guajira-Barranquilla xeric scrub (NT1308).
Paraprotus atroluteus Roewer, 1912
Distribution. Atlántico. Guajira-Barranquilla xeric scrub (NT1308).
Protus speciosus (Roewer, 1927)
Paraprotus speciosus Roewer, 1927: 628, pl. 1, fig. 11.
Protus speciosus —
Distribution. Amazonas. Solimões-Japurá moist forests (NT0163).
Remarks. The type locality for this species is Maranhão state, in Brazil. It was recorded for Colombia by
Rhaucoides nasa Medrano, García & Kury, 2022
Rhaucoides nasa
Distribution. Cauca. Magdalena Valley montane forests (NT0136).
Rhaucoides riveti Roewer, 1914
Rhaucoides riveti Roewer, 1914: 125, pl. 13, fig. 3. — Roewer 1923: 306, fig. 333.
Rhaucoides festae Roewer, 1925: 3, pl. 5, fig. 1. — Pararhauculus sulfureus Mello-Leitão, 1939: 171. — Established as a junior subjective synonym of Rhaucoides festae Roewer, 1925 by
Cumbalia octomaculata Roewer, 1963: 51, pl. 9, fig. 13.
Distribution. Nariño. Northwestern Andean montane forests (NT0145).
Rhaucus florezi García & Kury, 2017
Rhaucus florezi García & Kury, 2017: 426, figs 1e, 15–17, 18e, 23.
Distribution. Boyacá. Magdalena Valley montane forests (NT0136).
Rhaucus papilionaceus (Simon, 1879)
Erginus papilionaceus Simon, 1879: 205.
Flirtea papilionacea — Roewer 1912: 77. — Roewer 1923: 347. — Roewer 1927: 593. — Mello-Leitão 1932: 78.
Rhaucus (Erginus) papilionaceus — Henriksen 1932: 352.
Rhaucus papilionaceus —
Distribution. Santander. Magdalena Valley montane forests (NT0136).
Rhaucus quinquelineatus Simon, 1879
Rhaucus quinquelineatus Simon, 1879: 215. — Sørensen in Henriksen 1932: 358. —
Pararhaucus obscurus Pickard-Cambridge, 1905: 572. — Roewer 1912: 102. — Roewer 1923: 378.
Metarhaucus albilineatus Roewer, 1912: 147, pl. 7, figs 5, 6. —
Rhaucus (Rhaucus) muticus Sørensen, 1932: 360.
Rhaucus (Rhaucus) tristis — Sørensen 1932: 363, fig. 26.
Flirtea quinquelineata — Roewer 1912: 76. — Roewer 1923: 346, fig. 393. — Mello-Leitão 1923: 112. — Roewer 1927: 594. — Mello-Leitão 1932: 79, fig. 47. — B. Soares 1945: 343. — Roewer 1963: 58. —
Paecilaema obscurum — Goodnight and Goodnight 1953: 54. —
Flirtea mutica — Mello-Leitão 1933: 110.
Flirtea tristis — Mello-Leitão 1933: 110.
Distribution. Boyacá and Cundinamarca. Northern Andean páramo (NT1006), Magdalena Valley montane forests (NT0136) and Cordillera Oriental montane forests (NT0118).
Rhaucus robustus (Mello-Leitão, 1941)
Megarhaucus robustus Mello-Leitão, 1941: 169, fig. 4.
Rhaucus robustus — García & Kury, 2017: 422, figs 1c, 12–14, 18d, 23.
Distribution. Boyacá and Santander. Northern Andean páramo (NT1006) and Magdalena Valley montane forests (NT0136).
Rhaucus serripes (Simon, 1879)
Erginus serripes Simon, 1879: 204.
Metarhaucus fuscus Pickard-Cambridge, 1905: 572.
Metarhaucus reticulatus Roewer, 1912: 145, pl. 7, fig. 4.
Rhaucus (Rhaucus) geographicus Sørensen, 1932: 369.
Flirtea paucimaculata Roewer, 1963: 58, fig. 24. —
Flirtea serripes — Roewer 1912: 77; 1923: 348, figs 396–397; 1927: 593. — Mello-Leitão 1932: 78.
Rhaucus (Erginus) serripes — Henriksen in Sørensen 1932: 352.
Rhaucus serripes —
Erginus fuscus — Roewer, 1912: 68.
Metarhaucus fuscus — Roewer 1923: 342; 1927: 588.
