In the United States, tropical soda apple is most common in Florida and has been reported in Texas, Arkansas, Louisiana, Mississippi, Alabama, Georgia, South Carolina, North Carolina, Texas, Tennessee, Pennsylvania [59,71,90,96], and Puerto Rico [13,71]. By 2002, researchers reported that tropical soda apple may have been eradicated from Louisiana, Tennessee, and Pennsylvania , so its occurrence in these states is uncertain. By 2007, many of the small infestations of tropical soda apple had been eliminated in Mississippi , so its spread may be on the decline in that state. Tropical soda apple was first collected in the United States in southern Florida between 1987 and 1988 and spread to other southeastern and mid-Atlantic states soon after [70,108]. Herbaria records show that it had spread to at least one county (Jasper County) in Texas by 2004 . Tropical soda apple has the potential to invade the remaining southern states and some central states including Colorado, Kansas, and Illinois . It may be able to overwinter as a perennial at or below 33° N latitude and may persist as an annual in cooler areas . Plants Database provides a distributional map of tropical soda apple in the United States.
Tropical soda apple's introduction likely occurred through the unintentional movement of plants or seeds from South America, although its exact means of introduction is unclear . The spread of tropical soda apple within Florida and to other southeastern states has been facilitated by movement of cattle, pasture grasses, and composted manure from infested areas [71,108].HABITAT TYPES AND PLANT COMMUNITIES:
Tropical soda apple occurs on wildlands and in native plant communities [26,52,68]; however, little information was available on specific plant associations as of 2009.
Florida: In Florida, tropical soda apple has been observed in native plant communities such as hammocks , hammock edges , cabbage palmetto (Sabal palmetto) hammocks, cypress (Taxodium distichum) heads or domes [26,68,74], depression marshes, riparian areas, and pinelands (Pinus spp.). Herbaria collections indicate that tropical soda apple occasionally occurs in strand swamps, scrub, and mesic flatwoods . Of these Florida communities, tropical soda apple is most commonly noted in hammocks and cypress heads.
Hammocks: Hammock is a general term for a forest clump or a narrow band of vegetation often dominated by evergreen tree species, often oaks (Quercus spp.) (, review by ). Tropical soda apple occurred in the understory margins of saw-palmetto (Serenoa repens) , a species commonly found on the perimeter of hammocks . Hammocks can be hydric, mesic, or xeric and are most frequently defined by their topographic location (e.g., high, middle, or low slope) rather than their moisture content. Hammocks vary in their plant species composition and distribution (, review by ) and most commonly contain temperate species, but they contain tropical species in the very southern parts of Florida (review by ). Canopies may be open or closed . Hammocks are typically embedded within larger plant communities such as prairies, marshes , or pastures .
Cypress heads: Cypress heads are shallow, forested, usually circular depressions. Because small trees grow in the shallow water at the outer edge and large trees grow in the deeper water in the interior , cypress heads generally present a symmetrical, domed profile . Important tree species include pondcypress (T. distichum var. imbricarium), swamp tupelo (Nyssa sylvatica var. biflora), slash pine (Pinus elliottii), red maple (Acer rubrum), and wax-myrtle (Myrica cerifera). There is a diverse understory of shrubs and forbs including laurelleaf greenbrier (Smilax laurifolia), fetterbush (Lyonia lucida), poison-ivy (Toxicodendron radicans), grape (Vitis spp.), gallberry (Ilex glabra), Virginia chain-fern (Woodwardia virginica), and cinnamon fern (Osmunda cinnamomea) [40,62].
Mesic flatwoods: Tropical soda apple occasionally occurs in mesic flatwoods, which are of interest from a fire perspective. Mesic flatwoods have relatively open overstories dominated by longleaf pine (P. palustris), typical slash pine (P. elliottii var. elliottii), south Florida slash pine (P. elliottii var. densa), and pond pine (P. serotina) [40,81]. Several variations of mesic flatwood are recognized and typically differ from one another in ground cover composition .
For a complete description of these and other Florida plant communities, see .
Other states: In other southeastern states, tropical soda apple is most invasive in pastures but also occurs in croplands and native plant communities. It invades oak hammocks and cypress heads in Mississippi, Alabama, and Georgia  and wooded areas in Mississippi (reviews by [11,16]). In Texas, it occurs in native grasslands and forested areas (review by ). As of this writing (2009), nothing had been published about tropical soda apple's plant associations in states farther north.Because tropical soda apple is a relatively new invader to North America, it may occur in or spread to plant communities not mentioned above.
Aboveground: In North America, tropical soda apple has been described as a broadleaf herb [23,69,102], subshrub , or shrub [59,108]. In India, it is considered a "woody" herb . It is generally a perennial where it occurs in warm climates [11,23,70] and may remain green over the winter [23,59]. In places that experience frost, tropical soda apple may be an annual . It typically grows from 3 to 6 feet (1-2 m) tall, and the leaves and stems are lined with thorn-like prickles up to 1 inch (2.5 cm) long . Leaves are 2 to 8 inches (6-20 cm) long × 2 to 6 inches (6-15 cm) wide . Its inflorescence is a 1- to 3- flowered cyme . Fruits are globular berries. They are typically about 0.8 to 1 inch (2-3 cm) in diameter at maturity , but viable seed may develop in ripe fruits as small as 0.4 inch (1 cm) in diameter  (see Germination). As fruits ripen, they transition from green to yellow . The seeds are lens-shaped  and about 2 mm long .
Belowground: The root system of tropical soda apple can be extensive. In Florida, feeder roots, which are 0.25 to 1.0 inch (0.63-2.54 cm) in diameter, are located a few inches below the soil surface and are about 3 to 6 feet (1-2 m) long . Roots examined on a site in Mississippi were up to 1 foot (30 cm) deep with lateral branched roots up to about 3 feet (1 m) long and 0.6 to 1 inch (1.5-2.5 cm) in diameter .
