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An Ultimate Ungulate Fact Sheet: Discover the ungulates of the world!
 Hippocamelus bisulcus
 Patagonian huemul, South Andean huemul

Taxonomy | Description | Reproduction | Ecology | Behavior | Distribution | Conservation | Remarks | Literature

Taxonomy
Classification
 

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Suborder :
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Genus :

Animalia
Chordata
Mammalia
Cetartiodactyla
Ruminantia
Cervidae
Capreolinae
Odocoileini
Hippocamelus

Hippocamelus bisulcus [Molina, 1782].
Citation: Sagg. Stor. Nat. Chile, p. 320.
Type locality: Chilean Andes, Colchagua Prov.

The taxonomic record (above) is taken from Wilson and Reeder (1993).  No subspecies are recognized for the Patagonian huemul, although regional differences have been noted by various authors (e.g., Frid, 1994).  Although closely related to the taruca or North Andean huemul (H. antisensis), the two are consistently recognized as separate species (Geist, 1998).  Invalid synonyms for Hippocamelus bisulcus include andicus, cerasina, chilensis, dubius, equinus, huemel, and leucotis (Wilson and Reeder, 1993).

Click on the pictures above for a larger view of the photographs

General Characteristics

The Patagonian huemul is the largest herbivore of the South Andean region (MacNamara, 1990).  It is a stout deer, similar in form to many mountain-dwelling members of the Caprinae (Redford and Eisenberg, 1992).  Males are larger and heavier than females, notably around their neck (Redford and Eisenberg, 1992; Diaz, 2000).  Reported body weights for this species fall primarily between 70 and 100 kg, and head and body length is approximately 150 cm.  This species is larger and darker in coloration than its northern counterpart, the taruca (H. antisensis) (MacNamara, 1990; Geist, 1998).

Reported measurements for Patagonian huemul (Hippocamelus bisulcus)

Source                   Adult Weight   Head & Body Length    Shoulder Height     Tail Length 
Diaz, 2000

-

163 cm
151 cm

90 cm
81 cm

13 cm

MacNamara, 1990

45-65 kg

150-170 cm

91 cm

11.5-13 cm

Nowak, 1991
for Hippocamelus

45-65 kg

140-165 cm

77.5-90 cm

11.5-3 cm [sic]

Redford and Eisenberg, 1992

70.0 kg

149.7 cm

80.0-90.0 cm

12-13 cm

Smith-Flueck, 2000

100 kg

140-175 cm
140-157 cm

79-100 cm
78-84 cm

-

Whitehead, 1993

70-100 kg

-

80-90 cm

-

The dense, coarse pelage of H. bisulcus is a uniform dark brown, varying in summer from dark rust to deep coffee in color (MacNamara, 1990; Redford and Eisenberg, 1992; Geist, 1998; Diaz, 2000).  The winter coat is paler, with a yellow or grey tint (Redford and Eisenberg, 1992; Smith-Flueck, 2000).  The undersides, especially the anal and inguinal regions, are whitish, contrasting sharply with the dark upper coat (MacNamara, 1990; Diaz, 2000).  There is no lightly-colored rump or throat patch as seen in H. antisensis, but a darker spot is often present on the hindquarters (MacNamara, 1990; Geist, 1998).  The tail is short with a white underside (Diaz, 2000)

The coat is comprised of two layers: a long, greasy, bristly layer of guard hairs which covers a dense, woolly undercoat (MacNamara, 1990; Nowak, 1991).  The brittle guard hairs are hollow which, combined with the undercoat, provides insulation to -50oC (MacNamara, 1990; Diaz, 2000).  The pelage in winter is comprised of guard hairs 5-7 cm long, which are shed in large clumps during the spring and replaced with a summer coat with hairs 3-4 cm in length (Diaz, 2000; Smith-Flueck, 2000).  In all seasons, the hairs are slightly crinkled, growing the longest on the underside, tail, and legs (Nowak, 1991; Smith-Flueck, 2000).

