dcsimg
Image of big saltbush
Creatures » » Plants » » Dicotyledons » » Amaranth Family »

Big Saltbush

Atriplex lentiformis (Torr.) S. Wats.

Comments

provided by eFloras
Materials of big saltbush from the coastal and near coastal regions of California have somewhat broader, merely ovate, rounded leaves, and they have been regarded either at species level as Atriplex breweri S. Watson or at either varietal or subspecific level (see synonymy). The plants intergrade completely in interior situations with typical A. lentiformis, and their recognition at taxonomic level seems superfluous. C. A. Hanson (1962) noted the existence of putative hybrids between A. lentiformis and the herbaceous species A. leucophylla and A. davidsonii. Putative hybrids are also known between this species and A. canescens.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 4: 331, 369, 376, 377, 378 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Description

provided by eFloras
Shrubs, dioecious or less commonly monoecious, mainly 10-25(-35) dm, as broad or broader, unarmed or rarely so; branchlets terete, commonly puberulent. Leaves persistent, alternate, petiolate; blade gray-green, deltate to rhombic, ovate, or oblong-elliptic, 5-50 × 5-50 mm, base truncate to subhastate, margin entire to repand or subhastately lobed, apex rounded to obtuse, scurfy. Staminate flowers yellow, in clusters 1-2 mm wide, borne in panicles 0.5-5 dm. Pistillate flowers with less complex panicles. Fruiting bracteoles sessile, orbiculate to oval, greatly compressed, mainly 3-4.5 mm and wide, crenulate, apex rounded. Seeds brown, 0.8-1.6 mm wide. 2n = 18.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 4: 331, 369, 376, 377, 378 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Distribution

provided by eFloras
Ariz., Calif., Nev., Utah; Mexico.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 4: 331, 369, 376, 377, 378 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Flowering/Fruiting

provided by eFloras
Flowering spring-fall.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 4: 331, 369, 376, 377, 378 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Habitat

provided by eFloras
Saline to essentially non-saline drainages, stream and canal banks, roadsides, warm desert shrub, saltbush, and riparian communities; 70-1000m.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 4: 331, 369, 376, 377, 378 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Synonym

provided by eFloras
Obione lentiformis Torrey in L. Sitgreaves, Rep. Exped. Zuni Colorado Rivers, 169. 1853; Atriplex breweri S. Watson; A. lentiformis subsp. breweri (S. Watson) H. M. Hall & Clements; A. lentiformis var. breweri (S. Watson) McMinn
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 4: 331, 369, 376, 377, 378 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Common Names

provided by Fire Effects Information System Plants
big saltbush

big saltbrush

lenscale

len-scale saltbush

quail bush

quailbrush

white thistle
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Description

provided by Fire Effects Information System Plants
More info for the terms: cover, imperfect, seed, shrub

This description provides characteristics that may be relevant to fire ecology,
and is not meant for identification. Keys for identification are available [56,57,119,123].

Big saltbush is a large, perennial, native shrub. It typically grows to
between 3.3 and 8.2 feet (1-2.5 m) tall, but can reach 9.8 feet (3 m)
[8,57,79,90,119]. Plants are wide spreading
[25,113]. Individuals approximately 6.6 feet (2 m) tall were reported to
cover areas ranging from 5.6 m² to 7.8 m² [5],
and some plants reach coverages of up to 10 m² [79].
Big saltbush is typically evergreen, but can be
drought deciduous in some desert environments [25,28,113,119]. The numerous
leaves of big saltbush are somewhat thick, about 0.4 to 2 inches (1-5 cm) long,
0.25 to 1.5 inches (0.3-4 cm) wide, and covered in fine scales [8,25,113,119]. Big
saltbush branches are numerous and slender. The bark is typically covered in
fine scales when young and becomes rough on old trunks [113]. The small, imperfect flowers occur in
panicles [25,74,119]. The fruits are utricles with bracts typically 0.1 to 0.15 inch (3-4 mm) long and wide, which
contain a seed 0.04 to 0.06 inch (1-1.5 mm) wide [8,69,119].

license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Distribution

provided by Fire Effects Information System Plants
Big saltbush occurs from central California east into southern Nevada and
extreme southwestern Utah and south through western and central Arizona into
Baja California and Sonora, Mexico [8,57,73,119,123]. Quailbush is limited to
coastal regions of central and southern California and some nearby islands
[46,74]. Big saltbush's value as livestock forage and in disturbed site
rehabilitation are two major reasons for its introduction into several areas,
including Hawaii [8,55,65,109], Australia [6,60,62], and the Middle East [59]. Plants Database
provides a distributional map of big saltbush and its subspecies.
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Fire Ecology

provided by Fire Effects Information System Plants
More info for the terms: fire frequency, fire regime, forest, frequency, fuel, shrub

Fire adaptations:
Big saltbush produces abundant seeds [25] and is demonstrably fire resistant
(see IMMEDIATE FIRE EFFECT ON PLANT) [72,88].

FIRE REGIMES:
In desert shrublands fire is rare due to lack of continuous fuels
[67,82,100,120,121]. The expansion of invasive annuals
such as cheatgrass (Bromus tectorum) and red brome
(B. madritensis ssp. rubens) can increase the frequency of fire in these
ecosystems [121]. Fires in saltbush vegetation are likely to be more severe and spread
faster with increasing fuel porosity, decreasing levels of moisture, and
increasing amounts of fine fuels and dead vegetation [76].

Little is known of the role of fire in riparian habitats of the
desert Southwest. The flammability of riparian habitats would likely vary
temporally with drought and spatially due to fire frequency of surrounding
landscapes [110]. There is evidence that the fire frequency in riparian areas is
longer and more variable than that of the surrounding landscape [98,99,110]. Riparian
areas can slow or impede the spread of fire [29,98,99,104]. However, in drought
conditions higher fuel loads compared to other saltbush containing communities
(250 to 1000 lb/acre for mesquite bosque forest
compared to 40 to 100 lb/acre for saltbush/greasewood types [84]) can make
riparian areas more susceptible to fire [29]. Human ignitions sources
[29,110] and the invasion of tamarisk [16] will likely increase the frequency
of fire in these habitats.

