AmphibiaWeb - Aneides lugubris


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Aneides lugubris (Hallowell, 1849)
Arboreal Salamander
Subgenus: Aneides
family: Plethodontidae
subfamily: Plethodontinae
genus: Aneides

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Conservation Status (definitions)
IUCN Red List Status Account Least Concern (LC)
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National Status None
Regional Status Population numbers appear to be declining
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View distribution map in BerkeleyMapper.
View Bd and Bsal data (1009 records).

A large robust salamander, Aneides lugubris ranges 65-100 mm in snout-vent length (Lynch and Wake 1974). Dark brown dorsal color, with small, cream or yellow-colored spots on the head, trunk, tail, and limbs; cream-colored venter; yellow undersides of feet and tail. Its head is large and triangular with heavy jaw musculature, especially in adult males. Individuals of this species possess enlarged toe tips and prehensile tails (Stebbins 1985).

Distribution and Habitat

Country distribution from AmphibiaWeb's database: Mexico, United States

U.S. state distribution from AmphibiaWeb's database: California


View distribution map in BerkeleyMapper.
View Bd and Bsal data (1009 records).
Two subspecies are recognized. A. lugubris lugubris is limited to California and northern regions of the Baja California peninsula. Disjunct populations of A. l. lugubris also occur in the foothills of the Sierra Nevada. A. lugubris farallonensis is found only on South Farallon Island, California (Stebbins 1985).

Historical versus Current Distribution: Arboreal salamanders (Aneides lugubris) occur in coastal oak woodlands from northern California (Humboldt County) to approximately Valle Santo Tomás, Baja California del Norte, Mexico. Their range includes South Farallon, Santa Catalina, Los Coronados, and Año Neuvo Islands (Lynch and Wake, 1974; McPeak, 2000). In the foothills of the Sierra Nevada, a geographically isolated cluster of populations occurs in black oak and yellow pine forests (Lynch and Wake 1974). This group of populations is genetically distinct from coastal populations (Jackman 1993). The range of the arboreal salamander is similar to the range of the oaks, Quercus agrifolia and Q. wislizenii, presumably a consequence of shared moisture and soil requirements (Rosenthal 1957). However, in southern California, the species is frequently associated with sycamores (Platanus racemosa), bordering seasonal streams.

Populations have certainly been eliminated as coastal California habitats have been developed, but the species survives in many urbanized regions where adequate cover is present.

Adult Habitat Requirements: Arboreal salamanders are found in a variety of terrestrial and arboreal habitats, including under rocks and woody surface cover, in decaying stumps and logs, in decay holes in trees, and in rock crevices (Ritter and Miller 1899; Ritter 1903; Storer 1925; Miller 1944; Stebbins 1951; Rosenthal 1957; Anderson 1960). Climbing is facilitated by expanded tips of terminal phalanges and large subdigital pads, as well as by the prehensile tail of the arboreal salamander (Ritter and Miller 1899). Individuals have been found over 18m above ground in trees (Ritter and Miller 1899; Ritter 1903; Stebbins 1951). Arboreal salamanders can be found in microhabitats that are drier than those of sympatric salamanders (Storer 1925; Cohen 1952; Ray 1958; Anderson 1960). This species is generally absent from regions receiving < 25 cm of precipitation/yr (Rosenthal 1957).

Life History, Abundance, Activity, and Special Behaviors
Aneides lugubris is completely terrestrial and is nocturnal.

Courtship Behavior: A courting male places his mental gland on the female’s dorsum and, in a succession of quick strokes, draws the mental gland across the female’s back (Arnold 1977). During this behavior, the male’s large and monocuspid premaxillary teeth may scratch the female’s skin and enable efficient delivery of mental gland pheromones to the female’s circulation.

Brood Sites: Reported oviposition sites include in decay holes of live oak trees (most common), under rocks set deeply in the ground, in logs, under surface cover objects (e.g., stone slabs, flower box) and beneath the ground surface (Ritter and Miller, 1899; Ritter, 1903; Storer, 1925). Egg clutches have been found up to 9m in live oak trees (Ritter, 1903).