The build of the Patagonian huemul is distinctly stocky, a result of an arched back and relatively short legs (Nowak, 1991; Smith-Flueck, 2000).  The resulting crouching position is typical of many mountain-dwelling ungulates, as are the hard, pointed, sharply-edged hooves (Geist, 1998; Smith-Flueck, 2000).  Tarsal glands are present on the rear legs, but metatarsal glands are absent (Geist, 1998).

The ears are long and narrow (described by MacNamara (1990) as "donkey ears"); they measure around 17 cm in length, and are covered on their inner surface with white hair (Diaz, 2000; Smith-Flueck, 2000).  The only facial marking is a dark forked blaze on ridge of the nose, which runs from the dark rhinarium and splits in between the eyes to form 'eyebrows' (Smith-Flueck, 2000).  While this blaze is usually attributed to males alone, both sexes possessed such markings in a coastal Chilean population studied by Frid (1994).  The eyes are surrounded by a vague area of lighter colored hair, which accentuates the large preorbital glands (Geist, 1998; Diaz, 2000).  Varying authors report either a presence (MacNamara, 1990; Nowak, 1991) or absence (Smith-Flueck, 2000) of upper canine teeth.

Only males grow antlers; these are usually simple in form and typically branch just once, although antlers with up to five tines have been recorded (Nowak, 1991; Redford and Eisenberg, 1992; Smith-Flueck, 2000). In a typical forked antler, the rear tine is the longer, typically measuring 30-35 cm in length from the burr (where the antler joins the skull) to the tip of the tine (Nowak, 1991; Redford and Eisenberg, 1992, Diaz, 2000).  In young males the first set of antlers appears around eighteen months of age, although they may appear as early as five months of age (Redford and Eisenberg, 1992; Smith-Flueck, 2000). Males cast off their antlers near the end of the austral winter, from mid July to early September (Smith-Flueck, 2000), although Geist (1998) states that they are dropped in October-November. New antlers begin growing soon after old ones are shed, and the full size is reached (and velvet shed) after around five months of growth (Smith-Flueck, 2000).

Ontogeny and Reproduction

The breeding season of H. bisulcus is poorly defined and may differ widely between populations, but is typically at some time between mid-February and May (Smith-Flueck, 2000).  The Patagonian huemul appears to have a dominance group mating system, wherein one dominant male will mate with most of the females in a group (Smith-Flueck, 2000).  Although a male (buck) will mate with many females (does) as they become receptive, the association with a single doe may last for as long as 8-9 weeks, including a long period of time after mating (Smith-Flueck, 2000).

The gestation period has never been measured directly, but estimates range from 6-8 months - reported numbers include 180-210 days (Redford and Eisenberg, 1992), 200-220 days (Smith-Flueck, 2000) and 240 days (Geist, 1998).  Females almost always give birth to a single young, usually in the months of November and December, a time when the local vegetation is highly nutritious (Frid, 1994; Smith-Flueck, 2000).  Fawns are born with a thick, woolly coat which is not spotted (unlike many deer species), but rather a solid dark coffee-brown color (MacNamara, 1990; Redford and Eisenberg, 1992; Smith-Flueck, 2000).  A single newborn huemul examined by Smith-Flueck (2000) weighed 2035 g, with a total body length of 61.5 cm.  Milk teeth show at birth (Smith-Flueck, 2000).

Prior to giving birth, females seek seclusion; born in an isolated area (often along high bluffs), the newborn fawn will spend most of their time bedded down and separated from their mother, with the resting site being changed frequently to avoid predators. Eventually, the fawn will begin to follow its mother, although at a stomp of the dam's feet (indicating danger) the fawn immediately drops to the ground and freezes. Weaning occurs at 4-5 months of age (Smith-Flueck, 2000).

Despite the fact that females may reach sexual maturity as early as 6 months of age, the fecundity of H. bisulcus is low, with fewer than 50% of females breeding on an annual basis.  Smith-Flueck (2000) suggests that this may be due to a long interbirth interval, resulting in females only breeding every other year.   The maximum observed life span for this species is around 14 years of age (Smith-Flueck, 2000).