The following table provides fire return intervals for plant communities
and ecosystems where big saltbush occurs. Find further fire regime information for the plant communities in which this
species may occur by entering the species name in the FEIS home page under "Find FIRE REGIMES".

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
coastal sagebrush Artemisia californica <35 to <100
saltbush-greasewood Atriplex confertifolia-Sarcobatus vermiculatus <35 to <100
paloverde-cactus shrub Parkinsonia microphylla/Opuntia spp. 84]
California steppe Festuca-Danthonia spp. 84,103]
creosotebush Larrea tridentata <35 to <100 [84]
mesquite Prosopis glandulosa <35 to <100 [68,84]

license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Fire Management Considerations

provided by Fire Effects Information System Plants
More info for the terms: frequency, severity

More research is needed to fully understand the ability of big saltbush to
recover from fire and recolonize burned areas. However, big saltbush is likely
to have the best chance of persistence when prefire plant moisture contents are high and fire
severity and frequency are low.
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Growth Form (according to Raunkiær Life-form classification)

provided by Fire Effects Information System Plants
More info on this topic.

More info for the term: phanerophyte

RAUNKIAER [91] LIFE FORM:



Phanerophyte
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Habitat characteristics

provided by Fire Effects Information System Plants
More info for the term: series

In the desert Southwest big saltbush occurs in valleys [108,123], along smaller
waterways, including outwash bajadas [119,123], on floodplains [63,79,123], in
alkaline flats [74,113,123], and in saline areas [25,74]. In coastal regions big
saltbush, most often quailbush, occurs in saline areas [25,74], floodplains,
and near the bottom of coastal bluffs [45,86].

Elevations where big saltbush
occurs range from sea level [90] up to 4,000 feet (1,219 m) in Arizona and
Mexico [57,90]. Elevational ranges by state are shown below.

Arizona <
4,000 feet (1,220 m) [57]
California <
2,000 feet (610 m) [25,74]
Utah
2,500 to 3,120 feet (760-950 m) [119]
Mexico
0 to 4,000  feet (0-1,220 m) [90]

Temperature:
The optimal temperatures for big saltbush depend on the location of the
populations sampled. It has been demonstrated that for big saltbush
in coastal areas, temperatures below 97 °F (36 °C) result in higher CO2 uptake than big
saltbush in desert areas. However, above 97 °F (36 °C) big saltbush in desert
areas have more efficient CO2
uptake. Photosynthesis is most efficient at 111 °F (44 °C) [86]. Big saltbush
in desert areas have been shown to have a greater capacity to acclimate to high
temperatures [87]. For effects of temperature on germination see Germination.

Soil:
Big saltbush is typically found in moist to dry alkaline or saline soils
[37,57,90,111], and has low tolerance for acidity [90]. The range of pH and electrical conductivity found on 3 sites,
one in southwestern Utah and two in Nevada, containing big saltbush are shown in the table below [111].

pH Electrical Conductivity (mmhox/cm)
7.5-8.3 0.8-3.1

Values of pH and electrical conductivity measured on sites near Safford,
Arizona, where big saltbush was grown to test its use as a forage crop, are shown
in the table below [117].

Sample Date pH Electrical Conductivity (dS/m)
Pre-irrigation Mar. 1984 7.5 1.3 (s=0.3)
Furrow top June 1984 7.3 68.2
(s=20.2)
Furrow bottom June 1984 7.6 48.7
(s=24.1)
Post-irrigation Jan. 1985 7.9 9.6
(s=6.7)

Big saltbush occurs in a variety of soil textures from quite coarse soils,
especially in the case of the quailbush, which can grow in pure sand
[96] to silty loams and silty clay loams [63]. Big
saltbush was established in an area of revegetation with sandy loams [80].
Turner and Brown [108] note the occurrence of the saltbush series, a
community type containing big saltbush, in areas with soil textures that are
generally finer than sandy loams. Marks [63] reports saltbush communities
typically growing in soils with intermediate textures, such as silty loams to
silty clay loams. Soils with poor aeration can result in severe growth
limitations in big saltbush [6]. Soil texture has not been shown to have a
significant (p>0.05) effect on germination [125]. See the Germination and Seedling establishment/growth
sections for more information on factors affecting big saltbush in these stages.

Water:
Big saltbush may grow in areas with or without an accessible
water table [37,41,57,66]. In California, Pearcy and Harrison [86] found moist soil at depths between
7.9 to 15.8 inches (20-40 cm) on a desert and a coastal site containing big
saltbush. In an experiment investigating water use of several species, big saltbush was
grown in tanks with an experimentally set water table depth of between 3.3 and 5.5
feet (1-1.7 m) [66]. According to McDonald
and Hughes [66] big saltbush has
been found on sites with deep water tables. These plants are likely to survive on surface sources of soil moisture
and be less vigorous than specimens that occur in areas with a shallow water table.

Big saltbush can tolerate drought and flooding. Precipitation in areas with big
saltbush can be very low. For instance, Goodin and McKell [41] noted their
observation of big saltbush occurring in
conditions of 3.9 inches (100 mm) mean annual precipitation.
A catalog of native seeds recommends planting in areas which
receive at least 4 inches (101.6 mm) of rain per year [90]. Although these areas may not
typically receive much rain, big saltbush occurs in areas, such floodplains and
valley bottoms that are subject to flooding [108]. Big saltbush has been
classified as flood tolerant. It can survive flooding for most of a growing
season, with some root growth likely during this period [115].

Big saltbush can also tolerate irrigation with saline water. Electrical
conductivity and pH of water used to irrigate big saltbush at a site near
Safford, Arizona were measured twice during a study investigating its use as a forage
crop. In May of 1984 the water had an electrical conductivity (EC) of 10.3 dS/m
and a pH of 8.6. In September 1984 the electrical conductivity was 9.3 dS/m and
the pH was 8.8 [117]. The feasibility of irrigating big saltbush with saltwater has also been
investigated. Wiley and others [124] used big saltbush from a
site irrigated with seawater discharge from a shrimp aquiculture facility in
Sonora, Mexico. They reported total dissolved salts of 40 parts per trillion (ppt); typical levels for
seawater are between 30 to 35 ppt. In another investigation in the same area
using the same water source (hypersaline, 39%-41%), the growth rate of big
saltbush was less than that for sites irrigated with freshwater in Bodega Head and Death
Valley in California. However, mean annual productivity was 1,794 grams of dry
weight/m² (mean = 149), which is similar to the more
northern sites due to the longer growing season in Sonora [38]. See Palatability/nutritional value
for more information on the forage production of big saltbush.
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Habitat: Cover Types

provided by Fire Effects Information System Plants
More info on this topic.