The eggs are white and encapsulated in two jelly envelopes. Clusters are generally suspended from an overhead support by an 8-20 mm pedicel, although solitary eggs are also found associated with egg masses (Petranka 1998). The number of eggs in a clutch varies from 5 - 24 (Ritter 1903; Storer 1925; Stebbins 1951) with larger females producing more eggs (Anderson 1960). Ovarian counts range from 5-26 maturing oocytes (Anderson 1960). Females on densely populated islands tend to produce fewer eggs than females in less dense mainland populations (Anderson 1960). Eggs are large, 7 - 9.5 mm in diameter. Most females oviposit in late spring or early summer (Stebbins 1951; Anderson 1960). After an approximately 3-4 month developmental period, embryos hatch in August or September at between 26 and 32 mm TL (Storer 1925; Stebbins 1951).

Parental Care: Females are often found coiled around the eggs; males are often in attendance as well (Ritter and Miller 1899; Ritter 1903; Stebbins 1951). Presumed family groups may stay associated after hatching (Ritter 1903).

Age/Size at Reproductive Maturity: Arboreal salamanders are the largest species of Aneides; mature individuals range in size from 65-100mm SVL (Lynch and Wake 1974). Age-size relationships suggest that >= 3 years are required to reach maturity (Anderson 1960). Anderson (1960) reported that the minimum size of sexual maturity was 34mm SVL for females, though this size seems small for typical females reaching sexual maturity.

Behavior: The arboreal salamander may utter a mouselike squeak by forcing air through the jaws or nasal passages (Stebbins 1985).

The arboreal salamander is well known for its aggressive tendencies and weaponry. This species has a suite of morphological features that enable a strong, wound inflicting bite. The jaw muscles are hypertrophied, the skull is heavily ossified with especially strong jaws, and juveniles as well as adults possess enlarged and flattened, blade-like, monocuspid teeth (other plethodontids possess weaker bicuspid teeth as juveniles) (Wake 1966; Wake et al. 1983). In his description of the arboreal salamander, Cope (1899) writes that "On the whole, the physiognomy is not unlike that of a snapping tortoise." Scarred individuals are often found in the field (Miller 1944; N.L. Staub, personal observation) and Myers (1930) observed that salamanders housed in the same container bite each others’ tails. In a study of museum specimens, Staub (1993) found that 15% of the examined individuals were scarred, presumably from conspecific attacks. The frequency of scarring did not differ significantly between males and females (Staub 1993).

Feeding Behavior: Arboreal salamanders are nocturnal and feed most actively under moist/wet conditions. Adults tend to feed on larger prey than juveniles, although Wake et al. (1983) point out that arboreal salamanders of all sizes take a range of prey items. The diet of arboreal salamanders includes millipedes, annelids, snails, and especially colepterans, hymenopterans (ants), isopterans (termites), isopods (sowbugs), chilopods (centipedes), and lepidopterans (Miller 1944; Zweifel 1949; Bury and Martin 1973; Lynch 1985). Miller (1944) suggests that fungus is an important component of the diet, but other authors have not confirmed this observation. Relative to syntopic species, the arboreal salamander consumes disproportionately larger prey items than expected for individuals of a given body size (Lynch 1985), and comparative data suggest that arboreal salamanders consume numerous large-sized prey that other species are unable to capture (Bury and Martin 1973). The structural components of the feeding apparatus are well-developed (e.g., well ossified skull) (Wake et al. 1983). Despite the large jaws and teeth, prey are typically captured by the tongue and brought fully into the mouth, usually without contacting the marginal dentition (personal observation).

Predators: The Pacific rattlesnake (Crotulus viridis helleri) is a known predator of the arboreal salamander (Mahrdt and Banta 1997) and a California scrub jay (Aphelocoma coerulescens) has been observed trying to eat a juvenile arboreal salamander (Rubinoff 1996).

Anti-Predator Mechanisms: Several anti-predatory behaviors have been observed when individuals are startled or attacked: a defensive posture (raising the body stiffly off the ground; Cohen, 1952; Stebbins, 1951), squeaking (Ritter and Miller 1899; Storer 1925), rapid movement and jumping (Ritter and Miller 1899), and biting (Ritter 1903; Storer 1925; Stebbins 1951; Lynch 1981). The arboreal salamander will bite terrestrial garter snakes (Thamnophis elegans) and in some cases the snakes can die from the inflicted wounds (Lynch 1981). Micturition, the act of voiding the bladder when startled, is a novel putative antipredatory behavior that has been documented for the arboreal salamander (Staub and Anderson in press).

Parasites: Two species of nematode (Batracholandros salamandrae, Oswaldocruzia pipiens) have been found in the arboreal salamander (Schad 1960; Goldberg et al. 1998).