Ecology

H. bisulcus inhabits rugged and diverse terrain in the southern Andes (MacNamara, 1990; Smith-Flueck, 2000).  While most populations are presently restricted to high, relatively inaccessible regions between 900 and 1,700 meters above sea level, huemuls in coastal Chile have been observed at very low altitudes, even on the beach; i.e., at sea level (Nowak, 1991; Frid, 1994; Smith-Flueck, 2000).  Snow cover is a limiting factor in habitat choice - this species is not found in areas with over 30 cm of snow (Smith-Flueck, 2000).

Huemuls are frequently observed on north or north-western facing slopes, often with a pitch between 30 and 40 degrees (MacNamara, 1990; Redford and Eisenberg, 1992; Smith-Flueck, 2000).  In Chubut, Argentina, however, observations of this species have been made on slopes generally less than 25 degrees (Smith-Flueck, 2000).  Patagonian huemul are usually found at or below the tree line, principally inhabiting brushy areas with dense shrub cover (65% of observations in Argentina) and temperate forests (20% of observations in Argentina) (MacNamara, 1990; Nowak, 1991; Redford and Eisenberg, 1992; Smith-Flueck, 2000).  These subalpine forests are dominated by false-beeches Nothofagus sp. (including N. antarctica, N. betuloides, and N. pumilio; Fagaceae), with shrub cover including Discaria sp. (Rhamnaceae), Gaultheria sp.(Ericaceae), Embothrium coccineum (Proteaceae), Escallonia rubra (Escalloniaeae), and Mulinum spinosum (Umbelliferae) (MacNamara, 1990; Galende et al., 2005).

Seasonal movements are well-documented in this species; huemuls inhabit high altitudes during summer, with frequent usage of pasture and brush above the treeline (80%) or in forests (12.5%) (Nowak, 1991; Smith-Flueck, 2000).  Females especially prefer high cliffs and ridges (likely for the protection they offer from terrestrial predators), while males are found almost exclusively on flatter meadows (Frid, 1994; Smith-Flueck, 2000).  From these high elevations, huemuls move downslope in autumn in order to winter in valleys and denser forests (Nowak, 1991; Redford and Eisenberg, 1992); seasonal movements on the magnitude of two or three kilometers were documented in one animal (Smith-Flueck, 2000).

Patagonian huemuls are either solitary or found in small groups; these are generally composed of 2-5 individuals, although aggregations of up to ten individuals have been observed at low altitudes (Redford and Eisenberg, 1992; Smith-Flueck, 2000).  The structure of these groups is highly flexible, and a single individual may associate in several 'groups' during the course of a single day (Smith-Flueck, 2000). Adults of both sexes are often seen alone, while the most commonly observed grouping is a mother-offspring pair (29%).  Pairs of an adult male and female, either alone or accompanied by juveniles, are also seen regularly, while groups of adult males are infrequent and all-female groups never observed. Adult males tolerate the presence of subordinate males, and it has thus been inferred that territoriality is absent in this species (Smith-Flueck, 2000).

Local population density estimates range from 0.02 to 5.66 animals per square kilometer (Smith-Flueck, 2000), although Redford and Eisenberg (1992) report only the lower end of this range (0.02 to 1.2 per square kilometer).  Annual home range size in Tamango Nature Reserve, Chile was estimated to be 300 hectares (Smith-Flueck, 2000), a figure which compares well to the 340 hectares reported in Redford and Eisenberg (1992).  During the breeding season (between March and May), huemuls confine their movements to ranges of 36 to 73 hectares, although this is likely a gross underestimate of the area used throughout the year (Smith-Flueck, 2000).  On a daily basis, individuals may travel 3-3.9 kilometers as they search for food and shelter (Smith-Flueck, 2000).

Predators of the huemul include the puma (Puma concolor) and domestic dogs (Canis lupus familiarus), while the culpeo fox (Pseudoalopex [Dusicyon] culpaeus), wild cats (Oncifelis guigna and O. geoffroyi), and raptors, especially condors, may be a threat to young (Geist, 1998; Smith-Flueck, 2000).  When threatened by predators, H. bisulcus attempts avoidance by first hiding, but if discovered at close range will flee rapidly (Geist, 1998).  This species has low endurance when running, and will escape persistent pursuers by seeking refuge on cliffs or by swimming into lakes - this species swims with ease (Geist, 1998; Diaz, 2000; Smith-Flueck, 2000).