Erginus reticulatus — Roewer 1912: 68.
Metarhaucus reticulatus — Roewer 1923: 343, fig. 387; 1927: 588; 1959: 80. — Forcart 1961: 51. —
Flirtea geographica — Mello-Leitão 1933: 110.
Distribution. Boyacá and Cundinamarca. Northwestern Andean montane forests (NT0145), Magdalena Valley montane forests (NT0136), Cordillera Oriental montane forests (NT0118) and Northern Andean páramo (NT1006).
Rhaucus vulneratus Simon, 1879
Rhaucus vulneratus Simon, 1879: 213. Pickard-Cambridge 1905: 572. — Roewer 1912: 78. — Roewer 1923: 349, fig. 400. — Mello-Leitão 1923: 113. — Mello-Leitão 1932: 57, fig. 23. — Mello-Leitão 1933: 110. —
Neorhaucus aurolineatus Pickard-Cambridge, 1905: 572.
Rhaucus (Rhaucus) vulneratus — Sørensen 1932: 355.
Raucus vulneratus — González-Sponga 1992: 427.
Neorhaucus aurolineatus — Roewer 1912: 25. — Roewer 1923: 305.
Distribution. Boyacá and Cundinamarca. Magdalena Valley montane forests (NT0136) and Northern Andean páramo (NT1006).
Sibambea cincta (Perty, 1833)
Discosoma cincta Perty, 1833: 209, pl. 40, fig. 6.
Discosomaticus sturmi Roewer, 1963: 58, fig. 25.
Sibambea cincta —
Distribution. Amazonas and Vaupés. Purus várzea (NT0156), Iquitos várzea (NT0128), Solimões-Japurá moist forests (NT0163) and Caqueta moist forests (NT0107).
Remarks. The type locality for this species is the state of Bahia, in Brazil. It was recorded for Colombia by
Taito insperatus (Soares, 1970)
Cynorta insperata Soares, 1970: 323, fig. 3. —
Taito insperatus —
Distribution. Amazonas. Purus várzea (NT0156).
Taito medinae Kury & Barros, 2014
Taito medinae Kury & Barros, 2014: 39, figs 1a, 17j–l, 26a–g, 35.
Distribution. Amazonas. Solimões-Japurá moist forests (NT0163).
Taito oblongatus (Roewer, 1928)
Cynortula oblongata Roewer, 1928: 576, fig. 28. — Mello-Leitão 1932: 58. —
Taito oblongatus —
Distribution. Meta. Cordillera Oriental montane forests (NT0118).
Zaraxolia devians (Sørensen, 1932)
Distribution. Unknown department.
Allocranaus columbianus Roewer, 1915
Distribution. Quindío. Magdalena Valley montane forests (NT0136).
Cranaus albipustulatus Roewer, 1943
Distribution. La Guajira. Guajira-Barranquilla xeric scrub (NT1308).
Cranaus chlorogaster (Gervais, 1844)
Distribution. Unknown department.
Cranaus cinnamomeus (Gervais, 1844)
Distribution. Unknown department.
Deriacrus simoni Roewer, 1932
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Holocranaus calcar (Roewer, 1912)
Distribution. Antioquia. Cauca Valley montane forests (NT0109) and Magdalena Valley montane forests (NT0136).
Holocranaus calus (Goodnight & Goodnight, 1944)
Distribution. Valle del Cauca. Cauca Valley montane forests (NT0109).
Holocranaus longipes Roewer, 1913
Holocranaus longipes Roewer, 1913: 400, fig. 158. — Roewer 1923: 556, fig. 695. — 1932: 293, fig. 9. — Soares and Soares 1948: 602.
Phareicranaus giganteus Roewer, 1932: 299. —
Distribution. Unknown department.
Remarks. The type locality for this species is the Aguacatal River, Colombia. The locality is not precise (
Holocranaus pectinitibialis (Roewer, 1914)
Tolimaius pectinitibialis Roewer, 1914: 125, figs 12–13. — Roewer 1923: 558, fig. 698.
Holocranaus pectinitibialis — Soares and Soares 1948: 603. —
Distribution. Tolima. Magdalena Valley montane forests (NT0136).
Holocranaus simplex Roewer, 1913
Distribution. Unknown department.
Homocranaus tetracalcar Roewer, 1915
Distribution. Quindío. Magdalena Valley montane forests (NT0136).
