Index of Species Information

SPECIES:  Parkinsonia florida

Introductory

 
Pavek, Diane S. 1994. Parkinsonia florida. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/ [].

ABBREVIATION : PARFLO SYNONYMS : Cercidium floridum Benth ex Gray. (Fabaceae) [5,27,55,82] Cercidium torreyanum (S. Wats.) Sarg. [30] SCS PLANT CODE : PAFL6 COMMON NAMES : blue paloverde TAXONOMY : The currently accepted scientific name of blue paloverde is Parkinsonia florida (Benth.) S. Wats. [62,82,83]. Besides the typical subspecies that is recognized throughout most of the species range, peninsular blue pale verde (described as C. f. ssp. peninsulare (Rose) Carter) occurs in Baja California [76]. Occasionally, blue paloverde hybridizes with yellow paloverde (P. microphyllum) [39]. LIFE FORM : Tree FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY

DISTRIBUTION AND OCCURRENCE

SPECIES: Parkinsonia florida
GENERAL DISTRIBUTION : Blue paloverde is distributed through the Sonoran Desert.  Its range extends from central and southwestern Arizona into southeastern California [15,25,35,39,62,68].  Blue paloverde continues southward through western Sonora, Mexico [5,21,47].  Disjunct populations of blue paloverde are located in northern Sinaloa and Baja California Sur [27,31,39,55,76]. ECOSYSTEMS :    FRES30  Desert shrub    FRES40  Desert grasslands STATES :      AZ  CA  MEXICO BLM PHYSIOGRAPHIC REGIONS :     7  Lower Basin and Range KUCHLER PLANT ASSOCIATIONS :    K027  Mesquite bosque    K041  Creosotebush    K042  Creosotebush - bursage    K043  Paloverde - cactus shrub SAF COVER TYPES :     68  Mesquite    242  Mesquite SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Blue paloverde is a characteristic member of the Sonoran Desert floristic region [38,79].  It is a member of desert scrub communities. Blue paloverde is a major component in creosotebush (Larrea tridentata) and white bursage (Ambrosia dumosa) climax communities on lower bajadas [8,12,22,38,74]. Blue paloverde is a facultative desert riparian species that may be restricted to washes or arroyos in parts of its range but also occurs in upland communities.  It primarily occurs in communities irregularly scattered along arroyos [68].  These communities with intermittent water are variously classified as desert riparian associations [33], pseudo-riparian communities [11], desert wash woodlands [7,13,53,71], Colorado River riparian forests [49], and desert microphyll associations [61].  Codominants in all of these classifications are honey mesquite (Prosopis glandulosa var. glandulosa), smoketree (Psorothamnus spinosus), ironwood (Olneya tesota), desert willow (Chilopsis linearis), and catclaw acacia (Acacia greggii) [52,58,71]. Blue paloverde is a dominant member of the mixed scrub series with ironwood and jojoba (Simmondsia chinensis) [68].  Within the broadleaf woodland subformation, the paloverde series is dominated by either blue paloverde or yellow paloverde; the understory is sparse in this series [43]. Blue paloverde is listed as a dominant or indicator species in the following publications: (1)  A vegetation classification system applied to southern California [43] (2)  The vascular plant communities of California [61] (3)  Vegetation of the Santa Catalina Mountains, Arizona: a gradient        analysis of the south slope [74]. Species associated with blue paloverde but not previously mentioned in DISTRIBUTION AND OCCURRENCE include desert hackberry (Celtis pallida), desert lavender (Hyptis emoryi), big saltbrush (Atriplex lentiformis), Torrey seepweed (Suaeda torreyana), spidergrass (Aristida ternipes), and Rothrock grama (Bouteloua rothrockii) [23,47,49,68].