H. bisulcus is a browser, feeding almost exclusively on tender vegetation and only rarely on grasses or lichens (Geist, 1998; Smith-Flueck, 2000).  Several studies on food consumption have been conducted, which show a strong trend with some regional variation.  In addition to the species listed below, captive animals have shown a preference for willow (Salix sp.) (Smith-Flueck, 2000).

Galende et al. (2005), observing huemul in Nahuel Huapi National Park, identified 32 plant species consumed by H. bisulcus. Shrubs and trees comprised the greatest part of the diet (58.6% and 19.5% of fragments identified in feces, respectively), while forbs and grasses were occasionally consumed, each contributing to just over 9% of the diet. The shrub Ribes magellanicum (Grossulariaceae) and the tree Nothofagus pumilio (Fagaceae) were the principal components of the diet during the summer (28.5% and 33.4%, respectively), while in winter (when these plants drop their leaves) the shrubs Maytenus sp. (Celastraceae) and Gaultheria sp. (Ericaceae) were used heavily (50.8% and 28.7%, respectively).

Smith-Flueck (2000) reports 48 plant species which have been identified in the diet, comprised of 27-46% forbs and 31-72% woody plants when averaged across the year. Maytenus were a very important food item, making up as much as 60% of the annual diet in Argentina. Other frequently used species include Alstroemeria (9%), Chlorea viridiflora (Orchidaceae; 8%), Geranium (5%), and Schinus (5%).

The population living along the Chilean coast observed by Frid (1994) had a more restricted diet, with only 11 species of plant being eaten. The perennial forb Gunnera magellanica (Gunneraceae) was heavily preferred, with consumption of this plant accounting for as much as 82.5% of observed feeding time in grasslands and bluffs.  Feeding in moorland habitat was concentrated on two species: the tree Nothofagus antarctica (Fagaceae; 84.7% of observation time) and evergreen shrub Embothrium coccineum (Proteacea; 15.3% of observation time).

Behavior

H. bisulcus is primarily diurnal in its activity patterns, but may be active at night as well (Redford and Eisenberg, 1992). They have keen senses of sight, hearing, and smell, but (in undisturbed areas) are remarkably tolerant of humans and can be approached within a few meters (Diaz, 2000; Smith-Flueck, 2000). In heavily disturbed regions, huemul are much more flighty due to harassment by humans and especially dogs; in such areas, a huemul may take flight if approached within 300 meters (Smith-Flueck, 2000).

The courtship behavior of the Patagonian huemul is similar to other New World deer, and has been described in detail by Smith-Flueck (2000). As the breeding season approaches, males thrash their antlers against vegetation, helping to shed the velvet from the fully formed antlers and advertising their presence (they may fray the bark off of tree trunks from just above the ground to 113 cm high).  This behavior continues through the courtship period, and is coupled with scent marking using the facial glands (Nowak, 1991).  A male huemul will follow a potentially receptive female, sniffing her anogenital region and employing flehmen (lip-curl) after smelling her urine in order to determine whether or not the female is in estrus.  After determining the reproductive status of a female, the male will approach receptive mates with the head stretched low, performing a high amount of "foreplay" and non-copulatory mounting before achieving intromission.  Dominant males may chase off subordinates if they approach within 300 meters of an estrus female (Geist, 1998).  Otherwise, the low population densities at which huemuls live reduces amount of conflict between males, and may explain the reduced antlers of this species as well as the low frequency of dominance displays (Smith-Flueck, 2000).