Isocranaus gorgonae Hirst, 1926
Distribution. Nariño. Chocó-Darién moist forests (NT0115).
Isocranaus obscurus Roewer, 1915
Distribution. Meta. Apure-Villavicencio dry forests (NT0201).
Megacranaus areolatus Roewer, 1932
Distribution. Tolima.
Megacranaus pygoplus Roewer, 1913
Distribution. Antioquia. Northern Andean páramo (NT1006).
Metacranaus tricalcaris Roewer, 1913
Distribution. Antioquia. Cauca Valley montane forests (NT0109).
Neocranaus albiconspersus Roewer, 1913
Distribution. Maracaibo (without further specific locality data).
Remark. Several localities are called Maracaibo in Colombia and Venezuela.
Neocranaus armatissimus (Mello-Leitão, 1941)
Mitobatulina armatissima Mello-Leitão, 1941: 170, fig. 5. — Soares and Soares 1949: 235.
Neocranaus armatissimus —
Distribution. Nariño, Napo moist forests (NT0142).
Panalus robustus Goodnight & Goodnight, 1947
Distribution. Cauca. Cauca Valley montane forests (NT0109).
Paracranaus crassipalpis Roewer, 1913
Distribution. Atlántico. Guajira-Barranquilla xeric scrub (NT1308).
Peripa simplex Roewer, 1932
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Phalangodus anacosmetus Gervais, 1842
Phalangodus anacosmetus Gervais, 1842: 3, pl. 4; 1844: 114, pl. 46, fig. 3. — Erichson 1845: 267. — Thorell 1877: 115. — Simon 1879: 241. — Roewer 1913: 138, fig. 63. — 1923: 446, fig. 562. — Kästner 1937: 300, fig. 364. — Soares and Soares 1954: 289. — Kury 1996: 178, figs 1–4. — Acosta 1996: 224. —
Allocranaus giganteus Mello-Leitão, 1940: 307, fig. 8. —.B. Soares 1945: 349. — Soares and Soares 1948: 587.
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Phalangodus briareos Villarreal & García, 2016
Phalangodus briareos Villarreal & García, 2016: 9, figs 4–6, 7a–d, 18, 19. —
Distribution. Santander. Magdalena Valley montane forests (NT0136).
Phalangodus andresi sp. nov.
Distribution. Cundinamarca. Chocó-Darién Moist Forests (NT0115).
Phalangodus cottus Villarreal & García, 2016
Phalangodus cottus Villarreal & García, 2016: 15, figs 8a, b, 9, 10, 18.
Distribution. Meta. Apure-Villavicencio dry forests (NT0201).
Phalangodus gyes Villarreal & García, 2016
Phalangodus gyes Villarreal & García, 2016: 21, figs 7e–f, 8c–d, 11, 12, 18.
Distribution. Tolima. Magdalena Valley montane forests (NT0136).
Phalangodus kuryi Villarreal & García, 2016
Phalangodus kuryi Villarreal & García, 2016: 25, figs 13–15, 18.
Distribution. Magdalena. Guajira-Barranquilla xeric scrub (NT 1308).
Phareicranaus albigranulatus Roewer, 1913
Phareicranaus albigranulatus Roewer, 1913: 404, fig. 160. —
Distribution. Tolima. Magdalena Valley montane forests (NT0136).
Remarks.
Phareicranaus albigyratus Roewer, 1932
Phareicranaus albigyratus Roewer, 1932: 303. —
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Phareicranaus angelicus (Roewer, 1963)
Santinezia angelica Roewer, 1963: 69. — Pinto-da-Rocha and
Phareicranaus angelicus —
Distribution. Meta. Cordillera Oriental montane forests (NT0118).
Phareicranaus spinulatus (Goodnight & Goodnight, 1943)
Santinezia spinulata Goodnight & Goodnight, 1943: 9, figs 26–28. — Pinto-da-Rocha and
Phareicranaus spinulatus —
Distribution. Unknown department.
Sibundoxia scripta Roewer, 1963
Distribution. Putumayo. Eastern Cordillera real montane forests (NT0121).
Stygnicranaus alessandroi Orrico & Kury, 2009
Stygnicranaus alessandroi Orrico & Kury, 2009: 474, figs 2–5.
Distribution. Valle del Cauca. Cauca Valley montane forests (NT0109).