Aestivation: Arboreal salamanders are more tolerant of dry conditions than are many species of salamanders and are often among the last salamanders to retreat underground or into tree holes to avoid dessication (Miller 1944; Cohen 1952; Ray 1958; Petranka 1998). This species has relatively low rates of water loss compared to other salamanders, possibly due to postural adaptations (curled body and tightly coiled tail), and a rapid rate of water uptake (Cohen 1952; Ray 1958).

Historical versus Current Abundance: Arboreal salamanders remain common in many areas, however in some areas populations have declined in the past 20 years (D.B. Wake, in Petranka, 1998). Petranka (1998) suggests that large oaks used for nesting and aestivation should be preserved. The current decline of live oaks in California will have negative effects on arboreal salamander populations.

Trends and Threats
Although Aneides lugubris is not presently on any endangered species lists, population numbers appear to be declining (D. Wake pers. comm. 1999).

Possible reasons for amphibian decline

General habitat alteration and loss
Habitat modification from deforestation, or logging related activities
Prolonged drought

Interspecific Associations/Exclusions: Arboreal salamanders are syntopic with California slender salamanders (Batrachoseps attenuatus), the wandering salamander (A. vagrans), and the black salamander (A. flavipunctatus) in regions north of San Francisco Bay. Throughout most of the rest of its range A. lugubris occurs in sympatry with Ensatina and a number of species of Batrachoseps. Ecological interactions between these species are not well understood. Maiorana (1978) showed that there may be competition for food between California slender salamanders and arboreal salamanders when large prey are limited. When large prey items are not limiting however, Lynch (1985) found broad dietary differences between these two species-the arboreal salamander tends to eat a few, large bodied prey in addition to a diverse assortment of other prey items. Arboreal salamanders occasionally prey on Batrachoseps (Storer 1925; Miller 1944).

Chromosomal variation: There are two geographically segregated groups of chromosomally differentiated populations of the arboreal salamander (Sessions and Kezer 1987). These two karyotypes intergrade in south and east central Mendocino County (Sessions and Kezer 1987). Unpublished genetic analyses (allozymes and mitochondrial DNA sequences) show that the chromosomal units do not correlate with patterns of genetic variation (Jackman 1993). The Farallon Island population is genetically most similar to the nearest mainland population, not populations in the Gabilan mountains to the south as suggested by Morafka (1976) (Jackman 1993).

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Dunn, E. R. (1926). The Salamanders of the Family Plethodontidae. Smith College, Northhampton, Massachusetts.

Hallowell, E. (1849). ''Description of a new species of salamander from upper California.'' Proceedings from the Academy of Natural Sciences of Philadelphia, 4(126).

Lynch, J. F., and Wake, D. B. (1974). ''Aneides lugubris (Hallowell). Arboreal Salamander.'' Catalogue of American Amphibians and Reptiles. Society for the Study of Amphibians and Reptiles, 159.1-159.2.

Miller, L. (1944). ''Notes of the eggs and larvae of Aneides lugubris.'' Copeia, 4, 224-230.

Petranka, J. W. (1998). Salamanders of the United States and Canada. Smithsonian Institution Press, Washington D.C. and London.

Rosenthal, G.M. (1957). ''The role of moisture and temperature in the local distribution of the plethodontid salamander Aneides lugubris.'' Zoology, 54(6), 371-420.

Stebbins, R. C. (1985). A Field Guide to Western Reptiles and Amphibians. Houghton Mifflin, Boston.

Zweifel, R.G. (1949). ''Comparison of the food habits of Ensatina eschsholtzii and Aneides lugubris.'' Copeia, 4, 285-287.

Originally submitted by: Sarah Graber, Meredith J. Mahoney (first posted 1999-02-16)
Distribution by: Michelle S. Koo (updated 2021-03-17)
Life history by: Michelle S. Koo (updated 2021-03-17)
Comments by: Michelle S. Koo (updated 2021-03-17)

Edited by: Kellie Whittaker, Meredith J. Mahoney, Michelle S. Koo (2021-08-27)

Species Account Citation: AmphibiaWeb 2021 Aneides lugubris: Arboreal Salamander <> University of California, Berkeley, CA, USA. Accessed Feb 24, 2024.

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Citation: AmphibiaWeb. 2024. <> University of California, Berkeley, CA, USA. Accessed 24 Feb 2024.

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