Population structure: Tropical soda apple is an aggressive invader. It rapidly populates new sites and may eventually form monocultures  that occur in patches of 10 acres (4 ha) or more . Prior to control efforts, tropical soda apple commonly occurred in monocultures of 50 acres (20 ha) or more in Florida [70,85]. Dense monocultures occur primarily in cultivated pastures and may be less frequent on rangelands and wildlands .Raunkiaer  life form:
In Florida, tropical soda apple flowers and produces fruit throughout the year [2,70], but both events may be more concentrated during certain times. Periods of high flower and fruit production may vary with location. In Florida, most flowering and fruiting occurs from September to May, with fewer fruits produced in summer [65,70]. Another report from Florida found most flowering and fruit production occurred from February to August . In Mississippi, tropical soda apple's flowering and fruiting period begins in June and continues until the first fall frost, with peak production occurring in August (Bryson and Byrd unpublished data cited by ). In its native and nonnative ranges outside North America, tropical soda apple has been reported to flower primarily from September to April . In parts of India where it is hot, tropical soda apple can be an annual that produces flowers 3 months after germination and mature berries in another 2 months .REGENERATION PROCESSES:
Although seed is the primary mechanism for tropical soda apple spread , it also sprouts from the roots [11,69] and possibly
from the root crown.
Photo by J. Jeffrey Mullahey, University of Florida, Bugwood.org
Seed production: Tropical soda apple is generally considered a prolific seed producer [27,59,70,75,85,102]; however, seed production may vary between populations. In Florida, 1 plant may produce, on average, 125 fruits containing 413 seeds. One mature tropical soda apple plant has the potential to produce >50,000 seeds annually . Cook  indicated fruit production may be greater in Mississippi than in Florida. Eight to 10 tropical soda apple plants in Mississippi have the potential to produce 1 million seeds annually . Seed production may be less in other parts of the world. In hot climates in India, tropical soda apple completes its life cycle in 5 months , which may contribute to its reduced seed production in parts of its range. Studies in India found that 1 tropical soda apple plant produced 30 fruits . A review on tropical soda apple populations outside North America indicates that a single tropical soda apple fruit may contain 190 to 385 seeds . Fruit production may be greater in plants on phosphate-rich soils than in plants on unenriched soils (see Seedling emergence and plant growth).
Seed dispersal: Tropical soda apple seed dispersal throughout Florida and into other parts of the southeastern United States has been largely facilitated by cattle and operations associated with the transport of livestock and feed [26,59,65,85]. Cattle eat tropical soda apple fruit and disseminate the seed via feces [10,23,63,70]. In Florida, cow manure contained 35,000 to 75,000 seeds/ton of dry manure . Tropical soda apple seed is spread long distances as a contaminant in hay, grass seed, and sod, and by moving water [12,68]. Tropical soda apple seed was probably dispersed from Florida to other states by interstate transport of livestock, primarily cattle .
Wildlife, primarily feral pigs, northern raccoons, and white-tailed deer, also eat tropical soda apple fruit and spread the seed through their feces [23,26,59,63,85]. While it has been suggested that birds eat tropical soda apple fruit , one review indicated that birds had not been observed feeding on the fruits and that birds may not serve as a vector for tropical soda apple's spread .
Tropical soda apple seed may be dispersed by equipment or human and other animal movement. The seeds contain a sticky substance that adheres to the undersides of mowers, tires, front grills, blades, and shoes. Contaminated mowers, vehicles, and other equipment can transfer seed to uninfested pastures . The seed may also adhere to animal fur, providing another means for tropical soda apple seed dispersal.
As of this writing (2009), it was uncertain what happens to tropical soda apple seeds that are not dispersed by animals or equipment. They are likely gravity dispersed and fall near the parent plant.
Seed banking: Available evidence suggests that tropical soda apple forms a soil seed bank in its North American range, but seed bank longevity is unclear. There may be little opportunity for seed bank formation in areas like southern Florida, where tropical soda apple seedlings emerge year-round.
In cypress heads, tropical soda apple may reestablish from a soil seed bank after mature plants are eradicated by flooding . Herbicides that prevent seedling establishment from the soil seed bank are preferred for tropical soda apple control (see Chemical control) . Dormancy may allow tropical soda apple to form at least a short-term soil seed bank. In Mississippi, 10% to 18% of tropical soda apple seed buried in a field and exposed to cold winter temperatures germinated and emerged when moved to the greenhouse the following spring , suggesting that tropical soda apple can form a seed bank until at least the following growing season. Tropical soda apple seed may deteriorate rapidly in soil [11,63], but viability may be extended if seed is protected from deterioration. Tropical soda apple seed placed in dry, dark storage in the laboratory for up to 12 months remained viable [63,78]. One review suggested that tropical soda apple seed may survive for 2 or more years if soil is relatively dry . Seed overwintering on the soil surface may be protected from deterioration if the fruit remains intact .
Because tropical soda apple is commonly dispersed by wildlife, sites where wildlife congregate—such as oak hammocks, roadsides, ditch banks, and other fallow areas— may contain a disproportionate amount of tropical soda apple seed in the soil seed bank .
Germination: In the laboratory, seed viability and germination rates were high for tropical soda apple seed sown under variable conditions. Germination in tropical soda apple is epigeal . While some seed may undergo a short period of dormancy, dormancy may not be required for germination. Fruit size may be a better determinant of seed maturity than fruit ripeness. Germination may be enhanced by scarification and may be sensitive to changes in temperature, light, pH, moisture availability, and fruit ripeness.
Fruit diameter may be a better predictor of seed maturity than fruit ripeness in tropical soda apple. Under laboratory conditions, tropical soda apple seedlings did not emerge from seed removed from ripe fruit <0.4 inch (1 cm) in diameter or from unripe fruit <0.6 inch (1.5 cm) in diameter. Seedling emergence increased proportionally with increased fruit diameter (r²=0.9), with maximum emergence (90%) occurring from ripe fruits that were ≥1 inch (2.8 cm) in diameter. Although seed from unripe fruit may be sufficiently mature to germinate, germination may be greater with seed of ripe fruit (yellow) than from unripe fruit (green) .
In Florida, viability of tropical soda apple seed is likely high [2,63]. Laboratory testing found that viability of tropical soda apple seed was 89%  to 98% . Viability of tropical soda apple seed collected from cow manure ranged from 80% to 90% , suggesting that seed viability may be minimally affected by digestion.
Most fresh seed is apparently viable, but some tropical soda apple seed may be dormant [2,63,88]. In the laboratory, tropical soda apple seed germinated in 6 to 7 days (Mullahey unpublished data cited in ). In the laboratory, 20% of tropical soda apple seed collected in Florida was dormant . Other researchers in Florida reported that 4% to 16% of tropical soda apple seed was dormant. However, no seed remained viable after 90 days . An unpublished study (Wahaj and others cited in ) suggested that solasodine, a poisonous substance found in Solanum spp. (see Palatability and/or nutritional value), may inhibit tropical soda apple germination.