MANAGEMENT CONSIDERATIONS

SPECIES: Parkinsonia florida
WOOD PRODUCTS VALUE : The wood of blue paloverde is light to heavy, soft, and close-grained [30,70].  Blue paloverde is used for fuel [49]. IMPORTANCE TO LIVESTOCK AND WILDLIFE : Blue paloverde fruits, twigs, and leaves are used as livestock forage throughout the year [60].  Mule deer, bighorn sheep, and burros browse its twigs and leaves [15,80].  Small mammals consume blue paloverde seeds during summer and fall [15]. In southern Arizona, blue paloverde taller than 6.7 feet (2 m) is used for nesting [65].  With a large canopy, blue paloverde offers many sites for bird perching, nesting, and foraging.  The blue paloverde-ironwood vegetation type supports a high density and diversity of breeding birds [7,16,20].  In south central Arizona, 19 species of breeding birds were present in mesquite (Prosopis spp.) bosques where blue paloverde occurred [56]. Blue paloverde leaves and stems contain cyanogenic glycosides, alkaloids, and cinnamic phenolic acid which may deter herbivory [77]. PALATABILITY : NO-ENTRY NUTRITIONAL VALUE : Blue paloverde aboveground biomass is about 22 percent nitrogen, 50 to 80 percent dry matter, and 17 percent crude protein [4,63,64,80]. Equations are available to predict amounts of dry matter, nitrogen, and carbon based on blue paloverde height and crown measurements [4]. COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : Blue paloverde has successfully established by artificial seeding following highway construction [9]. Blue paloverde naturally established following removal of invasive populations of saltcedar (Tamarix ramosissima) [2].  Soil preparation, planting, and irrigation methods for blue paloverde are discussed in the literature [3,71]. OTHER USES AND VALUES : Blue paloverde fruits have been used by Native Americans for food [5]. The Pima and Papago in Arizona cooked young blue paloverde fruits and seeds and ground the seeds for porridge [15]. The Pima carved blue paloverde into large serving spoons [46]. OTHER MANAGEMENT CONSIDERATIONS : Blue paloverde and other species were tested for biomass production for use in fuelwood and erosion control programs.  Blue paloverde and ironwood ranked lowest of the tested species for biomass production [18]. Young blue paloverde can tolerate moderate grazing.  In greenhouse tests, blue paloverde sprouted following top removal.  At a transplant site near Travertine Point, California, severely gnawed blue paloverde transplants survived only when irrigated [3]. Seed predation by invertebrates such as bruchid beetles can lead to logarithmic increases in seed mortality of blue paloverde [28]. Blue paloverde has decreased in some areas of Arizona partly due to the erosion of broad flat washes into narrow, steep-sided channels [67].  In the microphyll woodlands of the desert washes, disturbance by offroad vehicles decreases density and biomass of perennial plants such as blue paloverde [7]. Natural recovery following disturbance is slow in wash woodlands in which blue paloverde occurs.  Optimal conditions for reestablishment occur infrequently.  It may take up to 60 years for these woodlands to reach predisturbance levels of biomass, and 180 years to reach predisturbance levels of species diversity [71].  In southeastern California, blue paloverde is a nurse plant for saguaro (Carnegiea gigantea) [13].  Saguaro eventually outlive or contribute to the death of paloverde species [35]. Blue paloverde does not have mycorrhizal nodules [72].  The presence of other mycorrhizal associations was not discussed.