This species is known to occur in association with the following cover types (as classified by the Society of American Foresters):

More info for the term: cover

SAF COVER TYPES [33]:





235 Cottonwood-willow

242 Mesquite
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Habitat: Ecosystem

provided by Fire Effects Information System Plants
More info on this topic.

This species is known to occur in the following ecosystem types (as named by the U.S. Forest Service in their Forest and Range Ecosystem [FRES] Type classification):

More info for the term: shrub

ECOSYSTEMS [36]:





FRES30 Desert shrub

FRES33 Southwestern shrubsteppe

FRES34 Chaparral-mountain shrub

FRES42 Annual grasslands
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Habitat: Plant Associations

provided by Fire Effects Information System Plants
More info on this topic.

This species is known to occur in association with the following plant community types (as classified by Küchler 1964):

More info for the term: shrub

KUCHLER [61] PLANT ASSOCIATIONS:





K027 Mesquite bosques

K035 Coastal sagebrush

K036 Mosaic of K030 and K035

K040 Saltbush-greasewood

K041 Creosote bush

K042 Creosote bush-bur sage

K043 Paloverde-cactus shrub

K048 California steppe

K058 Grama-tobosa shrubsteppe
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Habitat: Rangeland Cover Types

provided by Fire Effects Information System Plants
More info on this topic.

This species is known to occur in association with the following Rangeland Cover Types (as classified by the Society for Range Management, SRM):

More info for the terms: cover, grassland, shrub, woodland

SRM (RANGELAND) COVER TYPES [97]:




203 Riparian woodland

205 Coastal sage shrub

211 Creosote bush scrub

215 Valley grassland

217 Wetlands

414 Salt Desert Shrub

501 Saltbush-greasewood

505 Grama-tobosa shrub

506 Creosotebush-bursage

507 Palo verde-cactus
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Immediate Effect of Fire

provided by Fire Effects Information System Plants
More info for the terms: shrubs, wildfire

In laboratory
experiments, big saltbush has been shown to exhibit reduced flammability
compared to highly flammable chaparral shrubs [72] and plants with lower
silica-free mineral content than big saltbush [88]. The effects of wildfire or
prescribed burns on big saltbush have not been
investigated.
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Importance to Livestock and Wildlife

provided by Fire Effects Information System Plants
More info for the terms: cover, fresh, natural, shrubs

Big saltbush is important forage and cover species for wildlife and is used
to some extent as livestock forage.

Palatability/nutritional value:
Leaves and seeds of big saltbush are eaten by many species. Mule deer,
pronghorn, and livestock browse the leaves [6,25,57,84,94,113]. In literature
reviews, small mammals such as rabbits and rodents have been reported to eat
big saltbush [44,84]. Briggs and Cornelius [13] report rabbit damage to big
saltbush in a revegetation plot and Everett and others [32] report that,
although big saltbush was one of the least preferred species in their laboratory trials, deer
mice ate its seeds. Reviews have included big saltbush as a component
of the diet of several game birds [30,44]. In a literature review, Gullion [44]
noted use of big saltbush by ring-necked pheasants and Gambel?s quail.
Big saltbush is also important to some insects. The saltbush sootywing uses big
saltbush as one of its hosts as a caterpillar and feeds on the nectar of big
saltbush flowers as an adult [81].

Several studies have investigated the nutritional content of big
saltbush. Cibils and others [23] found the mean and range of several
nutritional measurements available in the literature. These are shown in the
table below and represent values for a number of saltbush species.

Mean Range
Crude Protein 17.7% 5.6%-24.2%
Fiber 30.3% 12.3%-36.0%
Cellulose 20.8% 12.5%-29.0%
Mineral Content 16.6% 4.2%-29.0%
Gross Energy 3.9 Mcal/kg 3.4-4.3 Mcal/kg

Although the values from several studies specifically investigating big
saltbush fall within these ranges [22,59,124], there are exceptions. For example, gross energy
reported by Wiley and others [124] was less than that reported
in the Cibils and others's literature review [23]. Wiley and others found 3.1 Mcal/kg in untreated big saltbush
and 3.9 Mcal/kg gross energy in washed big
saltbush. This data was obtained from big saltbush irrigated with highly
saline water (40 ppt) [124]. Khalil and others [59] included digestible energy, which was 3.215 Mcal/ Kg, and
metabolizable energy, which was 2.636 Mcal/ Kg. They also found a lower fiber
content, 8.0% dry weight [59], than the minimum reported by Cibils and others
[23].

Wiley and others [124] and Khalil and others [59] included other big
saltbush measurements. Wiley and others [124] reported mean ash content
measurements of 37.4% dry matter for untreated big saltbush and 21.7% dry
matter for washed big saltbush, while Khalil and others [59] found an
ash content of 22.0% dry weight. In addition, both of these studies measured acid detergent
fiber (ADF). Wiley and others [124] found an ADF of 23.2% dry matter in untreated big saltbush and 27.5%
dry matter in washed big saltbush, while Khalil and others [59]
measured ADF as 18.5% dry weight. Wiley and others [124] measured neutral detergent fiber as
41.6% dry matter for untreated big saltbush and 53.6% dry matter for washed big
saltbush. Khalil and others [59] included the results from their measurement of
digestible dry matter, which was 74.5% dry weight. They also measured several
important minerals. The results are included in the table below [59].

Na K Ca P Mg Fe Zn Cu Mn
Dry weight (%)
?g/g
4.91 2.76 1.12 0.28 0.79 250 59 26 75

Other studies investigating nutritional values of big saltbush included results over time
or variations due to site conditions, such as high salinity. Two studies have addressed the
effect of time on nutritional content of big saltbush. The table below
shows the results of Goodin and McKell [41] from two harvests in percent dry
weight.

