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FIRE ECOLOGY

SPECIES: Prosopis glandulosa | Honey Mesquite

FIRE ECOLOGY OR ADAPTATIONS:


Fire adaptations: When the aboveground portion of honey mesquite is damage by fire, regeneration occurs by sprouting from lateral roots in the upper 1 foot (0.3 m) of soil and establishing from seed [81]. Mature plants contain numerous, dormant buds on the upper 12 inches (30 cm) of the taproots [47,62,64] where they are insulated from the heat of most fires. Following top-kill by fire, numerous sprouts arise from the underground buds. Even 6- month- old seedlings have sufficiently developed underground stem buds to allow plants to survive "cool" burns [190]. The data of Ansley and others [10] suggest that bark on older stems is often thick enough to protect the phloem from damage; when top-kill does occur, it is more commonly via damage at canopy height. Mortality is low in honey mesquite, particularly in lowland areas where root systems are well developed [188,190]. In riparian communities of the Colorado River, however, where western honey mesquite grows with saltcedar, frequent fire will likely lead to a decline of western honey mesquite and increase of saltcedar because the latter grows much faster [4,126].

Numerous wild and domestic animals consume and disperse honey mesquite seed [104]. Little is known about honey mesquite seed banks, seed longevity in the field, or the importance of seed banks in recovery after fire [171]. Seed from off-site honey mesquite could potentially be transported to burned areas by animals. Johnston [97] states that where mesquite dominates brushy ranges, the successional changes may not have been from mesquite-free grasslands to brushlands, but from low stature mesquite grasslands to brushlands. Brown and Archer [33] hypothesize that since mesquites evolved with browsing Pleistocene megafauna, low densities of honey mesquite in southwestern grasslands prior to European-American introduction of livestock resulted primarily from limited seed dispersal after the Pleistocene [129].

Fire regimes: More is known about historic fire regimes in communities of the typical variety of honey mesquite than in western honey mesquite communities. Western honey mesquite occurs in the Mojave and Sonora deserts; not much is known of their fire histories. It is assumed that fuels in these desert were so discontinuous in the past that fire was infrequent [121]. In former desert grassland communities that honey mesquite has invaded in southeastern Arizona, southern New Mexico, and southwestern Texas, fires occurred at "rather frequent intervals" prior to livestock introduction [90]. McPherson [121] states that it is difficult to know detailed fire history in desert grasslands but indirect evidence, primarily accounts of European- American settlers, suggests that fires occurred at least every 10 years. Also, based on known rates of velvet mesquite establishment and growth in grasslands, McPherson [121] concluded that fires had to have occurred at 7 to 10 year intervals to prevent its establishment. Using a similar analysis, Paysen and others [135] concluded that the likely historic average fire return interval in mesquite savannas was 10 years. There were large numbers of livestock in some areas of the desert grassland as early as 1880, and fire frequency was reduced due to lack of fuel rather than fire suppression [90].

Honey mesquite also grows in dune fields that, because of low fuel loading, have seldom if ever burned. An example of such a habitat is the Wild Horse Desert of southern Texas, a sandy rangeland where fuel is discontinuous and honey mesquite grows 15 to 20 feet (4.6-6.1 m) tall [90].

Fire regimes for plant communities and ecosystems in which honey mesquite occurs are presented below. More information regarding fire regimes and fire ecology of these communities can be found in the 'Fire Ecology and Adaptations' section of the FEIS species summary for the plant community or ecosystem dominants below.

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
bluestem prairie Andropogon gerardii var. gerardii-Schizachyrium scoparium < 10 [106,135]
bluestem-Sacahuista prairie A. littoralis-Spartina spartinae < 10 
desert grasslands Bouteloua eriopoda and/or Pleuraphis mutica 5-100
plains grasslands Bouteloua spp. < 35
blue grama-tobosa prairie B. gracilis-Pleuraphis mutica < 35 to < 100 
paloverde-cactus shrub Cercidium microphyllum/Opuntia spp. < 35 to < 100 
blackbrush Coleogyne ramosissima < 35 to < 100 
juniper-oak savanna Juniperus ashei-Quercus virginiana < 35
Ashe juniper J. ashei < 35 
Ceniza shrub Larrea tridentata-Leucophyllum frutescens-Prosopis glandulosa < 35
galleta-threeawn shrubsteppe Pleuraphis jamesii-Aristida purpurea < 35 to < 100 [135]
mesquite Prosopis glandulosa < 35 to < 100 [121,135]
mesquite-buffalo grass Prosopis g.-Buchloe dactyloides < 35
Texas savanna Prosopis g. var. glandulosa < 10
shinnery Quercus mohriana < 35
little bluestem-grama prairie Schizachyrium scoparium-Bouteloua spp. < 35 [135]

POSTFIRE REGENERATION STRATEGY [166]:


Tree with adventitious bud/root crown/soboliferous species root sucker
Geophyte, growing points deep in soil
Initial off-site colonizer (off-site, initial community)
Ground residual colonizer (on-site, initial community)

Related categories for SPECIES: Prosopis glandulosa | Honey Mesquite

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Content on this web site is provided for informational purposes only. We accept no responsibility for any loss, injury or inconvenience sustained by any person resulting from information published on this site. We encourage you to verify any critical information with the relevant authorities.

Information Courtesy: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Fire Effects Information System

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