Germination rates of 69%  to 82.5 % [10,70] have been reported for tropical soda apple in the laboratory, and scarification of seed coat may improve germination [2,10]. In the laboratory, germination of seed removed from fruit was 82.5%. Germination increased to 90% when seed passed through the digestive tract of cattle within 24 hours, indicating that scarification or partial digestion of the seed coat may increase germination rates. Seed taking longer than 6 days to pass through the digestive tract may no longer germinate . Although scarified tropical soda apple seed germinated more quickly than unscarfied seed, percent germination was reduced, presumably from injury to the embryo .
In the greenhouse, tropical soda apple seeds germinated in constant temperatures ranging from 50  to 95 °F (10-35 °C) [2,33]. Germination increased with increased temperatures up to 86 °F (30 °C), and declined thereafter. Germination did not occur at temperatures ≥104 °F (40 °C) or ≤41 °F (5 °C) . Germination may be stimulated  or percent germination increased (Vincente 1972 cited in ) with alternating temperatures. In India, tropical soda apple seed did not germinate at constant temperatures of 68 °F (20 °C) or 86 °F (30 °C), but 10% germinated when temperatures were alternated between these 2 temperatures. Germination rates increased up to 82% when seed was subject to dormancy-breaking acid treatments and exposed to the same alternating temperatures .
In Florida, optimal germination temperature for tropical soda apple occurs from October until March . Based on results obtained in the laboratory, researchers concluded that air temperature ranges in much of the southeastern United States may be sufficient to allow tropical soda apple seed to germinate year-round . Ferrel  indicated that tropical soda apple seeds germinate anytime soil temperatures are 41 to 104 °F (5-40 °C). This means that for states like Florida, with average monthly soil temperatures ranging from 64 to 100 °F (18-38 °C), tropical soda apple can germinate year-round .
Based on its associated habitats (see Habitat Types and Plant Communities and Site Characteristics), tropical soda apple seed may germinate in full light or in shade. In Florida, seedlings occurred along the margins of saw palmetto canopies , suggesting seeds may germinate in partial shade. Under laboratory conditions, tropical soda apple seeds germinate in the dark [2,63]. Light may stimulate germination in tropical soda apple (Vincente 1972 cited in ).
Other factors that may influence germination in tropical soda apple seed include pH and moisture availability. Moderately alkaline soils may promote germination. Although tropical soda apple seed germinated in buffer solutions when the pH ranged from 3 to 13, germination was highest (71%) when the pH was 8. Germination declined sharply when pH was greater than 8 . Tropical soda apple seed germinates across a wide range of moisture conditions and may germinate under moderate water stress, but the percent of seed germinating may decline . Germination may be low for tropical soda apple seeds on the soil surface (see Seedling emergence and plant growth).
Seedling emergence and plant growth: Available information suggests that seedlings begin to emerge shortly after seed is dispersed (see Seasonal Development), and plants can produce fruit in as little as 2.5 months. Seedling emergence may be greater for buried seed than for seed on the soil surface. Precipitation and geographic location may influence length of tropical soda apple's growing season.
In the greenhouse, tropical soda apple seed sown at various depths, ranging from the soil surface to about 3 inches (8 cm), began to emerge 6 to 7 days after planting. Fifty percent of seedlings emerged within approximately 15 days of planting . Seedlings emerged from all depths, but most (63%) emerged from seed buried about 1 inch (3.6 cm) deep. Fewest (7%) emerged from seed on the soil surface . In another laboratory study, seedling emergence was greatest for seed planted about 2 inches (6 cm) below the soil surface (63%) and did not occur for seed sown more than about 5 inches (12 cm) deep. As in the previous study, seedling emergence from seed left on the soil surface was low (6.9%) . Seedlings emerging from unburied seed may grow more slowly and have lower vigor compared to seedlings emerging from buried seed. The authors attributed reduced emergence of seed on the soil surface to dry conditions .
After seedlings emerge, growth and fruiting occur rapidly [55,69,80,95], especially when nutrients are sufficient . In the greenhouse, tropical soda apple seed planted about 0.4 inch (1 cm) deep germinated, grew to a height of about 8 inches (20 cm), and had an average of 20 leaves within 60 days after planting. During the next 60 days, tropical soda apple plants underwent a "rapid" increase in height. Wild tropical soda apples may grow more slowly than greenhouse plants. Seedlings in a Florida pasture took 60 to 80 days to get about 8 inches (20 cm) tall and only had 4 to 8 leaves/plant. Flowering time for pasture plants was 120 days compared to 75 to 83 days for greenhouse plants . Trenholm and others  reported substantial growth in tropical soda apple plants in pastures and hammocks during the first 125 days of growth. Some plants developed fruit at 75 to 100 days of age; most other plants developed fruit by 125 days. . In India, cultivated tropical soda apple plants mature within 5 months of germination  and have up to 4 to 6 leaves within 45 days of emergence . In the greenhouse, increases in phosphorus increased tropical soda apple plant height and fruit production .
Plants in pastures may be more productive than plants in wildlands (hammocks). In southwestern Florida, growth and nutrient accumulation were compared between tropical soda apple plants in a pasture and a hammock. Although plants in both habitats grew well, plants in the pasture produced at least twice as much dry matter as plants in the hammock. Hammock plants had more dry matter production apportioned to their stem tissue than pasture plants, and they expanded their root system faster than pasture plants, presumably to enhance nutrient uptake. Nutrient concentrations in tropical soda apple plants were similar, regardless of habitat. Nutrient concentrations varied between plant parts (e.g., stem, root) and plants of different age classes .
Tropical soda apple height and diameter may increase with increased precipitation, but fruit production may be unaffected . Tropical soda apple populations may increase "rapidly" when several years of normal rainfall follow a drought .
Growth of tropical soda apple may slow or stop during winter. In the laboratory, overall growth of tropical soda apple increased with increases in night temperature. A regression model was developed to predict growth potential of tropical soda apple throughout the United States. In most southern states, tropical soda apple may grow during much of the year; however, it was predicted that 30% or more of its maximum growth occurs from April through October. If tropical soda apple spreads farther north and west, it may grow at rates similar to those predicted for southeastern climates; however, its growth would likely be restricted to warm months .