Stygnicranaus poncedeleoni Orrico & Kury, 2009
Stygnicranaus poncedeleoni Orrico & Kury, 2009: 476, figs 6–11.
Distribution. Valle del Cauca. Northwestern Andean montane forests (NT0146).
Tetracranaus zilchi Roewer, 1963
Distribution. Valle del Cauca. Northwestern Andean montane forests (NT0146) and Magdalena Valley montane forests (NT0136).
Ventrifurca albipustulata Roewer, 1913
Ventrifurca albipustulata Roewer, 1913: 383, figs 149–150. —
Microcranaus pustulatus Roewer, 1913: 353, fig. 137. —
Cayabeus perlatus Roewer, 1932: 337, fig. 53. —
Distribution. Antioquia. Cauca Valley montane forests (NT0109).
Ventrifurca caffeinica Villarreal, Kury & Pinto-da-Rocha, 2015
Ventrifurca caffeinica
Distribution. Quindío. Cauca Valley montane forests (NT0109).
Ventrifurca dybasi (Goodnight & Goodnight, 1947)
Rhopalocranaus dybasi Goodnight & Goodnight, 1947: 40, fig. 20.
Neocranaus dybasi —
Ventrifurca dybasi —
Distribution. Valle del Cauca. Cauca Valley montane forests (NT0109).
Remarks. Generic assignment from Neocranaus by
Ventrifurca phallaina sp. nov.
Distribution. Valle del Cauca. Chocó-Darién moist forests (NT0115).
Ventrisudis mira Roewer, 1963
Distribution. Huila. Patía Valley dry forests (NT0225).
Camelianus fuhrmanni Roewer, 1912
Distribution. Antioquia. Cauca Valley montane forests (NT0109) and Magdalena Valley montane forests (NT0136).
Cucutacola nigra Mello-Leitão, 1940
Distribution. Norte de Santander. Catatumbo moist forests (NT0108).
Gonogotus areolatus Roewer, 1943
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Rhopalocranaus apiculatus Roewer, 1932
Distribution. Unknown department.
Rhopalocranaus atroluteus Roewer, 1913
Distribution. Tolima. Magdalena Valley montane forests (NT0136).
Rhopalocranaus columbianus (Roewer, 1963)
Microcranaus columbianus Roewer, 1963: 64, figs 34, 35.
Rhoplocranaus columbianus —
Distribution. Cauca. Patía Valley dry forests (NT0225).
Rhopalocranaus ypsilon Roewer, 1913
Distribution. Tolima. Magdalena Valley montane forests (NT0136).
Semostrus tarsalis Roewer, 1943
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Callcosma barasana Pinto-da-Rocha & Bragagnolo, 2017
Callcosma barasana Pinto-da-Rocha & Bragagnolo, 2017: 103, figs 4B, 8B, 10B, 13A, B.
Distribution.Vaupés. Caqueta moist forests (NT0107).
Callcosma gracillima Roewer, 1932
Callcosma gracillima Roewer, 1932: 331, fig. 47. — Soares and Soares 1948: 591. —
Distribution. Amazonas. Solimões-Japurá moist forests (NT0163).
Nomoclastes quasimodo Pinto-da-Rocha, 1997
Nomoclastes quasimodo Pinto-da-Rocha, 1997: 171, figs 1–6, 449, 450, 587, 592, 596. –
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Nomoclastes taedifer Sørensen, 1932
Nomoclastes taedifer Sørensen, 1932: 300, fig. 11. — Roewer 1943: 36. — Pinto-da-Rocha 1997: 171, figs 7, 8. —
Distribution. Department unknown.
Paraphalangodus synacanthus Roewer, 1915, new family assignment
Distribution. Tolima (without a specific locality).
Remark. The type locality for this species refers to Páramo del Tolima, located in the department of Tolima, which comprises four páramo complexes, namely Las Hermosas, Chilí Barragán, Nevado del Huila-Moras, and Los Nevados. Therefore, the specific location within the Tolima department cannot be determined without further information. Originally described as Gonyleptidae,
Quindina bella Roewer, 1915
Quindina bella Roewer, 1915: 128, fig. 14. — Roewer 1923: 564, fig. 707. — Soares and Soares 1948: 615. —
Distribution. Tolima. Magdalena Valley montane forests (NT0136).
Quindina discolor Pinzón & Pinto-da-Rocha, 2020
Quindina discolor Pinzón & Pinto-da-Rocha, 2020: 542, figs 3, 4.