Harvests at 45 cm height Protein Ash Fiber Nitrogen-free extract Fat Ca P Total carbohydrates
1st harvest (June) 16.9 31.6 8.5 40.2 2.8 1.00 0.21 2.9
2nd harvest (Sept.) 14.6 23.9 17.9 41.0 2.6 1.08 0.17 -

Watson and others [117] found an effect of harvest treatment and
phenological stage on the nutritional content of big saltbush. Like Goodin and
McKell [41] they observed a decrease in ash and protein contents over time. The
table below shows nutritional information determined by Watson and others
[117] from harvests of aboveground plant material when plants were harvested near 60 cm tall. All
measurements are shown in percentages of dry weight, except fluoride, which is in ppm.

Weeks after transplanting Crude Protein Ash Neutral- detergent fiber Acid-detergent fiber Ca P F Oxalate
11 15.1 18.4 43.2 29.1 1.05 0.14 12.0 4.49
18 9.1 15.3 56.8 38.5 0.94 0.10 7.0 3.68
28 5.6 11.0 64.8 42.6 0.67 0.07 3.0 2.78

Salinity has also been shown to have an effect on nutritional aspects of big
saltbush. Ibrahim [50] measured the contents of several minerals in four salinity treatments. The results of this
investigation, in percent dry weight, are shown in the table below.

Treatment Ash Ca Mg Na K
Control 16.7 0.4 1.3 1.7 2.9
~ 12 dS/m 22.9 0.7 1.6 1.7 4.2
~ 24 dS/m 32.6 1.0 2.1 2.6 5.4
~ 36 dS/m 36.8 2.3 2.2 2.8 6.3
Mean 27.3 1.1 1.8 2.2 4.7

The following table shows the ion contents in mol/g of dry weight for several durations of
salinity treatments found by Malcolm and others [62]. The 1st number in each column is the
result for the low salinity treatment of 160 mS/m, while the 2nd number is
from the high salinity treatment, 1,900 mS/m.

Duration of Salinity (days) Ca Mg Na K
0 50/--- 80/--- 140/--- 120/---
0.5 60/50 80/90 20/60 70/60
3 60/50 70/90 20/80 80/70
6 100/60 100/120 50/300 260/190
12 200/100 170/280 140/1710 60/470

Toxicity of big saltbush may be a problem in some areas. Concern over selenium and oxalate
levels have been addressed. In a literature review Guillion [44] notes that saltbush species can reach toxic
levels of selenium. In a laboratory study soil was injected with 3
mg sodium selenate per kilogram of soil. This was repeated every ten days until
the soil had been injected with 18 mg of Se/kg of soil. The harvested big
saltbush contained selenium at a concentration of 7 ppm, while the combined,
root free soil had a concentration of 2 ppm. These selenium levels in big saltbush could
be toxic if it comprised the majority of the diet [27].
Glenn and O'Leary [38] measured oxalate levels and
found mean of 3.57% dry weight. The highest oxalate values Watson and
others [117] obtained was 4.57% dry weight. This was considered nontoxic.
Watson and others [117] also determined that fluoride
levels were sufficiently low.

In addition to the possibility of toxicity, there are other disadvantages of
use of big saltbush as a forage species that should be addressed when
considering its use. It has been found to lack phosphorus [117] and
carbohydrates [41]. Other authors have noted the high levels of ash [38]
and salts, especially sodium [38,50,59]. Acceptability of big saltbush
is also an issue. Domestic goats found diets with 25% big saltbush (leaves and smaller
stems) palatable, but big saltbush had been shown in previous investigations to have low
acceptance when comprising larger proportions of the goat diet [124]. The Cibilis and
others's [23] literature review also addressed the issue of adaptation to the
diet. They suggest that if a period of adjustment is necessary for animals to
uptake the nitrogen in big saltbush, as some evidence suggests, saltbush
species may be much less useful in filling gaps in food availability.
Despite these concerns most agree that big saltbush is valuable
forage for livestock, when not the sole food source [41,59,117,124].

In addition to the nutrition value, productivity of big saltbush is another
attribute which increases its forage potential. Ibrahim [50] notes that big saltbush can produce over five kilograms of
dry matter every 3 months. Goodin and McKell [41] reported
yields from big saltbush planted as a forage crop. Fresh weight yields (kg/ha) for
various harvesting strategies are included in the table below.

1st 45-cm harvest 2nd 45-cm harvest 60-cm harvest 75-cm harvest Season mean
8,626 5,518 15,076 16,009 15,076

They found no statistically significant (p > 0.05) advantage of harvesting twice when plants reached 17.7
inches (45 cm) compared to harvesting once at 23.6 or 29.5 inches (60 or 75 cm) height. Watson and others [117]
also determined there was no advantage to harvesting more than once during the
establishment year. The highest estimated yield of big saltbush they obtained
was 14.7 tonnes/hectare. In addition, transplant survival of big saltbush was
high [117]. In a later investigation, Watson and O'Leary [116]
found yield rates of 6.3 t/ha, 9.3 t/ha, and 3.5 t/ha in the subsequent harvests.
Only one treatment with saline water (EC
18 dS/m) occurred before the first harvest, but thereafter the
irrigation water had a mean electrical conductivity of 18 dS/m.
The drop in the yield of the third harvest reflected loss of individuals from
previous harvests [116]. Glenn and O'Leary [38] measured the productivity of
big saltbush when irrigated with hypersaline (39%-41%) seawater and obtained
an estimate of 794 grams of dry weight/ m2/ year (s=149) over a
year, which was similar to productivities of big saltbush irrigated with
freshwater on sites with shorter growing seasons. Despite encouraging results
with forage crops, sustainable browsing of livestock on natural stands of big saltbush is
complex. According to the Cibils and others [23] literature review,
the processes of recruitment and mortality in saltbush species are more
sensitive to changes than other shrubs. Care must be taken to incorporate
both the effects of herbivory and its interactions with intra- and interspecific
"competition" of the plant species when managing these communities.

