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New Mexico
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Madrean Pine-Oak

Description, importance and conservation status:

This habitat type is found only in the Animas and Peloncillo Mountains in Hidalgo County. It is part of the "Madrean Sky Islands" and corresponds to the habitat of the same name in Arizona (AZ PIF).

This habitat is defined by Chihuahua pine (Pinus leiophylla) and Arizona white oak (Quercus arizonica). Mean annual precipitation is 22 inches per year. Mean annual temperature is 52 degrees. Elevations range from 5000 to 7000 feet.

Associated trees in this type include emory (Q. emoryi), netleaf (Q. rubosa) and silverleaf oak (Q. hypoleucoides). Associated conifers include border pinyon (P. discolor) and alligator juniper (J. deppeana). Some common shrubs are manzanita (Arctostaphylos pungens), yuccas (Yucca spp.), agave (Agave spp.), beargrass (Nolina microcarpa) and wright silktassel (Garrya wrightii). Herbs include bullgrass (Muhlenbergia emersleyi), mutton grass (Poa fendleriana), sedge (Carex sp.), beggartick grass (Aristid orcuttiana), pinyon ricegrass (Piptochaetium fimbriatum), bluestems (Schizachyrium spp.), and pennyroyal (Hedeoma spp.)

Principal influences in this habitat are fire, grazing, fuelwood cutting, road-building, and mining. Fire has been largely suppressed since the 1880's, concurrent with the advent of large-scale grazing. A study of this type of forest in Arizona concluded that low intensity fires had burned some part of a 215-acre forest plot in 67 different years over a hundred-year period (Ganey et al. 1996 in Ffolliott et al. 1996). Fires can be expected to encourage oak and juniper growth and enhance germination of such shrubs as manzanita and deerbrush (Ceanothus sp.). Chihuahua Pine, in particular, is a fire-adapted species and shows shade tolerance in an understory of oaks and junipers (Dick-Peddie 1993). It appears that the presence of Chihuahua pine signifies a climax forest. Long-term, year-long and rotation-pasture grazing has reduced the palatable herbaceous component and favors poisonous or thorny understory species such as sages (Artemisia spp.), broom snakeweed (Gutierrezia sarothrae) and catclaw mimosa (Mimosa sp.). A change to these species' dominance in the understory may have influenced the production of less palatable plants and mat-forming, low grasses such as blue grama (Bouteloua gracilis) (Neilson 1986).

The Buff-breasted Flycatcher was historically a breeding species in this type of New Mexico woodland. Prior to the 1990's, it was last definitely sighted in the state in 1929. The last recorded nest was reported in 1887 (Hubbard 1978). However, this species has been recently documented in this habitat in the Peloncillo Mountains several times. This species would be considered a priority species if it were to be found breeding again in the state.

The Buff-breasted Flycatcher breeds in wide mountain canyons with open growth of pines and/or oaks. Its habitat usually contains an open understory of grasses and small trees or burned forest with patches of living pines. Nesting has been documented in Arizona between 6400 and 9400 feet. Optimal habitat has a gradual slope and canopy cover of about 20% above 33ft (10m) and <10% cover below 16ft (5m). Typical canopy trees are pines of medium-age or older. The understory should have 198-210 small oaks per acre (80-85 per hectare). These forest patches should be >492ft (150m) wide (Bowers and Dunning 1994). Management for this species may return it to the regular breeding avifauna of the state.

Additionally, the Gould's subspecies of Wild Turkey resides in the Peloncillo Mountains. This New Mexico state Threatened and Endangered Species is found nowhere else in the state. The population currently appears stable.

This habitat is managed or owned by private land-owners in the Animas Mountains, primarily by the Animas Foundation. Portions of the Peloncillo Mountains are also managed by the Animas Foundation. Other sections are managed by the U.S. Forest Service or by other private land-owners.

Physiographic Areas covered: Mexican Highlands.

Associated priority species from Appendices B and C:

Table 1. Madrean Pine-Oak Priority Species

Highest Priority

Priority

High Responsibility

Montezuma Quail
Whiskered Screech-Owl
Elegant Trogon
Strickland's Woodpecker
Black-throated Gray Warbler

Zone-tailed Hawk
Elf Owl
Whip-poor-will
Western Bluebird
Grace's Warbler

Ash-throated Flycatcher
Cassin's Kingbird
Mexican Jay
Bridled Titmouse
Juniper Titmouse
Hepatic Tanager

Additional Representative Species: Hutton's Vireo

Bird Habitat Requirements, Population and/or Habitat Objectives:
(in taxonomic order)

Montezuma Quail (Hagelin 1998)

Associated Species: Acorn Woodpecker, Ash-throated Flycatcher, Cassin's Kingbird, Hutton's Vireo, Bridled Titmouse, Canyon Towhee, Black-chinned Sparrow

Distribution: Found in the Mexican Highlands, the Mogollon Rim including up to the Magdalena mountains and in the Colorado Plateau north to the Sacramento and Capitan mountains.

Population and/or Habitat Objectives:

Whiskered Screech-Owl (Williams 1999)

Associated Species: Northern Pygmy-Owl, Western Screech-Owl, Whip-poor-will, Acorn Woodpecker, Buff-breasted Flycatcher, Cassin's Kingbird, Mexican Jay, Black-throated Gray Warbler, Hepatic Tanager, Black-headed Grosbeak

Distribution: Currently found only in 5 canyons in the Peloncillo Mountains.