Distribution. Magdalena. Santa Marta montane forests (NT0159).
Quindina hermesi Pinzón & Pinto-da-Rocha, 2020
Quindina hermesi Pinzón & Pinto-da-Rocha, 2020: 537, figs 1, 2.
Distribution. Atlántico, Bolívar. Magdalena-Urabá moist forests (NT0137) and Guajira-Barranquilla xeric scrub (NT 1308).
Quindina marginata (Roewer, 1963)
Deriacrus marginatus Roewer, 1963: 68, fig. 42. —
Quindina marginata —
Distribution. Huila. Magdalena Valley montane forests (NT0136).
Eutimesius ephippiatus (Roewer, 1915)
Distribution. Quindío. Magdalena Valley montane forests (NT0136).
Eutimesius ornatus (Roewer, 1943)
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Eutimesius simoni Roewer, 1913
Distribution. Putumayo. Napo moist forests (NT0142).
Fortia jedi Villarreal, Kury & Colmenares, 2022
Fortia jedi
Distribution. Magdalena. Santa Marta montane forests (NT0159).
Fortia sith Villarreal, Kury & Colmenares, 2022
Fortia sith
Distribution. Magdalena. Santa Marta montane forests (NT0159).
Jabbastygnus huttorum Kury & Villarreal, 2015
Jabbastygnus huttorum Kury & Villarreal, 2015: 32, figs 4D–F, 17–19.
Distribution. Boyacá. Magdalena Valley montane forests (NT0136).
Metaphareus albimanus Roewer, 1912
Distribution. Tolima. Magdalena Valley montane forests (NT0136).
Niceforoielus assimilis Mello-Leitão, 1941
Distribution. Norte de Santander. Catatumbo moist forests (NT0108).
Obidosus carnaval (Villarreal-Manzanilla & Pinto-da-Rocha, 2006)
Protimesius carnaval Villarreal-Manzanilla & Pinto-da-Rocha, 2006: 229, figs. 29–35, 44, 45.
Obidosus carnaval — Villarreal et al. 2019: 229, figs 29–35, 44, 45.
Distribution. Amazonas. Solimões-Japurá moist forests (NT0163).
Remarks. The type locality for this species is Moa River in the state of Acre, in Brazil. It was recorded for Colombia by Villarreal-M. and Pinto-da-Rocha (2006).
Phareus antrophilus Villarreal & Rodríguez, 2006
Phareus antrophilus Villarreal & Rodríguez, 2006: 103, figs 1–9.
Distribution. Santander. Magdalena Valley montane forests (NT0136).
Phareus raptator (Gervais, 1844)
Goniosoma raptator Gervais, 1844: 107 (vol. 3), pl. 47, figs 1, 1a.
Liophareus mamillatus Mello-Leitão, 1940: 309, fig. 10. — B. Soares 1945: 386.
Colomphareus rugosus Goodnight & Goodnight, 1943: 10, figs 32–35. —
Allophareus robustus Roewer, 1963: 60, figs 26–28. —
Phareus raptator — Simon 1879: 219. — Roewer 1912: 149. — 1913: 155, figs 68, 69. — 1923: 457, figs 475, 476. —
Distribution. Cundinamarca. Cordillera Oriental montane forests (NT0118), Magdalena Valley montane forests (NT0136) and Northern Andean páramo (NT1006).
Stygnus gertschi (Roewer, 1963)
Distribution. Cauca. Patía Valley dry forests (NT0225).
Stygnus pectinipes (Roewer, 1943)
Distribution. Putumayo. Napo moist forests (NT0142).
Stygnus simplex (Roewer, 1913)
Distribution. Putumayo. Napo moist forests (NT0142).
Timesius vesicularis (Gervais, 1844)
Distribution. Department unknown.
Stygnommatidae Roewer, 1923
Stygnomma fuhrmanni Roewer, 1912
Distribution. Antioquia. Cauca Valley montane forests (NT0109).
Incertae sedis
Hevelia crucis Kury, García & Ahumada-C., 2023
Hevelia crucis
Distribution. Bolívar. Magdalena-Urabá moist forests (NT0137).
Fissiphallius spinulatus Martens, 1988
Distribution. Cundinamarca. Northern Andean paramo (NT1006).