Cover value:
Dense stands of big saltbush provide excellent cover for several species. Most work has
investigated avian use of big saltbush. Anderson and others [3] found that plots with
big saltbush had higher avian densities (p<0.05)
than vegetatively similar sites without big saltbush in 3 out of the 4 seasons investigated.
Species including blue grosbeak,
blue-gray gnatcatcher, Crissal thrasher, ruby-crowed kinglet, Gambel's quail,
and verdin had higher densities on sites with big saltbush [3]. Similar studies
have found comparable results [2,28]. Disano and others [28] found that densities of several
avian species and guilds, such as
passerine granivores, Gambel quail, and to a lesser extent permanent residents
and visiting insectivores, were higher in areas where big saltbush and Mohave seablite
coverage was approximately 1,500 plants per hectare compared to densities
averaged over all riparian vegetation types along the lower Colorado River. Gullion [42]
lists big saltbush as one of several species in habitats that provide
excellent Gambel quail cover. In a literature review he notes big saltbush's
importance to Gambel's quail in southern Nevada [44]. Ohmart and Anderson [79] note the
possibility of high densities of foliage arthropods contributing to the high
avian habitat quality of big saltbush, although the mechanisms behind the
interaction between big saltbush and avian populations are uncertain. In
addition to providing anecdotal evidence suggesting that big saltbush
revegetation efforts improved habitat quality to the point of allowing for
successful establishment of Gambel's quail, Ermacoff [30] reported
an increase in ring-necked pheasant activity and populations as well as increased cottontail
populations. Little else has been published regarding small mammal use of big
saltbush. However, information on rodent use of saltbush vegetation in
general is available [1].
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Life Form

provided by Fire Effects Information System Plants
More info for the term: shrub

Shrub
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Management considerations

provided by Fire Effects Information System Plants
Vines [113] notes that big saltbush is a suspected hay fever plant.
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Other uses and values

provided by Fire Effects Information System Plants

Quailbush is used as a hedge plant in coastal
California [96,113].

Traditional Uses:
Castetter's [21] literature review of studies on tribes of
the American southwest included information regarding the Pima Indians' practice
of pit curing and drying big saltbush seeds before using them to make a thick gruel.
Bean and Saubel [7] report a similar practice among the Chauilla as well as
use of the flour to make small cakes, use of leaves as a soap, and use of flowers,
stems and leaves as a treatment for nasal congestion. Conrad [25] suggests that seeds were
likely used in a similar way to fourwing saltbush. Seeds of fourwing saltbush
were also reportedly ground into flour. Other uses for fourwing saltbush that
may have been similar for big saltbush are the use of the ground meal as an
emetic, use of ground flowers or roots moistened with saliva in treating ant
bites, and addition of ashes to water for dyeing meal greenish-blue [25].

license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Phenology

provided by Fire Effects Information System Plants
More info on this topic.

Big saltbush flowers from mid- to late summer, with fruits maturing in September
and October [8,25,74,113].
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Plant Response to Fire

provided by Fire Effects Information System Plants
More info for the term: seed

Big saltbush can survive at least some fires
[16]. The limited information available suggests that the most likely
POSTFIRE REGENERATION STRATEGY of big saltbush is seed production [25,100]. In addition, a
study investigating its use as a forage crop demonstrated big saltbush survival
and growth after a harvest of over 50% of the vegetation [117]. Although fire may elicit a different
response, it is possible that big saltbush can persist after substantial damage.
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Post-fire Regeneration

provided by Fire Effects Information System Plants
More info for the terms: adventitious, secondary colonizer, seed, shrub

POSTFIRE REGENERATION STRATEGY [102]:




Shrub without adventitious bud/root crown

Secondary colonizer (on-site or off-site seed sources)
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Regeneration Processes

provided by Fire Effects Information System Plants
More info for the terms: cotyledon, dioecious, formation, monoecious, seed

Big saltbush reproduces by seed [25,79].

Breeding system: Big saltbush
can be either monoecious or dioecious [113,119,123]. In plantings done to
determine potential of big saltbush as a forage crop the sex ratio was 60% male
plants, 10% female plants, and 30% monoecious plants [117]. In their 1984
article, Freeman and others [35] included data from previous research
demonstrating change of sex in big saltbush. Plants typically change from
dioecious to monoecious, but can also change from female to male. The ability to
change sex appeared to enhance survival and may provide a reproductive advantage
to the population. The table below shows the number of individuals from a wild
population of 70 that exhibited each type of change in sex between 1978 and 1983
[35].



Type of Change in Sexual Morphology
Number of individuals
Female to male or female to monoecious to male 9
Female to monoecious 9
Male to monoecious 5

Pollination:
According to Meyer [69] saltbush
species are wind pollinated, but evidence demonstrating this for big saltbush
is lacking. Saltbush sootywing butterflies feed on
big saltbush nectar [81]. Whether they or
other insects transfer pollen while feeding is not reported.

Seed production:
Big saltbush has been reported to produce an abundance of seeds [25],
but quantitative data illustrating this are not available.

Seed dispersal:
Ohmart and Anderson [79] note that seed dispersal
occurs mainly by water and vertebrates. Several species, including ring-necked pheasants and
Gambel's quail, are known to eat big saltbush seeds [25,44], but there is no research
addressing bird dispersal of big saltbush seeds.

Seed banking:
Again there is little information available. However, seeds have been successfully stored in
sealed containers for 5 years [8]. Jorgensen
[53] reports a maximum storage time of 6 years.

Germination:
In laboratory studies, big saltbush germination rates have varied. Watson and
others [118] obtained average germination rates of 7% one year and 57% the following
from four replicates of 25 seeds incubated on a 68/100 °F (20/40 °C) diurnal temperature regime. Seeds
were collected in the fall and winter of both years. In low salinity treatments Jackson and others
[51] found 21% to 24% mean germination rates of seeds with utricles removed, and Young and others [125]
report a mean germination rate of 39% to 40% over 55 different temperature
treatments ranging between 32 °F and 104 °F (0 and 40 °C). Malcolm and others obtained high germination rates, above 80%,
with big saltbush seeds that had their utricles removed [62].