Smith-Flueck (2000) describes this species' repertoire of vocalizations, many of which are audible to humans at a distance of 30 meters or more.  During the breeding season, males either a grunt or produce a series of soft whines while pursuing females; a doe, in return, will produce a snort when she is the object of a male's attention.  Agonistic encounters between males are accompanied by a rapid series of sharp notes, lasting 3-6 seconds and descending in volume throughout the series; Smith-Flueck (2000) suggests that older males may produce deeper noises, thereby advertising the male's status.  The alarm call of the Patagonian huemul is a snort, which is usually accompanied by the stamping of the front legs.  Fawns bleat in alarm; these cries usually bring the mother immediately to the fawn.

Genetics

The karyotype of the Patagonian huemul is 2n = 70 (Spotorno et al., 1987 in Redford and Eisenberg, 1992).

Distribution

Prior to the arrival of Europeans in South America, the Patagonian huemul was abundant in southern Chile and Argentina between 34° and 53° S latitude, being found primarily along the spine of the Andes, but also on steppes east of the mountains (Redford and Eisenberg, 1992).  As the map below indicates, the present distribution is significantly reduced, with the majority of subpopulations being restricted to the high Andes.  Redford and Eisenberg (1992) report that H. bisulcus is presently found in the Chilean provinces of Aisén, Magallanes, Nuble, and continental Chiloé.  The Argentinian populations are restricted to provinces of Neuquén, Rio Negro, Chubut and Santa Cruz..

Countries: Argentina, Chile (IUCN, 2006).

Hippocamelus bisulcus range map

Range Map (Redrawn from Diaz, 2000)

Conservation Status

H. bisulcus is classified as endangered (C2a) by the IUCN (2006), and is listed on Appendix I of CITES (2007) along with the congeneric taruca (H. antisensis).  The total population of this species is estimated to be between 1,000 and 1,500 individuals, of which 350-600 inhabit Argentina (Flueck and Smith-Flueck, 2006) - both Redford and Eisenberg (1992) and Smith-Flueck (2000) suggest that current numbers may be less than 1% of this species' pre-European abundance.  Coupled with the reduction in numbers, a reduction in range of over 50% has been noted [Weber and Gonzalez (2003) state that this species inhabits only 30% of its former range], with the result that wild huemul populations are now highly fragmented (Smith-Flueck, 2000).

Threats to huemuls are both ongoing and numerous.  Humans affect huemul directly through hunting (poaching) and by encroaching on this species' habitat (IUCN, 2006).  In the Nevados area of Chile (the site of the most northerly population of huemul), land settlement, construction of pipelines, and logging (along with the construction of logging roads) have all served to reduce native habitats and increase the presence of humans in the region (Povilitis, 1998).  An influx of tourists has also occured, although the impacts of tourism have yet to be determined (Flueck and Smith-Flueck, 2006).  However, perhaps the largest threat comes from domestic stock and introduced species (Redford and Eisenberg, 1992; IUCN, 2006).  Harassment and depredation by domestic dogs, susceptibility to diseases and parasites of introduced species (especially domestic cattle and sheep), and competition from introduced species (e.g., red deer) are all major factors in the continued decline of this species (Povilitis, 1998; Flueck and Smith-Flueck, 2006; IUCN, 2006)

This species is actively protected in Chile, and a conservation agreement between Argentina and Chile is in effect (Weber and Gonzalez, 2003).  However, Flueck and Smith-Flueck (2006) expressed concern regarding the actual conservation status in Argentina; these authors advocate increased conservation measures be taken if this species is to continue to survive.  In 2007, the Huemul Task Force was created under the IUCN Species Survival Commission to provide recommendations - based on sound scientific information - through which the recovery of huemul can be achieved.

Remarks

H. bisulcus is the national animal of Chile (Weber and Gonzalez, 2003), and is the only large herbivore to inhabit the subantarctic false-beech habitat of Patagonia (Smith-Flueck, 2000).

The common name huemul (pronounced hw~y~mul) is of Araucanian origin, and is said to derive from the verb "huemin", meaning "to follow"; this is apparently in reference to a custom of this species of walking in single file (MacNamara, 1990; Smith-Flueck, 2000).  The name is also occasionally spelled as guemal.  In the past, this species was popularly known as the "Chilean huemul".  However, since many populations inhabit Argentina, the use of this name has been replaced by the more appropriate name "Patagonian huemul" (Smith-Flueck, 2000).  An increase in the use of the local name "taruca" for H. antisensis has meant that H. bisulcus is now sometimes referred to simply as the "huemul".