Fissiphallius sturmi Martens, 1988
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Fissiphallius sympatricus Martens, 1988
Distribution. Cundinamarca. Magdalena Valley montane forests (NT0136).
Icaleptes malkini Kury & Pérez, 2002
Distribution. Cesar. Santa Marta montane forests (NT0159).
Usatama infumatus Kury, García & Medrano, 2019
Usatama Kury, García, and Medrano 2019: 239, figs 1–4.
Distribution. Cundinamarca. Cordillera Oriental montane forests (NT0118).
Minuides oedipus Roewer, 1963
Minuides oedipus Roewer, 1963: 48, figs 6–8; — Šilhavý 1978: 62. —
Distribution. Huila. Magdalena Valley dry forests (NT0221).
Remarks. Minuides oedipus Roewer, 1963 treated as a Kimulidae in Kury´s catalogue (
Stygnoleptes analis Banks, 1913
Distribution. Department unknown.
Stygnoleptes crassus (Sørensen, 1932)
Distribution. Department unknown.
Timoleon crassipes Sørensen, 1932
Distribution. Department unknown.
Two species, Cosmetus flavopictus Simon, 1880 and Stygnoplus forcipatus have traditionally been associated with the list of Colombian species, which we do not consider in our list. Cosmetus flavopictus was described for a locality in Darien, extrapolated by
The Colombian opilionofauna of the suborder Laniatores is composed of 173 species, three of which are described in the present work. The 12 families listed in Colombia demonstrate the country’s high taxonomic diversity for this group. The most diverse family is Cosmetidae with 67 species (Fig.
Selected Colombian harvestmen species, live specimens A Barinas piragua (Agoristenidae) from Bolívar B Eucynorta quadripustulata (Cosmetidae) from Bolívar C Phalangodus cottus (Cranaidae) from Cundinamarca D Phareicranaus sp. (Cranaidae) from Chocó E Ampycus telifer (Ampycidae) from Amazonas F Quindina hermesi (Nomoclastidae) from Bolívar G Stygnomma sp. (Stygnommatidae) from Tolima. Photographs by: Hugo Vides (A, B, F); Andrés García (C); Sarah Crews (D); Arthur Anker (E); Julio González / Entomopixel (G).
Laniatores species described from Colombia A the pie chart shows authors who described two or more species. For each author, every described species was counted, regardless of whether the authorship of the species is shared with other authors. For example, Usatama infumatus was described by Kury, García & Medrano, 2019, and was counted as a species for each author. Authors with one species are included in the others category B accumulation curve of Laniatores species described from Colombia. Pink: descriptions made between 1833 and 1911; ochre: 1912–1963; green: 1964–2023 C Laniatores species in RUNAP D families of Laniatores species described from Colombia.
Most records come from a few departments, indicating a sampling bias. Approximately 22% of the species are known from the department of Cundinamarca (38 spp.) near the capital of the country, followed by Tolima and Boyacá with 13 species each. In contrast, all six departments of the Amazon region have a combined total of only 15 recorded species. This exemplifies the limited knowledge we have on the diversity of harvestmen in the Colombian Amazon region. Of the 173 species of Laniatores known in Colombia, 35 are recorded without a specific locality; 28 of which have no information other than their presence in Colombia, and only seven have been located at a specific department (Table
Number of Opiliones species by family recorded in WWF terrestrial ecoregions from Colombia. When the locality is unknown or not precise enough, the abbreviation DNA is used, and the record is not assigned to any ecoregion. DNA = does not apply.