Thorough studies on the effect of temperature on big saltbush germination
have been performed. Young and others
[125] investigated the effects of 55 different alternating and constant
temperature regimes on big saltbush germination. They obtained the best
germination rates, between 65% and 68%, when the 8-hour warm period temperature
was between 68 °F and 86 °F (20 and 30 °C) and the 16-hour cold period temperature was between
41 °F and 59 °F (5 and 15 °C). No germination occurred when warm and/or cold period temperatures
were below 41 °F (5 °C). When both were 41 °F (5 °C) the mean germination rate was 5%. The only
other temperature regimes that resulted in no germination were at warm-period
temperatures of 104 °F (40 °C) when the cold-period temperature was 95 °F (35 °C) or higher.
Mean germination was 6% when
both warm and cold period temperatures were 95 °F (35 °C). All
other temperatures resulted in germination greater than 20%. Results are from
4 replications of 100 seeds each [125]. Young and others
[125] did not find a significant effect (p>0.01) of light on big saltbush germination. Mikhiel and others
[70] found the highest germination rate with a treatment in which seeds were
exposed to 50 °F (10 °C) and 68 °F (20 °C) each for 12 hours per day. The germination rates for
the 3 treatments are shown in the table below [70].

5 and 15 °C 10 and 20
°C 20 and 30
°C
41% 47% 32%

In addition to temperature, salinity has a strong influence on germination
rates. Jackson and others [51] observed no big saltbush germination in salinity
treatments of 18,000 mg/L and higher. At salinity levels of 6,000 mg/L and
lower, mean big saltbush germination rates were between 21% and 24%. The table
below shows the germination rates of big saltbush subject to 4 salinity
treatments [50].

control ~12
dS/m
~24 dS/m
~36 dS/m
47.2% 25.2% 23.8% 14.3%

Differences between the control and the 3 salinity treatments were significant
(p<0.05), while the
differences between salinity treatments were not statistically significant. The
germination rate at the ~24 dS/m salinity level was significantly (p<0.05) higher than other
saltbushes tested, including cattle saltbush and fourwing saltbush [50]. Mikhiel and others
[70] also determined germination rates for big saltbush at 4 salinity levels;
their results are shown in the table below. Unlike many other species
investigated, big saltbush does not exhibit a significant synergistic effect of
temperature and salinity [70].

0.0 M
0.05 M
0.20 M
0.40 M
63%
66%
31%
1%

In the field, estimates for germination rates are from
rehabilitation plantings. For example, in a review of several revegetation
projects, Biggs and Cornelius [13] report that germination of big saltbush on
the Cibola National Wildlife Refuge in Arizona was initially high, with over 1,000
seedlings produced on four 19.7-foot à 29.5-foot (6- à 9-m) plots. Anderson and others' [3]
first attempt at establishing big
saltbush on the lower Colorado River, by broadcast seeding, was almost entirely
unsuccessful. The table below shows big saltbush percent germination per meter of
seeds planted in loam in watered areas along the lower Colorado River in their
third attempt to establish big saltbush. The number of meters sampled per site
is shown in parentheses [3].

  Site 1 Site 2 Site 3
Nov. 6 9.4 (35) 2.8 (36) 9.9 (20)
Mar. 6 5.6 (31) 4.0 (64) 6.8 (11)

Seedling establishment/growth:
Big saltbush can successfully establish on many types of sites [3,13,30,41,60,80].
After 1 growing season in the northern portions of the Crescent Bypass
riparian revegetation area, about 34 miles (56 km) south of Fresno, California, most big saltbush
had grown quickly and survival was 88% [80]. In a review of
revegetation projects, Briggs and Cornelius [13] report that some big
saltbush grew to over 3 feet (1 m) and were producing seed after 3 growing seasons
at Mittry Lake in Arizona. In rehabilitation plantings in western Australia, big
saltbush had relatively high establishment compared to several other saltbush
species and reached 14.6 inches (37 cm) tall and 40.6 inches (103 cm) diameter after 2 years' growth [60].
Three years following planting of quailbush in San Onofre State Beach, California, coverages reached 11.9% on a site that had
been hydroseeded and 13.8% on a site that had been broadcast seeded and raked
[48].

Despite the ability of big saltbush to tolerate drought, establishment and
survival are probably improved with greater availability of water. Young big
saltbush plants have been reported to be more susceptible to drought (Anderson
and Ohmart, personal communication in [58]). Goodin and McKell [41] noted a lack
of regeneration when subject to only 3.9 inches (100 mm) mean precipitation and
speculated that the dry conditions were interfering with seedling establishment.
Big saltbush growth to 6 feet (1.8 m) in height and diameter within a year was
documented in plantings done near the Fresno Slough from 1959 to 1960 [30].
Given the short distance to the slough, the water table was likely shallow and
plants were also irrigated during the summer months. In addition, Watson and
others [118] found a general trend toward larger numbers of big saltbush
establishing closer to the irrigation source. In 1992, they found 5 big
saltbush established per linear meter when 1.5 meters from the irrigation
source; this decreased with distance from the irrigation source. In 1993, a
drier year, less than 1 big saltbush established per linear meter when 1.5
meters from the irrigation source. Again establishment decreased as distance
from the irrigation source increased, although at a lower rate than observed in
1992 [118]. For more general information, see the Water section below.

High levels of salinity appear to affect seedling development. Jackson and
others [51] reported no effect of salinity on the growth of big saltbush
seedlings at salinity levels of 18,000 mg/L and lower. However at 36,000 mg/L
and 60,000 mg/L,  shoot biomass was significantly (p<0.05) less than the
6,000 mg/L and 18,000 mg/L treatments. The total stem growth over 120 days was
also significantly less (p<0.05) at 36,000 mg/L and 60,000 mg/L salinity levels
compared to less saline treatments. The effects of the higher salt
concentrations became larger over time. However, none of these salinity
treatments resulted in seedling mortality [51]. In addition, Malcolm and others
[62] found increased cotyledon width and more rapid formation of true leaves in
delayed salinity treatments, where big saltbush seeds were subject to a period
of low salinity (160 mS/m) before salinities were increased (1900 mS/m).



Asexual regeneration: There have
been no reports of big saltbush reproducing asexually in the wild.
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Regional Distribution in the Western United States

provided by Fire Effects Information System Plants
More info on this topic.