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Parkinsonia florida
GENERAL BOTANICAL CHARACTERISTICS : Blue paloverde is a native, spiny, small tree or subtree [30,35,39,78]. It has multiple stems [4].  Blue paloverde grows to 32.8 feet (10 m) tall with a trunk diameter of 1.5 feet (0.5 m) and a crown spread of 163.4 square feet (15.2 sq m) [4,5,30,39].  Blue paloverde has thin-barked, photosynthetic stems [3,66].  Age influences photosynthetic rate of stems; younger stems have higher photosynthetic rates [41].  Its pinnately compound leaves are about 1 inch (2.5 cm) long and drought-deciduous [3,30,54,66,78].  Inflorescences of blue paloverde are 1.5 to 4.7 inches (4-12 cm) long with one or more flowers [55,62,70]. The fruits are flat legumes, 1.5 to 4 inches (4-10 cm) long [39,62,70]. Each legume holds one to eight flat seeds [36,39,70]. RAUNKIAER LIFE FORM :       Phanerophyte REGENERATION PROCESSES : Blue paloverde reproduces sexually and probably asexually.  In a greenhouse study, young blue paloverde sprouted after plants were clipped to less than one-half of their total height [3].  A close relative, yellow paloverde, sprouts following top-kill [32]. Photoperiod controls blue paloverde flower and fruit initiation and stem growth; however, moisture and temperature determine actual organ production [13,66]. Abiotic and biotic agents aid in seed dispersal.  The flat seeds of blue paloverde prevent air loft and allow downward dispersal into washes. Fruits and seeds do not float.  Occasionally, blue paloverde fruits disperse unopened.  Some seed dispersal occurs via animals.  Blue paloverde has been found occasionally in ant formicaries below the soil surface.  Seeds will germinate in these caches.  Birds probably move seed upstream [36]. Large seedbanks of blue paloverde may be present.  Scarification from flash floods or other abrasive processes facilitates germination [36,43,71,73].  Blue paloverde germinates well on sandy deposits [67]. Shade and litter beneath mature blue paloverde alters seed microsites and makes germination more likely [54]. Blue paloverde establishment is limited by climate extremes, low moisture availability, poor soil characteristics, and herbivory.  Rapid, deep root development is important for blue paloverde establishment.  In greenhouse trials, blue paloverde roots grew an average of 0.3 inch per day (0.9 cm/day) [3].  Mature blue paloverde has deep root systems that reach ground water and make blue paloverde less vulnerable to drought [42].  A herbivory experiment was conducted on blue paloverde at Travertine Point, California.  Seven months after blue paloverde germinated, rabbits and other rodents grazed 86 percent of the seedlings.  Ninety percent of these grazed blue paloverde seedlings appeared unlikely to survive [3]. SITE CHARACTERISTICS : Blue paloverde occurs in arid and semiarid climates characterized by high summer temperatures and highly variable rainfall.  Precipitation predominantly falls bimodally, in winter and in summer [40,52,53,66]. Blue paloverde is found at elevations from sea level to 4,000 feet (0-1,220 m) [4,15,26,34,74].  It occurs on almost level (less than 5%) to steep slopes [4]. Blue paloverde predominantly grows in washes, but is also found in upland habitats.  Blue paloverde occurs in moderate to large watersheds from 1 to 50 square miles (2.6-130 sq km) [81].  It grows on terraces, high flood plains, arroyos or dry washes, and intermittent streambeds more than 4 to 5 feet (1.2-1.5 m) wide with deep soil [8,54,79,81].  In the northern Sonoran Desert at moderately high elevations, blue paloverde grows in upland positions [66].  Blue paloverde occupies hills, mountain slopes, and middle to lower bajadas [4,54,65]. Blue paloverde grows in soils with low levels of nutrients, especially nitrogen and phosphorus [3].  Soil textures it occurs on may be sandy to gravelly, coarse loamy to fine sand overlain with fine gravel [4,54,65]. SUCCESSIONAL STATUS : Facultative Seral Species Blue paloverde occurs from pioneer to climax communities, depending on site characteristics.  In fact, classical succession may not occur in the desert ecosystems where blue paloverde occurs.  In the xeroriparian systems to which blue paloverde belongs, community development is influenced by catastrophic floods and long recovery periods [26].  After disturbance of the desert scrub communities, former dominants such as blue paloverde are the first to appear and replace themselves [48]. SEASONAL DEVELOPMENT : Flower and leaf production of blue paloverde vary according to the amounts of precipitation received [66].  Blue paloverde remains leafless throughout most of the year [30].  Leaves are produced between mid-July and late November, depending on the summer rains [66].  Leaves drop during drought and are not replaced until the following spring [13]. Blue paloverde typically flowers sporadically after rains from late March to May, but flowering may extend into July [5,15,30,66,70]. Populations of blue paloverde also may bloom August to October [30]. Fruits mature about 1 month after flowering, typically from May to July [66,70].

FIRE ECOLOGY

SPECIES: Parkinsonia florida
FIRE ECOLOGY OR ADAPTATIONS : Blue paloverde is susceptible to fire; its photosynthetic stems are probably easily killed by fire.  It may sprout from the root crown if its postfire response is similar to its response to clipping. The historical fire regime of the Sonoran Desert is mostly unknown [24]. Thomas [59] mentioned that fire free periods in the Sonoran Desert are greater than 250 years.  However, Loftin [32] stated that fires were relatively common in the Sonoran Desert under appropriate conditions, especially during summer.  Fires that do occur are usually low-severity due to small fuel loads [37]. Grazing and vegetation change have probably altered the fire regime from historic patterns.  On the Santa Rita Experimental Range in southern Arizona, frequent fires were common until 1916 because dense stands of grass were present.  Fires were frequent at the turn of the century in desert grasslands that border the desert scrub communities where blue paloverde occurs.  By the 1960's, fire frequencies had declined due to grazing and fire suppression [24].  In south-central Arizona, understory vegetation beneath paloverde species, ironwood, mesquite, and saguaro associations changed from grasses to low shrubs due to grazing pressures.  This has altered the fire regime, resulting in less frequent fires [50].  However, where introduced annual grasses now predominate, fire frequency may have increased. The Sonoran savanna grasslands are subtropical, fire-climax communities. Blue paloverde occurs infrequently in these communities at their northern limits [10]. POSTFIRE REGENERATION STRATEGY :    Tree with adventitious-bud root crown/soboliferous species root sucker    Secondary colonizer - off-site seed