Vegetative regeneration: New shoots sprout from tropical soda apple's extensive roots [11,102], root buds , and probably from its root crown. Regeneration from root segments can also occur [24,33,69] and may be influenced by segment size. In the greenhouse, 6-inch (15 cm) root segments produced significantly (P<0.02) more shoots than 2-inch (7.5 cm) root segments . Regeneration from rootstocks of the previous year may be limited to areas with mild winters or may occur after unseasonably warm winters in cooler climates .
Mature tropical soda apple plants that are cut or mowed may regrow from adventitious buds that develop on the callused tissue of the remaining stem apex. In a controlled experiment, tropical soda apple plants of various ages (1-55 days old) regrew from adventitious buds after cutting. The average percentage of 1-day-old plants that regrew after mowing was 75%. Bud formation was greater in 20-day-old plants than for plants cut 1 or 10 days after emergence, and a higher proportion of regrowth occurred on plants that were 25 days old than in plants that were cut sooner .SITE CHARACTERISTICS:
In its native range, tropical soda apple occurs in tropical climates and is found at low elevations, mostly below 300 feet (100 m) . In North America, it is "well suited" for warm temperatures ; however, it has spread to northern areas such as Pennsylvania, where January temperatures can fall to 28 °F (18 °C) or lower . Field tests indicated that tropical soda apple can survive as a perennial at winter temperatures ≤50 °F (10 °C) at 33 °N latitude and may survive colder temperatures as an annual . Germination of tropical soda apple seed may be influenced by soil temperature as well as air temperature.
In southern Florida, tropical soda apple may occur on seasonally wet soils ; however, it does not tolerate inundation for more than 3 weeks . Cypress heads support tropical soda apple until their centers become completely flooded; then tropical soda apple dies back to the outer, drier regions. As the water in the cypress head recedes during the dry season, new tropical soda apple plants establish from the soil seed bank and begin to occupy the inner regions of the cypress head . Tropical soda apple's ability to germinate under moderate water stress  suggests it could establish in dry habitats or during periods of moderate drought. Its ability to tolerate a range of environmental conditions (e.g., temperature, moisture) may allow tropical soda apple to persist during years that are unfavorable for reproduction .
Information pertaining to tropical soda apple's preferred substrate is limited. In Florida, tropical soda apple occurs in somewhat poorly drained , sandy soils [12,36,61]. In an experimental field in Florida, it occurred in soils that were 96% to 99% sand and contained a small percentage of silt and clay . On 5 sites in Mississippi, tropical soda apple grew in sandy loam soils . In bahia grass pastures, where tropical soda apple can be abundant, soil pH is maintained from 5 to 7 . Alkaline conditions may favor germination. Tropical soda apple may flourish in soils rich in phosphorus [3,17].SUCCESSIONAL STATUS:
In North America, tropical soda apple grows in open and shaded sites, as evidenced by its occurrence in both pasture and wooded plant communities (see Habitat Types and Plant Communities), and seedlings may establish in shade (see Germination). One review suggested that tropical soda apple preferred open to semishaded sites , suggesting it may be intolerant of deep shade. In Mississippi, some tropical soda apples were observed in shade, but most were in full sunlight .Tropical soda apple occurs in oak hammocks, cypress heads, and other plant communities in Florida and the southeastern United States (see Habitat types and plant communities); however, nothing has been documented about its successional status in these communities as of 2009. General information pertaining to successional patterns in Florida's plant communities is available in these publications: [40,81].
Fire adaptations and plant response to fire: As of this writing (2009), no published information was available on fire adaptations of tropical soda apple or its ability to establish after fire. Tropical soda apple's ability to regenerate vegetatively, produce abundant seed, and establish on disturbed sites suggests that fire may favor its spread. Postfire establishment may occur by vegetative regeneration or by seed. There is potential for postfire sprouting to occur from roots, root buds, and possibly the root crown. Tropical soda apple is known to sprout from adventitious buds on the stem apex after being cut and may do so after fire if fire severity is low and the stem apex is not killed.
Postfire seedlings may establish from residual or off-site seed sources. Tropical soda apple may establish from off-site seed source dispersed by wildlife, cattle, humans, or contaminated equipment. In some species, fire induces postfire germination through heat scarification of seed in the soil seed bank (reviews by [32,47]). Germination of tropical soda apple seed increased when scarified by digestion (see Seed banking and Germination), and heat scarification of residual seed may promote a similar response.
FUELS AND FIRE REGIMES:
Fuels: As of this writing (2009), no published information was available on tropical soda apple's fuel characteristics. Large patches of tropical soda apple may contribute to fuel loads, especially in areas where it dies back in the winter.
Fire regimes: Information pertaining to tropical soda apple on wildlands is limited, making it difficult to infer what relationship, if any, tropical soda apple has with fire. It is possible, however, to discuss fire regimes as they pertain to broad classifications of plant communities in which tropical soda apple occurs.
Plant communities associated with tropical soda apple, such as oak hammocks and cypress heads, are typically described as islands or clumps of vegetation embedded within larger, characteristically open plant communities (e.g., wet grasslands, prairies) (, review by ). Fire may play a greater role in maintaining surrounding communities than the embedded communities. For example, wet grasslands in southeastern United States tend to be flammable and are adapted to frequent fire (review by ). Presettlement fire regimes for these communities have been classified as stand-replacement types with 1- to 10-year return intervals (reviews by [73,100]). Conversely, oak hammocks within wet grasslands may rarely burn and generally develop in the absence of fire. Low-intensity fires (review by ) characterized by short flame lengths (<2 feet) may occur in hammocks (review by ). Fire may be less frequent in hammocks than in surrounding plant communities, because vegetation in hammocks is generally considered less flammable than surrounding vegetation (review by ). Hammock litter generally holds more moisture than litter of surrounding communities, making hammocks more resistant to fire (reviews by [73,81]). Furthermore, embedded vegetation types may be somewhat protected from the frequent fires that normally spread through the surrounding vegetation because they often occur near wetlands, ponds, or lakes where they are rarely exposed to direct head fire (review by ). Fires may be more frequent on the upper slopes rather than low to midslopes of hammocks and may play an important role in the formation and maintenance of xeric hammocks (review by ). During times of drought, or where hammocks have expanded out to surrounding vegetation, hammocks may experience high-intensity fires (reviews by [73,81]). Little is known about fire's relationship to cypress heads (reviews by [73,87], but understory fire may play a role in their formation .