This species can be found in the following regions of the western United States (according to the Bureau of Land Management classification of Physiographic Regions of the western United States):

BLM PHYSIOGRAPHIC REGIONS [9]:





3 Southern Pacific Border

7 Lower Basin and Range

12 Colorado Plateau
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

States or Provinces

provided by Fire Effects Information System Plants
(key to state/province abbreviations)


UNITED STATES

AZ CA HI NV UT



MEXICO

B.C.N. Son.




license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Successional Status

provided by Fire Effects Information System Plants
More info on this topic.

More info for the terms: frequency, series, succession, woodland

Although little research has been done addressing the successional status of big
saltbush, it probably occurs in both early
and late successional stages.

In riparian areas, disturbances, typically floods, occur regularly. Johnson and others [52] note that
desert riparian communities that establish
after a disturbance typically have the same species assemblages as before the
disturbance. Species composition is influenced more by site characteristics, such as depth to water
table, than time since last disturbance. The frequency and intensity of
disturbances does affect which species can establish. For instance, consistent
flooding can allow for establishment of species that do not tolerate high
levels of salt [13]. This interaction between disturbance and site characteristics results in a
dynamic mosaic of vegetation types [18]. Whether flooding was recent or occurred some
time ago, big saltbush could occur on a site with appropriate conditions. Whether this trend would be
observed after other types of disturbances, such
as fire, has not been reported. However, Busch [16] was unable to detect
a postfire successional trend in burned cottonwood-willow woodland along the lower Colorado River.


Although healthy riparian forests of the Southwest may not exhibit Clementsian succession, changes
to disturbance regimes have resulted in changes in species composition.
In altered habitats, such as those with decreased water tables, decreased
frequency of flooding, and a resulting increase in fire, tamarisks (Tamarix
spp.) can replace native species over time [17,24], resulting in older sites
being dominated by dense stands of tamarisk [24]. Due to big saltbush being a
"vigorous competitor" on sites where it is already established, these areas may be less likely to
follow this pattern [28].However, the strong response of tamarisks after fire [16] could
negatively affect big saltbush exposed to increased fire
frequencies. For a comprehensive review of tamarisks see the
FEIS Tamarisk review
and Glenn [37].


Few studies have addressed succession in saltbush scrub. Karpiscak [54]
summarizes succession in
saltbush and creosotebush shrublands. Species typical of saltbush or
creosotebush vegetation typically recolonize
abandoned agricultural areas after a series of mostly invasive annuals. Russian-thistle
(Salsola kali) gives way to several mustard species
(Brassicaceae) after two or three years, which is followed by annual grasses.
Goldenbush (Isocoma spp.) and desertbroom (Baccharis sarothroides)
follow, and typically establish just before saltbush or creosotebush species
[54].

license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Synonyms

provided by Fire Effects Information System Plants
A. lentiformis (Torr.) S. Wats. var. breweri (S. Wats.) McMinn [113]

    = A. lentiformis ssp. breweri (S. Wats.) Hall & Clements [55]
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Taxonomy

provided by Fire Effects Information System Plants

The scientific name of big saltbush is Atriplex lentiformis (Torr) S.
Wats. (Chenopodiaceae) [55,57,73,74,119,123]. There are currently 2 recognized subspecies of big saltbush [55,74]:



A. lentiformis subsp. breweri (S. Wats.) Hall & Clements, quailbush

A. lentiformis subsp. lentiformis, big saltbush


Big saltbush may not regularly
hybridize, even though it occurs with several Atriplex species [46].
However, Hanson [46] reports hybrids of quailbush and beach saltbush (A. leucophylla)
and quailbush and Davidson's bractscale (A. serenana var. davidsonii) in the
collections of the California Academy of Sciences.

license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Value for rehabilitation of disturbed sites

provided by Fire Effects Information System Plants
More info for the terms: reclamation, seed, shrubs

Big saltbush is a recommended revegetation species in riparian areas throughout
its range [19] and has also been used in
revegetation projects in other habitats [10,60] and outside its native
distribution [60]. It has been
planted in projects with varied goals, including soil stabilization [10,60,90]
and improvement or creation of habitat and forage for wildlife [3,30,90]
and those with constraints, such as the need for quick growth [10,30,60] or revegetation sites
with high salinity [60,79,80,90,95]. In addition, Disano and others [28] state that big saltbush
is "a vigorous competitor" once
established and can reduce the costs of controlling tamarisk invasion on a site. Given the number
of uses of big saltbush, it is not surprising that its
inclusion in revegetation projects is widespread. In 1979 the 'Casa' cultivar became available for
California revegetation
projects [20]. In 1984 Carlson [20] reported that approximately 15,000
individuals were grown in nurseries annually and that foundation individuals for
seed orchards would be ready that year. Plummer [89] gives an estimate of 500 pounds
of big saltbush seeds sold annually [89]. In 1996, 5 of Utah's 13 seed
suppliers sold 100 pounds of big saltbush seeds.

Although pretreatment of seeds is not necessary for germination, some pretreatments
may enhance germination rates. For example, a month-long
afterripening period is suggested by Jorgensen and Stevens [53], and improved germination occurs if seeds are rinsed
or soaked and then wrung [8,125]. Young and others [125]
reported increases in germination rate of 20% or more in seeds that were
rinsed and wrung before planting when incubated at temperatures between 50 °F and 77 °F (10?-25 °C).
The maximum germination rate, just over 80%, was observed when rinsed and wrung
seeds were germinated at 68 °F (20 °C).

Conditions that improve germination include covering seeds with a small
amount of soil and germinating at optimal temperatures and salinities.
Depth of planting appears to be important factor for germination success. Goodin
[40] reports that big saltbush should not be planted at depths of more than 0.2
to 0.4 inches (5-10 mm). Also germination is significantly (p < 0.05) enhanced when a thin
layer of soil covers the seeds. The
table below shows germination rates for different soil types when seeds were
planted at either a depth of 0.2 inches (0.5 cm) or on the soil surface. Differences between soil types
were not statistically significant (p > 0.05) [125].