The genus name Hippocamelus is a combination of the Greek words hippos (a horse) and kamelos (a camel) - while huemuls are not closely related to either, they were first described (from hearsay information) as a type of wild ass (Diaz, 2000).  The species name bisulcus translates from Latin as "having two furrows", or "cloven"; which Diaz (2000) suggests refers to original classification of this deer as a cloven-hoofed horse.

Local names
Huemul [from Araucanian Indians] (MacNamara, 1990; Smith-Flueck, 2000)
 
French
Huémul des Andes méridionales (IUCN, 2006)
Huemul du Chili (MacNamara, 1990)
 
German
Südlicher Andenhirsch (MacNamara, 1990)
 
Spanish
Huemul Patagónico (Redford and Eisenberg, 1992)
Ciervo Andino meridional (IUCN, 2006)
Literature Cited
CITES (Convention on the International Trade in Endangered Species of Wild Flora and Fauna).  2007.  Appendices I, II and III, as adopted by the Conference of the Parties, valid from 4 March 2007.  Available online at http://www.cites.org/

Diaz, N. I.  2000.  The huemul (Hippocamelus bisulcus Molina, 1782): A historical perspective.  In The Patagonian Huemul: A mysterious deer on the brink of extinction. By N.I. Diaz and J.A. Smith-Flueck.  Buenos Aires, Argentina: Literature of Latin America (Monograph No. 3).  pp. 1-31.

Flueck, W. T., and J. M. Smith-Flueck.  2006.  Predicaments of endangered huemul deer, Hippocamelus bisulcus, in Argentina: a review.  European Journal of Wildlife Research; 52(2): 69-80.

Frid, A.  1994.  Observations on habitat use and social organization of a huemul (Hippocamelus bisulcus) coastal population in Chile.  Biological Conservation; 67: 13-19.

Geist, V.  1998.  New World deer.  In Deer of the World: Their Evolution, Behaviour, and Ecology.  By Valerius Geist.  Mechanicsburg, PA: Stackpole Books, 1998.  pp. 103-121.

IUCN (International Union for Conservation of Nature and Natural Resources). 2006. 2006 IUCN Red List of Threatened Species. Available online at http://www.redlist.org/

MacNamara, M.  1990.  Guemals, Pudus, and Brockets (Genera Hippocamelus, Pudu, and Mazama).  In Grzimek's Encyclopedia of Mammals. Edited by S. P. Parker. New York: McGraw-Hill. pp. 219-229.

Nowak, R. M. [editor]. 1991.  Walker's Mammals of the World (Fifth Edition).  Baltimore: The Johns Hopkins University Press.

Povilitis, A.  1998.  Characteristics and conservation of a fragmented population of huemul Hippocamelus bisulcus in central Chile.  Biological Conservation; 86: 97-104.

Redford, K. H., and J. F. Eisenberg.  1992.  Mammals of the Neotropics: The southern cone.  Chicago: University of Chicago Press.

Smith-Flueck, J.  2000.  The current situation of the Patagonian huemul.  In The Patagonian Huemul: A mysterious deer on the brink of extinction. By N.I. Diaz and J.A. Smith-Flueck.  Buenos Aires, Argentina: Literature of Latin America (Monograph No. 3).  pp. 67-145.

Weber, M., and S. Gonzalez.  2003.  Latin American deer diversity and conservation: A review of status and distribution.  Ecoscience; 10(4): 443-454.

Whitehead, K. G.  1993.  The Whitehead Encyclopedia of Deer.   Stillwater, MN: Voyageur Press, Inc.  