Tropical soda apple also occurs  in fire-maintained communities such as mesic flatwoods ([40,50], review by ). Mesic flatwoods experience surface fires that generally burn much of the groundlayer vegetation. On average, surface fires occur every 2 years and stand-replacing fires every 65 years. Fire
Although tropical soda apple has not been studied for its potential to alter fire regimes in wildlands, it may alter fuel characteristics and impact fire regimes, especially where it dominates the plant community. Impacts of invasive species on fire regimes have been discussed by several authors (e.g., [9,30]). A review by D'Antonio  suggests that species that alter the disturbance regime of a site are qualitatively different from the rest of the species in a community. Where invaders are similar in life form to natives, they tend to alter primarily fuel biomass per unit area of ground, which may influence fire intensity or slightly modify the existing fire regime. Where invaders differ in life form from natives, they have the potential to substantially alter fire frequency and the ecological community [8,9,30]. Before a determination can be made on tropical soda apple's ability to alter fire regimes on wildlands, more information is needed on tropical soda apple's fuel characteristics and the species composition typical of plant associations where it is invasive.
See the Fire Regime Table for further information on fire regimes of vegetation communities associated with tropical soda apple. 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".
Most of those descriptions are for large plant community classifications that contain the embedded community types that may contain tropical soda apple; fire regimes for embedded communities are likely different. However, information on the fire regimes of these large plant community types may provide some information about the fire ecology of embedded plant communities. Tropical soda apple was probably not present when reference fire regimes were functioning but has established since habitat alteration and fire exclusion began.FIRE MANAGEMENT CONSIDERATIONS:
In general, preventing invasive plants from establishing in weed-free burned areas is the most effective and least costly management method. There are a number of general guidelines, which may help to prevent tropical soda apple's postfire establishment and spread on burned sites where it previously occurred or on sites that are near tropical soda apple infestations. This can be accomplished through early detection and eradication of new infestations, careful monitoring and follow-up, and limiting dispersal of its seed on burned sites. General recommendations for preventing postfire establishment and spread of invasive plants include:
Palatability and/or nutritional value: Like many plants in the Solanaceae family, tropical soda apple contains solasodine, a substance poisonous to humans and other animals . Solasodine is concentrated in tropical soda apple's fruit, especially in the mucilaginous layer surrounding the seed [65,80]. The level of solasodine increases as tropical soda apple berries mature and declines as berries become overripe . Although tropical soda apple fruit may be bitter-tasting to humans , the taste apparently does not preclude livestock and wildlife from eating tropical soda apple fruit .
Livestock do not eat tropical soda apple foliage . Wunderlin speculated  that the spines and glandular hairs on the foliage prevent cattle from eating the foliage.
Cover value: In Brazil, Mechanitis lysimnia, a butterfly, lays its eggs on the leaves of tropical soda apple and other Solanum spp. .OTHER USES:
Due to its rapid spread, tropical soda apple is on the Federal Noxious Weed List . In Florida, tropical soda apple was listed in 1994 on the state's noxious weed list as a Category I invasive, making it unlawful to introduce, have in one's possession, move, or release it in the state [26,67]. Category I invasive species in general are "nonnative species that have invaded natural areas and are displacing native plants or are disrupting natural community structure and function" . Tropical soda apple's greatest impact in Florida has been to bahia grass pastures, where it displaces the shade-intolerant nonnative grass [27,34,66,103] and can eventually form monocultures . When it establishes in wooded areas, it prevents cattle from seeking shelter from the sun [27,103], presumably because its spines restrict livestock movement . As of 2009, tropical soda apple was estimated to infest nearly 1 million acres (400,000 ha) of pasture in Florida .
It is unclear what impacts tropical soda apple has in states outside Florida, but research in Mississippi indicates it has the potential to become a threat . Georgia declared tropical soda apple a "Public Nuisance" for its impacts to the agricultural and horticultural industries . The Tennessee Exotic Pest Plant Council has given tropical soda apple a ranking of 1. Plants in this category pose a severe threat in Tennessee because of their invasive tendencies and their ability to spread easily into native plant communities and displace native vegetation .
Tropical soda apple's ecological impacts have not been well documented , and little has been reported on its impacts to wildlands. It is assumed that tropical soda apple displaces native plants and interferes with natural ecosystem processes [23,26,66]. However, it has been suggested that on uncultivated rangelands and wildlands, tropical soda apple may not form dense monocultures (Mullahey personal communication cited in ). Eight years after its introduction to North America, tropical soda apple was reported in 20 natural areas from as far north as Alachua County, Florida (Florida EPPC 1996 cited in ). In Florida, it is estimated that wooded areas comprise 10% of the total land infested by tropical soda apple . The spines on tropical soda apple can degrade wildlife habitat by creating physical barriers for animal movement, especially in large infestations . Tropical soda apple is reported in numerous native plant communities in North America and, based on its ability to adapt to a wide range of environmental conditions, it has the potential to establish in many other communities throughout its current and predicted range  (see General Distribution).
Because tropical soda apple may invade phosphate-mine reclamation sites, it may interfere with restoration efforts . Tropical soda apple's increased fecundity with increased phosphorus levels (see Seedling emergence and plant growth) has led researchers to conclude that soils high in phosphorus may be predisposed to invasion by tropical soda apple .
Economic impacts: Tropical soda apple is a serious economic threat to the beef cattle industry. If left uncontrolled, it can infest a pasture in 1 to 2 years , reducing pasture productivity and lowering stocking rates . Surveys taken in 1993 indicated that Florida's beef cattle producers attributed $11 million dollars in production losses to tropical soda apple. Losses were associated with lower carrying capacity of pastures and heat stress on cattle that could not access shade . Based on field tests in Florida, 20 tropical soda apple plants/acre of pasture could result in an estimated revenue loss of $49/acre due to a decrease in bahia grass yield . Restrictions on the interstate movement of livestock, seed, hay, soil, and manure may have additional economic impacts to the beef cattle industry .
Because it interferes with crop production, tropical soda apple is a threat to the vegetable crop industry [26,27]. It also acts as an alternative host for the potato fungus Alternaria solani  and 6 viruses  that cause economic damage to vegetable crops of the Solanaceae family . Tropical soda apple may be a host to bidens mottle virus, which causes damage to crops outside of the Solanaceae family . Additionally, numerous crop pests utilize tropical soda apple as an alternative host . Although no estimates of monetary losses to this industry were found, one review predicted that tropical soda apple "will" have major economic impacts to agriculture .
Control: As of this writing (2009), research is ongoing. The University of Florida's West Florida Research and Education Center and the Center for Aquatic and Invasive Plants provide information on tropical soda apple control.