WWF Ecoregion | Code (WWF) | Families | Species |
---|---|---|---|
Magdalena Valley montane forests | NT0136 | Agoristenidae | 6 |
Cosmetidae | 25 | ||
Cranaidae | 12 | ||
Fissiphalliidae | 2 | ||
Manaosbiidae | 5 | ||
Nomoclastidae | 4 | ||
Stygnidae | 6 | ||
Cordillera Oriental montane forests | NT0118 | Agoristenidae | 4 |
Cosmetidae | 10 | ||
Cranaidae | 1 | ||
Kimulidae | 1 | ||
Stygnidae | 1 | ||
Northern Andean páramo | NT1006 | Cosmetidae | 10 |
Cranaidae | 1 | ||
Fissiphalliidae | 1 | ||
Stygnidae | 1 | ||
Cauca Valley montane forests | NT0109 | Cranaidae | 9 |
Manaosbiidae | 1 | ||
Stygnommatidae | 1 | ||
Guajira-Barranquilla xeric scrub | NT1308 | Agoristenidae | 3 |
Cosmetidae | 4 | ||
Cranaidae | 3 | ||
Nomoclastidae | 1 | ||
Chocó-Darién moist forests | NT0115 | Cosmetidae | 7 |
Cranaidae | 2 | ||
Ampycidae | 1 | ||
Napo moist forests | NT0142 | Agoristenidae | 1 |
Cosmetidae | 2 | ||
Cranaidae | 1 | ||
Stygnidae | 3 | ||
Solimões-Japurá moist forests | NT0163 | Cosmetidae | 3 |
Ampycidae | 2 | ||
Nomoclastidae | 1 | ||
Stygnidae | 1 | ||
Santa Marta montane forests | NT0159 | Agoristenidae | 1 |
Icaleptidae | 1 | ||
Nomoclastidae | 1 | ||
Stygnidae | 2 | ||
Magdalena Valley dry forests | NT0221 | Agoristenidae | 1 |
Cosmetidae | 1 | ||
Cranaidae | 2 | ||
Zalmoxidae | 1 | ||
Northwestern Andean montane forests | NT0145 | Cosmetidae | 1 |
Cranaidae | 2 | ||
Apure-Villavicencio dry forests | NT0201 | Cranaidae | 2 |
Ampycidae | 1 | ||
Patía Valley dry forests | NT0225 | Cranaidae | 1 |
Manaosbiidae | 1 | ||
Stygnidae | 1 | ||
Catatumbo moist forests | NT0108 | Agoristenidae | 1 |
Manaosbiidae | 1 | ||
Stygnidae | 1 | ||
Magdalena-Urabá moist forests | NT0137 | Agoristenidae | 1 |
Cosmetidae | 1 | ||
Incertae sedis | 1 | ||
Nomoclastidae | 1 | ||
Sinú Valley dry forests | NT0229 | Cosmetidae | 2 |
Amazon-Orinoco-Southern Caribbean mangroves | NT1401 | Agoristenidae | 1 |
Cosmetidae | 1 | ||
Caqueta moist forests | NT0107 | Cosmetidae | 1 |
Ampycidae | 1 | ||
Nomoclastidae | 1 | ||
Purus várzea | NT0156 | Cosmetidae | 2 |
Eastern Cordillera real montane forests | NT0121 | Cranaidae | 1 |
Iquitos várzea | NT0128 | Cosmetidae | 1 |
Llanos | NT0709 | Cosmetidae | 1 |
Unknown Locality | DNA | Cosmetidae | 21 |
Cranaidae | 6 | ||
Manaosbiidae | 1 | ||
Nomoclastidae | 1 | ||
Stygnidae | 1 | ||
Zalmoxidae | 3 |
Geographical distribution of A Gonyleptoidea (Ampycidae, Manaosbiidae, Nomoclastidae and Stygnidae) and B Samooidea (Kimulidae, Stygnommatidae) and Zalmoxoidea (Icaleptidae, Fissiphalliidae, Zalmoxidae) in Colombia. Colored polygons follow the regionalization of the Neotropical region proposed by WWF (
The Colombian NSPA lists 1,486 protected zones, of which 60 are NNP and FFS. The remaining areas are designated with some other category of protection (
Similar to other neotropical countries, the taxonomic knowledge of harvestmen in Colombia is primarily based on the contributions of foreign authors. Remarkably Carl F. Roewer described almost half of the species known of the country. Therefore, for a pragmatic approach we divided the history into three periods: the first period prior to Roewer´s contributions, the second period in which most of the descriptions took place, led by Roewer’s works but with contributions from other authors, and finally, the third, post-Roewerian or modern period, with contributions from a diverse group of authors, including local authors for the first time. Our goal is not to present a detailed chronology, but rather to provide a general overview of the historical panorama and the individual contribution of the authors to the knowledge of the Colombian fauna. For a detailed chronicle and an in-depth look at the early history of opilionology, we recommend referring to
Colombia is recognized as a megadiverse country, renowned for its numerous protected natural areas compared to other neotropical countries. Despite ongoing conservation efforts, there is a need to increase the knowledge on biodiversity in these areas to support their proper management and handling. Unhappily, the information available on Laniatores in these areas is still limited, despite the growing number of arachnologists in the region and the country, and the increasing research focus on local fauna (Fig.