Wilson, D. E., and D. M. Reeder [editors]. 1993. Mammal Species of the World (Second Edition). Washington: Smithsonian Institution Press.  Available online at http://nmnhwww.si.edu/msw/

Additional Resources (Special thanks to DeerLab; http://www.deerlab.org/)

Corti, P., S. González, R. López, V. Maldonado, J. Smith-Flueck, and F. Vidal Mugica.  2006.  Recomendaciones de la Mesa Experiencias y perspectivas futuras de manipulación, traslocación y conservación ex situ.  In 5th Argentine-Chilean Binational Huemul Conservation Meeting, Administración de Parques Nacionales, Bariloche, Argentina.   pp. 59-60.

Diaz, N. I.  1993.  Changes in the range distribution of Hippocamelus bisulcus in Patagonia.  Zeitschrift fur Saugetierkunde; 58: 344-351.

Flueck, W. T. 2003. Consideraciones acerca de la calidad nutritiva de hábitat, hábitat óptimo, y evaluación de hábitat para huemul. In 4ta reunión Chileno-Argentina sobre estrategias de conservación del huemul.  Edited by G. Acosta-Jamett.  CONAF and CODEFF, Las Trancas, Chile.  pp. 30-34.

Flueck, W. T., and J. M. Smith-Flueck. 1992. Consideraciones acerca de la regulación nutricional de la reproducción y dinámica poblacional en cérvidos. Int. Semin. Native and Introduced Deer in Chile. Asoc. Criaderos de Ciervos Chile: 63-72.

Flueck, W. T., and J. M. Smith-Flueck. 1993. Status und Strategien zum Schutz des bedrohten Süd-Andenhirsches (Hippocamelus bisulcus): Bericht über das erste Argentinisch-Chilenische Treffen.  Zeitschrift fur Jagdwissenschaft; 39(3): 208-210.

Flueck, W. T., and  J. M. Smith-Flueck.  2005.  Hoof growth as a predictor of neonatal age for the Patagonian huemul deer.  Journal of Neotropical Mammalogy; 12(2): 245-248.

Flueck, W. T., and J. M. Smith-Flueck.  2006.  Herbívoros exóticos y su papel en la recuperación del huemul. Proc. 5th Argentine-Chilean Binational Huemul Conservation Meeting, Chalten, SC, Argentina.

Flueck, W. T., and J. M. Smith-Flueck.  2006.  Why the Patagonian huemul deer in Argentina fails to recover: An ecological hypothesis.  In Advances in deer biology.  Edited by L. Bartos et al.  Research Institute of Animal Production, Praha, Czech Republic.  pp. 181-185.

Frid, A.  1991.  Into the last outpost of the huemul.  International Wildlife; 21: 14-19.

Frid, A.  1997.  Apocalypse cow: cattle vs.Chile ’s endangered deer.  Wildlife Conservation; 100: 52-57.

*Frid, A.  1999.  Huemul (Hippocamelus bisulcus) sociality at a periglacial site: Sexual aggregation and habitat effects on group size.  Canadian Journal of Zoology; 77(7): 1083-1091.

*Frid, A.  2001.  Habitat use by endangered huemul (Hippocamelus bisulcus): cattle, snow, and the problem of multiple causes.  Biological Conservation; 100(2): 261-267.

*Galende, G., E. Ramilo, and A. Beati.  2005.  Diet of Huemul deer (Hippocamelus bisulcus) in Nahuel Huapi National Park, Argentina.  Studies on Neotropical Fauna and Environment; 40(1): 1-5.

MacNamara, M. C.  1982.  Huemul: a deer of distinction.  Animal Kingdom; 85: 5-13

Povilitis, A.  1978.  The Chilean huemul project - a case history.  In Threatened Deer: Proceedings of a working meeting of the Deer Specialist group of the Survival Service Commission.  Morges, Switzerland: IUCN.  pp.109-128.

Povilitis, A.  1979.  The Chilean huemul project 1975 –76: huemul ecology and conservation.  Unpublished Ph D Dissertation,Colorado State University: Fort Collins.

Povilitis, A. J.  1983.  Social organization and mating strategy of the huemul (Hippocamelus bisulcus).  Journal of Mammalogy; 64(1): 156-158.

Povilitis, A.  1983.  The huemul in Chile: national symbol in jeopardy?  Oryx; 17: 35-40.

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