Tropical soda apple is difficult to control due to its extensive root system, which can generate new shoots, its prolific seed production (see Regeneration Processes), and its tendency to form large patches. The sharp prickles act as barriers, limiting access to infested sites . Complete eradication may be unlikely . Efforts to control tropical soda apple may be most effective if the entire plant, including its immature and mature fruit and its root system, is removed [12,24]. Effective weed control strategies need to account for a soil seed bank lasting approximately 3 to 12 months (see Seed banking) . To prevent reintroduction of seed from neighboring uncontrolled populations of tropical soda apple, repeat control measures and follow-up monitoring may be required [23,85].
Invasive plant control is most effective when it employs a long-term, ecosystem-wide strategy rather than a tactical approach focused on battling individual invaders . In all cases where invasive species are targeted for control, the potential for other invasive species to fill their void must be considered regardless of what control method is employed . Efforts to control tropical soda apple would be enhanced if more were known about ecosystem responses to tropical soda apple invasion in wildlands.
Fire: For information on the use of prescribed fire to control this species, see Fire Management Considerations.
Prevention: Regulations and collaborative efforts have been initiated to prevent the spread of tropical soda apple to areas outside its current (2009) North American range. Since it is on the Federal Noxious Weed List, the interstate movement of tropical soda apple plants or products containing tropical soda apple is prohibited . Additionally, Vermont, Massachusetts, Kansas, Minnesota, Arizona, California, and Oregon have placed restrictions on tropical soda apple transportation and/or have listed it as a potential noxious weed or pest plant in their state . In 1994, numerous southern and mid-Atlantic states formed the Tropical Soda Apple Task Force to develop effective strategies to control and limit the dissemination of tropical soda apple. As of 2009, a set of best management practices was being developed to help control tropical soda apple and slow its spread [48,71]. The tropical soda apple Research and Extension Group was organized in 1993 at the University of Florida to facilitate communication among the various researchers and extension programs involved with tropical soda apple control .
Florida cattlemen and sod farmers have been targeted for cooperative participation in programs and/or regulation related to cattle transport activities in an effort to slow the spread of tropical soda apple . The Tropical Soda Apple Task Force collaborates with industry representatives to find cooperative approaches to slow the spread of tropical soda apple. As of 2009, no official regulatory policies had been issued in Florida restricting cattle movement as it pertains to tropical soda apple spread; however, other states may have regulations concerning the acceptance of cattle from Florida . At the time of this writing (2009), Florida Department of Agriculture and Consumer Services was charging a fee to certify sod as tropical soda apple-free .
Various other methods have been suggested to prevent the spread of tropical soda apple by seed. Control methods that reduce tropical soda apple fruit production  or seed dispersal, such as mowing, may help prevent the spread of tropical soda apple (see Physical or mechanical control). Cleaning off all equipment and vehicles that have been used on sites infested with tropical soda apple may help to reduce the spread of tropical soda apple seed . Researchers studying tropical soda apple seed viability in the digestive tracts of cattle concluded that cattle grazing on tropical soda apple-infested lands be held in small feedlots that are tropical soda apple-free prior to transporting them to noninfested pastures. Cattle removed from tropical soda apple-infested sites for at least 1 week prior shipping are less likely to spread tropical soda apple seed through their feces . A laboratory study indicated that there was potential to prevent the spread of viable tropical soda apple seed by feeding cattle herbicide-treated feed . The authors, however, did not indicate how this treatment could influence the health of cattle or consumers of beef.
Cultural control: Following greenhouse and field tests, Akanda and others  suggested that maintaining a thick cover of grass may help reduce emergence of tropical soda apple seedlings in pastures.
Physical or mechanical control: For small patches, tropical soda apple seedlings and mature plants can be pulled or dug out, but care must be taken to remove the entire root to prevent regrowth . Mechanical procedures such as mowing or plowing may be inappropriate in wildlands.
For established populations and large patches of tropical soda apple in pastures, maintaining plants in a fruit-free condition may limit seed dispersal [63,69]. Moderate tropical soda apple control (83%) has been achieved by mowing plants 3 consecutive times at 60-day intervals, preferably before they set fruit. Improved control was achieved (93-100%) when mowing was done in combination with an herbicide application (see Integrated management) . Since tropical soda apple plants typically regrow and produce fruit in approximately 70 to 80 days after being cut , mowing every 50 to 60 days is recommended to prevent seed dispersal [65,67,69]. Because laboratory tests showed that tropical soda apple seed from fruits <0.4 inch (1.0 cm) in diameter did not germinate, Bryson and Byrd  suggested that mowing or handpicking tropical soda apple when fruits are <0.4 inch in diameter may help reduce seed dispersal and subsequent seedling establishment.
A greenhouse study suggests that control strategies that keep tropical soda apple seed at the soil surface (e.g., mowing) or at depths >4 inches (10 cm) (e.g., plowing) could substantially reduce tropical soda apple seedling establishment  (see Germination).
Since new shoots can regenerate from root fragments, tilling is not recommended for mechanical control of tropical soda apple .
Biological control: Biological control of invasive species has a long history that indicates many factors must be considered before using biological controls [98,104]. Tu and others  provide background information and considerations for biological control of invasive species in general in their Weed Control Methods Handbook. Additionally, the University of Florida's West Florida Research and Education Center and the Center for Aquatic and Invasive Plants provide information on biological control of tropical soda apple.
Efforts to identify an effective biological control for tropical soda apple were initiated in the early 1990s. Researchers, mostly affiliated with the University of Florida, have been studying a variety of insects, fungi, bacteria, and viruses for their potential to control tropical soda apple. As of this writing (2009), researchers had released a South American beetle for biological control for tropical soda apple, and other South American insects were being evaluated .
Gratiana boliviana was approved for field release in 2003. Since then, more than 220,000 of the leaf beetles have been released throughout Florida and parts of Alabama, Georgia, and South Carolina [48,58,97]. Populations of the beetle have established on several of these sites . In 2007, G. boliviana was released in Jasper County, Texas, to control tropical soda apple [48,97]. Since its release in 2003, G. boliviana has spread as far north as Rhea County, Tennessee, at 35.6 ° N latitude . After evaluating G. boliviana's generational turnaround and tolerance to cold, Diaz  concluded that the northern extent of this beetle's range in the United States would be near 32 to 33 ° N latitude.