FIRE EFFECTS

SPECIES: Parkinsonia florida
IMMEDIATE FIRE EFFECT ON PLANT : Blue paloverde with its thin photosynthetic bark is probably top-killed by fire.  Surviving rootstocks may sprout if the response of blue paloverde is similar to yellow paloverde [32].  If plants are heat damaged, they may die several months after burning [14].  Seeds are probably killed by fire unless protected by insulating layers of soil. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : In desert plant communities where blue paloverde occurs, 20 years may be necessary for plant densities to recover to prefire levels [14,32,51]. Four years after a February 1964 fire in a southeastern California desert scrub community, soils beneath burned and unburned woody plants were surveyed.  Soil beneath burned blue paloverde had a strongly hydrophobic layer overlain by a slightly hydrophobic layer.  Burned soil had a slightly higher degree of water repellency than unburned soil. This water-repellent burned soil causes a reduction of available water moisture and inhibits germination of species such as annuals beneath blue paloverde [1].  This may protect blue paloverde from some fires. Native annual plants probably did not create the same large fuel load that introduced annual species currently provide [32]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : It is difficult to control shrubs and trees with fire on arid habitats due to lack of fuel.  Two consecutive wet winters are probably necessary to develop adequate fuel to sustain a fire in the desert scrub [37]. Prescribed fires once every 10 years would keep blue paloverde in check [23]. Depending upon the season of burning, soil nutrients may be quickly translocated following fire on the desert soils where blue paloverde occurs.  Available nitrogen in the soil drops below prefire levels for several years due to removal of nitrogen-containing ash by run-off[75]. Dry matter levels are useful for predicting flammability of fuels.  Near Tucson, Arizona, aboveground biomass of blue paloverde was 80.3 percent dry matter [4].

REFERENCES

SPECIES: Parkinsonia florida
REFERENCES :  1.  Adams, Susan; Strain, B. R.; Adams, M. S. 1970. Water-repellent soils,        fire, and annual plant cover in a desert scrub community of southeastern        California. Ecology. 51(4): 696-700.  [5407]  2.  Anderson, Bertin W.; Ohmart, Robert D.; Disano, John. 1979. Revegetating        the riparian floodplain for wildlife. In: Johnson, R. Roy; McCormick, J.        Frank, technical coordinators. Strategies for protection and management        of floodplain wetlands & other riparian ecosystems: Proc. of the        symposium; 1978 December 11-13; Callaway Gardens, GA. Gen. Tech. Rep.        WO-12. Washington, DC: U.S. Department of Agriculture, Forest Service:        318-331.  [4367]  3.  Bainbridge, David A.; Virginia, Ross A. 1990. Restoration in the Sonoran        Desert of California. Restoration and Management Notes. 8(1): 3-14.        [14975]  4.  Barth, R. C.; Klemmedson, J. O. 1982. Amount and distribution of dry        matter, nitrogen, and organic carbon in soil-plant systems of mesquite        and palo verde. Journal of Range Management. 35(4): 412-418.  [2980]  5.  Benson, Lyman; Darrow, Robert A. 1981. The trees and shrubs of the        Southwestern deserts. Tucson, AZ: The University of Arizona Press.        [18066]  6.  Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals,        reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's        associations for the eleven western states. Tech. Note 301. Denver, CO:        U.S. Department of the Interior, Bureau of Land Management. 169 p.        [434]  7.  Berry, Kristin H. 1980. A review of the effects of off-road vehicles on        birds and other vertebrates. In: DeGraaf, Richard M., technical        coordinator. Management of western forests and grasslands for nongame        birds: Workshop proceedings; 1980 February 11-14; Salt Lake City, UT.        Gen. Tech. Rep. INT-86. 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