Population and/or Habitat Objectives:

Elegant Trogon (Kunzmann et al. 1998)

Associated Species: Zone-tailed Hawk, Elf Owl, Black-chinned Hummingbird, Dusky-capped Flycatcher, Hepatic Tanager, Brown-crested Flycatcher, Magnificent Hummingbird, Strickland's Warbler

Distribution: Currently found only in the Peloncillo Mountains

Population and/or Habitat Objectives:

Strickland's Woodpecker (Williams 1999)

Associated Species: Zone-tailed Hawk, Common Poorwill, Ash-throated Flycatcher, Mexican Jay, Grace's Warbler, Hepatic Tanager

Distribution: Found only in the Peloncillo and Animas mountains of New Mexico

Population and/or Habitat Objectives:

Hutton's Vireo (Davis 1995)

Associated Species: Whip-poor-will, Ash-throated Flycatcher, Dusky-capped Flycatcher, Bridled Titmouse, Bewick's Wren, Black-throated Gray Warbler, Black-headed Grosbeak

Distribution: Found in the southwestern quadrant of the state as far north and east as the Black Range. May occasionally breed in the Organ mountains in Dona Ana County.

Population and/or Habitat Objectives:

Mexican Jay (Brown 1994)

Associated Species: Wild Turkey, Juniper Titmouse, Bridled Titmouse, Black-throated Gray Warbler, Black-headed Grosbeak, Spotted Towhee

Distribution: Found in the Mogollon Rim and the Mexican Highlands west of the Black Range and south of Reserve and Luna.

Population and/or Habitat Objectives:

Black-throated Gray Warbler (Guzy and Lowther 1997)

Associated Species: Elf Owl, Plumbeous Vireo, Juniper Titmouse, White-breasted Nuthatch, Bewick's Wren, Western Bluebird, Black-headed Grosbeak

Distribution: Found throughout the state in appropriate habitat. Very few are in the Pecos and Staked Plains.

Population and/or Habitat Objectives:

Overall Habitat Strategies:

Fire

Cool Fires are characterized by low flames (2-3 ft. high). They generally do not kill oaks. Shrubs are often reduced in height but not in density. Grass cover is reduced but recovers quickly, sometimes within two years. These types of fires were probably regular in this habitat until fire suppression in these forests became a management goal. Allowing fire likely favors snag nesters such as Whiskered Screech-Owl and Strickland's Woodpecker in the long-term, but snag nesters may show an initial decline following a fire (Ganey et al.1996). Open-forest bird species such as Cassin's Kingbird, Western Bluebird, and Chipping Sparrow will probably increase (Ganey et al.1996). Ground-nesting species such as Montezuma Quail and Wild Turkey, or those preferring denser forests such as Elf Owl and Black-throated Gray Warbler, will probably decline in the short term (Ganey et al. 1996).

Hot Fires are often stand-replacing fires, sterilizing the soils and destroying habitat for many species. They burn overstory trees and are costly to fight. Recovery of bird populations in high-intensity burns can be delayed (Johnson and Wauer in Ganey et al. 1996). However, these fires may not be catastrophic, especially if they burn in a mosaic pattern over the landscape (Ganey et al. 1996). Cavity-nesters will probably benefit from "mosaic" fires, especially along edges of unburned areas (Ganey et al. 1996).

While frequent, cool fires are thought to be the natural fire regime in this habitat, restoring these forests to a more natural state could be difficult given the heavy fuel buildup allowed through fire suppression. Hot fires should be allowed to burn under management rather than quickly extinguishing them. Prescribed, cool fires may be the most economical and efficacious way to achieve a more natural condition. This method may cause initial declines in bird populations. Public education about the initial costs of restoring forests to a more natural condition should be undertaken. (Ganey et al. 1996)

Research and monitoring needs:

1. Determine estimated Montezuma Quail population for the state

2. Determine number of breeding Strickland's Woodpecker in the state

3. Determine combined effects of differing grazing regimes, with and without fire, on this habitat; determine the long-term effects on birds.

Additional species for which monitoring is recommended:

Table 2. Madrean Pine-Oak Woodland Priority Species: Habitat Factors

Species

Vegetation Composition/ Structure

Abiotic Factors

Landscape Factors

Special Factors

MZQU

open oak or pine-oak woodland; grass: 1ft or taller; of total grass coverage, 50% must be tall grass

 

associated with drainages when oaks follow drainages into grasslands

 

WHSO

dense pine oak woodlands; needs oaks from 17-23ft high

often found on north-facing slopes

favors oak riparian areas in canyons

may use nest boxes

STWO

pine-oak woodlands

 

often found in riparian canyons

 

HUVI

pine-oak woodland dominated by evergreens with high % closed canopy moderate to dense shrub canopy closure

 

edges of clearings needed; nests about third tree in from edge

 

MEJA

mature pine-oak woodland with junipers

 

territories may include riparian drainage

 

BTYW

mature pinyon-juniper oak often with closed canopy

 

associated with tree/shrub or tree/grass edges