Initial evaluations of G. boliviana's release reported extensive (20-100%) defoliation on tropical soda apple by the beetle . One review reported that this beetle chews holes in the upper leaves of tropical soda apple, substantially reducing the weed's survival . A later review indicated that G. boliviana has not typically controlled individual plants unless the beetles were present in "very high" numbers. The beetle may, however, reduce the number of fruits and/or reduce a plant's overall fitness. The review also suggested that G. boliviana is better suited for control of small infestations of tropical soda apple than large or remote infestations . No nontarget effects had been reported within 3 years of the beetle's release .
Tobaviruses are being evaluated for their potential to control tropical soda apple . In the greenhouse, tropical soda apple plants inoculated with Tobacco mild green virus died within 14 days of inoculation. Researchers concluded that Tobacco mild green virus was lethal to tropical soda apple and should be further evaluated for possible use in integrated management of tropical soda apple . Overholt and others  investigated the influence of Tropical soda apple mosaic tobamovirus on the beetle G. boliviana, and also tested transmission of the virus by the beetle. Under laboratory conditions, there was no evidence of viral transmission by G. boliviana; however, the virus reduced the effectiveness of G. boliviana as a biological control agent on tropical soda apple, which may limit its use for integrated management.
Chemical control: Research on chemical control of tropical soda apple was ongoing as of 2009. See West Florida Research and Education Center and the Center for Aquatic and Invasive Plants databases for information on chemical control of tropical soda apple.
Herbicide treatments have and continue to be developed to control tropical soda apple and are being used in the field to reduce tropical soda apple populations and slow its spread. In the greenhouse, tropical soda apple was controlled 90 days following herbicide treatments . Field tests in Florida indicated that herbicide applied in April could reduce tropical soda apple cover from 11% to 98% in 50 to 335 days, depending on the type of herbicide applied . Seed production may be stopped if herbicide is applied prior to tropical soda apple flowering . Combining herbicides with a growth regulator that prevents flowering, such as maleic hydrazide, may extend the number of days that herbicide controls tropical soda apple . While control may be achieved with one application of herbicide, repeat herbicide applications may be necessary for herbicides that lack preemergence control [36,84,85]. Herbicides must be translocated to the roots of tropical soda apple to kill root buds; otherwise, root sprouting occurs. Results from a greenhouse study suggest that translocation of herbicide to the roots of tropical soda apple is optimized in September and October in southern Florida .
Many chemicals have been studied to control tropical soda apple, especially for large infestations in pastures. Reports from the University of Florida Extension service indicate that "excellent" chemical control may be achieved if herbicide is applied correctly. As of this writing (2009), aminopyralid and triclopyr were recommended for control of tropical soda apple [35,84,85]. Herbicide treatments developed for tropical soda apple control have been designed for specific circumstances, and each has strengths and weaknesses. Therefore, it is important to understand the benefits of these herbicides to achieve maximum effectiveness . A few publications contain specific information on the use of these and other herbicides to control tropical soda apple: [84,85]. Trenholm  provides a detailed analysis of nutrient accumulation in tropical soda apple that may help to identify optimal herbicide application timing.
Herbicide treatments developed for pasture use may not necessarily be appropriate for oak hammock areas  or other wildlands. Because imazapyr usually stays within the top 20 inches (50 cm) of soil and may not affect mature oak trees, one study recommended its use to control tropical soda apple in oak hammocks. Lowering herbicide rates from those recommended for pasture use may help to reduce risk to immature oak trees .
Herbicides are effective in gaining initial control of a new invasion or a severe infestation, but they are rarely a complete or long-term solution to weed management . See the Weed Control Methods Handbook  for considerations on the use of herbicides in wildlands and detailed information on specific chemicals.
Integrated management: As of this writing (2009), mowing in combination with herbicide treatment was being recommended as one method to control tropical soda apple [61,85]; however, mowing-herbicide treatment may be difficult and/or inappropriate in wildlands, and is likely limited to pastures.
Herbicide treatment following frost may control tropical soda apple. In Florida, over 95% of tropical soda apple plants were controlled within 120 days following various herbicide treatments that were applied to regrowth 60 days following a heavy frost. Effectiveness of this integrated approach may be influenced by herbicide concentration and timing of application .Ferrell and others  investigated the potential to use Tobacco mild green mosaic tobamovirus in conjunction with herbicide for tropical soda apple control. The tobavirus was mixed with various synthetic herbicides and rubbed on the leaf surface of tropical soda apple plants. On the average, mixtures containing the tobavirus reduce tropical soda apple by 81% compared to the control rate from herbicide alone .
|Fire regime information on vegetation communities in which tropical soda apple may occur. This information is taken from the LANDFIRE Rapid Assessment Vegetation Models , which were developed by local experts using available literature, local data, and/or expert opinion. This table summarizes fire regime characteristics for each plant community listed. The PDF file linked from each plant community name describes the model and synthesizes the knowledge available on vegetation composition, structure, and dynamics in that community. Cells are blank where information is not available in the Rapid Assessment Vegetation Model.|
|Vegetation Community (Potential Natural Vegetation Group)||Fire severity*||Fire regime characteristics|
|Percent of fires||Mean interval
|Everglades (marl prairie)||Replacement||45%||16||10||20|
|Surface or low||9%||20|
|Pond cypress savanna||Replacement||17%||120|
|Surface or low||57%||35|
|Surface or low||97%||2||1||8|
Replacement: Any fire that causes greater than 75% top removal of a vegetation-fuel type, resulting in general replacement of existing vegetation; may or may not cause a lethal effect on the plants.
Mixed: Any fire burning more than 5% of an area that does not qualify as a replacement, surface, or low-severity fire; includes mosaic and other fires that are intermediate in effects.
Surface or low: Any fire that causes less than 25% upper layer replacement and/or removal in a vegetation-fuel class but burns 5% or more of the area [46,50].
1. Akanda, Rais U.; Mullahey, J. Jeffrey; Dowler, Clyde C.; Shilling, Donn G. 1997. Influence of postemergence herbicides on tropical soda apple (Solanum viarum) and bahiagrass (Paspalum notatum). Weed Technology. 11(4): 656-661. 
2. Akanda, Rais U.; Mullahey, J. Jeffrey; Shilling, Donn G. 1996. Environmental factors affecting germination of tropical soda apple (Solanum viarum). Weed Science. 44(3): 570-574. 
3. Albin, Cheri L. 1994. Non-indigenous plant species find a home in mined lands. In: Ecological restoration of lands infested with non-indigenous plant species. In: Schmitz, Don C.; Brown, Tom C., eds. An assessment of non-indigenous species in Florida's public lands. Technical Report No. TSS-94-100. Tallahassee, FL: Florida Department of Environmental Protection: 252-253. 