  Sand Loam Clay
Surface 0% 2% 2%
Buried 0.5 cm deep 28% 45% 56%

The ease of propagating saltbush species, including big saltbush from cuttings [64,77,122]
provides another method for production. Wieland and others [122] report
that cuttings of many of the saltbush species tested rooted without the
application of rooting hormone, although rooting success in big saltbush was
best when rooting hormone was used. Richardson and others [92] investigated
factors affecting rooting success of fourwing saltbush, shadscale, and valley
saltbush. They found that 4.7 inch (12 cm) cuttings had much higher rooting success than
2.4 inch (6 cm) cuttings, that
concentrations of rooting hormone between 0.3% and 2.0% had the best results
depending on the species, and that propagating cuttings in spring and summer
resulted in the highest success while propagating cuttings in fall had the
lowest success. In a study of 54 Nevada shrubs, big saltbush was one of
the easiest species to propagate from cuttings and had higher rooting success
when cuttings were semi-hardwood and/or collected during the stage of twig
growth [31].

Several methods and levels of effort toward subsequent maintenance have allowed
successful establishment of big saltbush. Hydroseeding [10,48], use of a niche
seeder [60], broadcast seeding then raking [48], and transplanting individuals
older than 9 months [95] have all resulted in successful establishment of big
saltbush. Briggs and Cornelius [13] provide a review of several revegetation
efforts; some of these plant big saltbush and planting methods used differ.
Given the susceptibility of young
saltbush to drought, irrigation during the first summer is likely to improve
establishment (Anderson and Ohmart, personal communication in [58]). Reductions in salinities, even for short
periods after planting, may also assist in establishing big saltbush [62]. For general information on effects of
water and salinity in big saltbush establishment see Seedling establishment/growth.
Fencing may be included to reduce
browsing [95], as several revegetation projects have reported losses from
livestock and small mammals such as rabbits and gophers [13,39,95]. Seed
predation by deer mice has also been investigated. Although not a preferred
species, big saltbush seeds may suffer from high predation rates when other
food sources are lacking [32]. Collection of seed from on-site sources is another
option. This is recommended for riparian revegetation efforts [58] and has
produced good results [10]. Seeds can be stored for a maximum of 3 to 6 years
[8,53,89]. Winter has been suggested as the best time for planting seeds
[58,90], while transplants 2 to 3 years old have been successfully planted
throughout the summer when irrigated [95].

Large rates of big saltbush mortality and low growth rates have been
reported, but the cause of these outcomes is unknown. For instance, on the third
attempt Anderson and others [3] successfully
established big saltbush on three watered sites along the lower Colorado River.
Mean growth rates from the time of planting to 6 months later were between 0.8
and 1.2 inches (2-3 cm). Big saltbush planted at a mine reclamation site exhibited 100% mortality.
Whether this was due to the level of soluble salts, which ranged between 335 and
3182 ppm, or some other factor or factors is not discussed [78].
license
cc-publicdomain
bibliographic citation
Meyer, Rachelle. 2005. Atriplex lentiformis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us/database/feis/plants/shrub/atrlen/all.html

Atriplex lentiformis

provided by wikipedia EN

Atriplex lentiformis (quail bush, big saltbrush, big saltbush, quailbrush, lenscale, len-scale saltbush and white thistle) is a species of saltbush.[2]

Distribution

Atriplex lentiformis is native to the southwestern United States and northern Mexico, where it grows in habitats with saline or alkaline soils, such as salt flats and dry lake beds, coastline, and desert scrub. It can also be found in nonsaline soils on riverbanks and woodland.

Description

Atriplex lentiformis is a spreading, communal shrub reaching one to three meters in height and generally more in width. It is highly branched and bears scaly or scurfy gray-green leaves up to 5 centimeters long and often toothed or rippled along the edges. This species may be dioecious or monoecious, with individuals bearing either male or female flowers, or sometimes both. Male flowers are borne in narrow inflorescences up to 50 centimeters long, while inflorescences of female flowers are smaller and more compact. Plants can change from monoecious to dioecious and from male to female and vice versa.[2]

This species blooms in June and July.

Uses

This saltbush species, A. lentiformis, and Atriplex canescens are the food plants for the saltbush sootywing Hesperopsis alpheus, a butterfly.[3]

Atriplex lentiformis is used in restoration of riparian habitats, one of the native plants in riparian zone restoration projects in its native ranges.[2]

Lower Gila River and Colorado River regions

Atriplex lentiformis grows in the Mesquite Bosque vegetative association with the native Arrowweed - Pluchea sericea, Velvet mesquite - Prosopis velutina, and others in the Lower Colorado River Valley and Gila River valleys of southwestern Arizona, southeastern California, and northwestern Mexico.

The maximum height occurs where a groundwater source supplies plentiful moisture, and saline soil conditions are optimal for the quailbush with other plants losing from the competition. However, the invasive species Tamarisk - Tamarix ramosissima and tumbleweed, Tumbling oracle - Atriplex rosea are successful and problematic competitors. The saltbush can reach 3.5 metres (11 ft) tall and wide in advantageous growing locales, with the form becoming a large flattened hemisphere, with adjacent hemispheres merging into an impenetrable thicket mass.

References

  1. ^ a b c Proc. Amer. Acad. Arts 9:118. 1874 "Atriplex lentiformis". Germplasm Resources Information Network (GRIN). Agricultural Research Service (ARS), United States Department of Agriculture (USDA). Retrieved December 5, 2009.
  2. ^ a b c d e Meyer, Rachelle (2005). "Atriplex lentiformis". Fire Effects Information System. Rocky Mountain Research Station, Fire Sciences Laboratory: USDA, U.S. Forest Service. Retrieved December 4, 2009.
  3. ^ "Butterflies and Moths: Saltbush Sootywing". Archived from the original on 2007-11-18. Retrieved 2008-11-27.

license
cc-by-sa-3.0
copyright
Wikipedia authors and editors
original
visit source
partner site
wikipedia EN

Atriplex lentiformis: Brief Summary

provided by wikipedia EN

Atriplex lentiformis (quail bush, big saltbrush, big saltbush, quailbrush, lenscale, len-scale saltbush and white thistle) is a species of saltbush.

license
cc-by-sa-3.0
copyright
Wikipedia authors and editors
original
visit source
partner site
wikipedia EN