The central and eastern cordillera are the most populated and accessible areas of Colombia. They are home to the largest universities and biological collections in the country and, consequently, the region with the highest number of descriptions and records of Laniatores (Figs
In contrast, the peripheral zones, like the Amazon, the Pacific, or the Caribbean, have received less attention from researchers. Nevertheless, recent efforts have been made to strengthen research in these regions. For instance, a school of arachnology at the Universidad del Valle, has emerged to study the Laniatores of Valle del Cauca in the Pacific region. Similarly, in the Caribbean, harvestmen have been the focus of some degree work, and recent collections have yielded specimens that have been added to the country’s biological collections, resulting in the descriptions of new species and new records (e.g.,
Therefore, we believe that although the national inventory of Laniatores is far from being complete, further work on the local fauna will increase our knowledge of the group over time. Regarding the Colombian protected areas, the RNSC is the area with the lowest number of records of Laniatores (one species), while RDIM presents the highest number of records (16 species), probably because it is the only protected area in the country conceived as a rational use mode (
Geographical distribution of the families A Cosmetidae and B Cranaidae in Colombia. Colored polygons represent the RUNAP areas. Civil Society Nature Reserve (CSNR), Flora and Fauna Sanctuary (FFS), National Protective Forest Reserve (NPFR), Regional Natural Park (RNP), Regional Protective Forest Reserve (RPFR), National Natural Parks (NNP), Regional Integrated Management Districts (RDIM).
Geographical distribution of A the superfamilies Gonyleptoidea (Agoristenidae, Ampycidae, Manaosbiidae, Nomoclastidae and Stygnidae) and B Samooidea (Kimulidae, Stygnommatidae) and Zalmoxoidea (Icaleptidae, Fissiphalliidae, Zalmoxidae) in Colombia. Colored polygons represent the RUNAP areas. Flora and Fauna Sanctuary (FFS), National Protective Forest Reserve (NPFR), National Natural Parks (NNP), Regional Integrated Management Districts (RDIM).
Continued exploration of ecosystems is imperative to search for Opiliones and achieve reliable taxonomic identifications, which are essential to determine the true distribution of the species. Such data is important in establishing their threat category, according whit the criteria from the International Union for Conservation of Nature (IUCN). This should be a goal for arachnology, given the high endemicity exhibited by these organisms and the significant anthropogenic pressures to which they are exposed.
Phalangodus is an Andean cranaid genus whose species could be considered examples of short-range endemism, as defined by
Phalangodus andresi sp. nov. possesses all generic diagnostic characters presented by
Moreover, the family Ampycidae is known to have a little-explored diversity, primarily in Ecuador and Colombia. However, the taxonomic assignment of new species is a challenge for taxonomists due to the paucity of old descriptions and poor generic diagnosis. In addition, many species exhibit similar external morphology, and for more species, genitalia remain unknown, with just some exceptions (e.g.,
To Eduardo Flórez, Daniela Martínez and Sebastian Galvis for their collaboration during the visit by DAC and OV to the arachnological collection of
The authors have declared that no competing interests exist.
No ethical statement was reported.
This study has been partly supported by the Vice-Rector’s Office for Research of the Universidad del Quindío for LDS through the founding of the publication costs. Idea Wild funded photographic equipment for OV in the framework of the project ID. VILLVENE0122. Universidad de Cartagena funded the DAC’s visit to
OVM conceived the project, structured an initial draft of the manuscript, identified the new species, and contributed to their description and illustration, as well as with the list of species. DAC participated in the identification of the species, elaboration of the descriptions and illustrations, worked on the list of species, and collaborated significantly in the final writing of the manuscript. LDS collected two of the new species, participated in the identification of the species, contributed to the imaging, coordinated the making of the maps, and contributed to the overall writing of the manuscript. All authors contributed equally by writing results and discussion and agreed with the final version of the manuscript.
Osvaldo Villarreal https://orcid.org/0000-0001-5355-3723
Daniela Ahumada-C. https://orcid.org/0000-0002-4182-5143
Leonardo Delgado-Santa https://orcid.org/0000-0002-9714-6924
All of the data that support the findings of this study are available in the main text or Supplementary Information.
List of Laniatores species for Colombia
Data type: xlsx
Explanation note: List of Laniatores species for Colombia, with their registration source, distribution associated with WWF biogeographic ecoregions and their presence in protected areas, National System of Protected Areas.