4. Asher, Jerry; Dewey, Steven; Olivarez, Jim; Johnson, Curt. 1998. Minimizing weed spread following wildland fires. Proceedings, Western Society of Weed Science. 51: 49. 
5. Babu, C. R.; Hepper, F. N. 1979. Taxonomy and nomenclature of Solanum khasianum and some of its relatives. Kew Bulletin. 34(2): 407-411. 
6. Baker, C. A.; Kamenova, I.; Raid, R.; Adkins, S. 2007. Bidens mottle virus identified in tropical soda apple in Florida. Plant Disease. 91(7): 905. 
7. Bredow, E.; Pedrosa-Macedo, J. H.; Medal, J. C.; Cuda, J. P. 2007. Open field host specificity tests in Brazil for risk assessment of Metriona elatior (Coleoptera: Chrysomelidae), a potential biological control agent of Solanum viarum (Solanaceae) in Florida. Florida Entomologist. 90(3): 559-564. 
8. Brooks, Matthew L. 2008. Effects of fire suppression and postfire management activities on plant invasions. In: Zouhar, Kristin; Smith, Jane Kapler; Sutherland, Steve; Brooks, Matthew L., eds. Wildland fire in ecosystems: Fire and nonnative invasive plants. Gen. Tech. Rep. RMRS-GTR-42-vol. 6. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 269-280. 
9. Brooks, Matthew L.; D'Antonio, Carla M.; Richardson, David M.; Grace, James B.; Keeley, Jon E.; DiTomaso, Joseph M.; Hobbs, Richard J.; Pellant, Mike; Pyke, David. 2004. Effects of invasive alien plants on fire regimes. BioScience. 54(7): 677-688. 
10. Brown, W. F.; Mullahey, J. J.; Akanda, R. U. 1996. Survivability of tropical soda apple seed in the gastro-intestinal tract of cattle. In: Proceedings of the tropical soda apple symposium; 1996 January 9-10; Bartow, FL. Gainesville, FL: University of Florida, Institute of Food and Agriculture Science: 35-39. 
11. Bryson, Charles T.; Byrd, John D., Jr. 2007. Biology, reproductive potential, and winter survival of tropical soda apple (Solanum viarum). Weed Technology. 21(3): 791-795. 
12. Bryson, Charles T.; Byrd, John D. 1994. Solanum viarum (Solanaceae), new to Mississippi. Sida. 16: 382-385. 
13. Bryson, Charles T.; Westbrooks, Randy; Maddow, Victor. 2009. Species information: Solanum viarum--tropical soda apple, [Online]. In: IPAMS: Invasive plant atlas of the MidSouth. Mississippi State, MS: Mississippi State University, GeoResources Institute (Producer). Available: http://www.gri.msstate.edu/ipams/Species.php?SName=Solanum+viarum&CName= [2009, September 28]. 
14. Bussan, Alvin J.; Dyer, William E. 1999. Herbicides and rangeland. In: Sheley, Roger L.; Petroff, Janet K., eds. Biology and management of noxious rangeland weeds. Corvallis, OR: Oregon State University Press: 116-132. 
15. Busse, Matt D.; DeBano, Leonard F. 2005. [revised 2008]. Soil biology. In: Neary, Daniel G.; Ryan, Kevin C.; DeBano, Leonard F., eds. Wildland fire in ecosystems: effects of fire on soil and water. Gen. Tech. Rep. RMRS-GTR-42-vol. 4. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 73-92. 
16. Byrd, John D., Jr.; Bryson, Charles T.; Westbrooks, Randy G. 2004. Tropical soda apple (Solanum viarum Dunal) identification and control. Jackson, MS: Mississippi Department of Agriculture and Commerce, Bureau of Plant Industry. 2 p. In cooperation with: U.S. Department of Agriculture, Animal and Plant Health Inspection Service, Plant Pest Quarantine. 
17. Call, N. M.; Coble, H. D. 1998. Phosphorous effects on tropical soda apple (Solanum viarum Dunal) growth and development. Proceedings, Southern Weed Science Society. 51: 244-245. Abstract. 
18. Call, N. M.; Coble, H. D.; Thomas, J. F. 1999. Physiological aspects of tropical soda apple (Solanum viarum Dunal) regrowth. Proceedings, Southern Weed Science Society. 52. Abstract: 214-215. 
19. Chand, Pradeep K.; Chand, Suresh. 1995. High frequency plant regeneration from Solanum viarum protoplasts. Journal of Herbs, Spices & Medicinal Plants. 3(4): 21-34. 
20. Chapman, Rachel Ross; Crow, Garrett E. 1981. Raunkiaer's life form classification in relation to fire. Bartonia. Philadelphia, PA: Philadelphia Botanical Club. 48: 19-33. 
21. Charudattan, R.; DeValerio, J. T.; Pettersen, M. S. 2001. Biological control of tropical soda apple with plant pathogens and integration of biological control with other management options. Weed Science Society of America. 41: 80. Abstract. 
22. Cipollini, Martin L.; Levey, Douglas J. 1997. Secondary metabolites of fleshy vertebrate-dispersed fruits: adaptive hypotheses and implications for seed dispersal. The American Naturalist. 150(3): 346-372. 
23. Coile, Nancy C. 1993 [Revised 1996]. Tropical soda apple, Solanum viarum Dunal: the plant from hell. Botany Circular No. 27. Tallahassee, FL: Florida Department of Agriculture and Consumer Services, Division of Plant Industry. 4 p. 
24. Cooke, Linda. 1997. Nothing but a wasteful weed. Agricultural Research. 45(4): 14-15. 
25. Core, Jim. 2002. ARS researchers winning the battle with noxious weeds. Agricultural Research. 50(1): 12-13. 
26. Cuda, J. P.; Coile, N. C.; Gandolfo, D.; Medal, J. C.; Mullahey, J. J. 2004. Tropical soda apple. In: Coombs, Eric M.; Clark, Janet K.; Piper, Gary L.; Cofrancesco, Alfred F., Jr., eds. Biological control of invasive plants in the United States. Corvallis, OR: Oregon State University Press: 396-399. 
27. Cuda, J. P.; Gandolfo, D.; Medal, J. C.; Charudattan, R.; Mullahey, J. J. 2002. Tropical soda apple, wetland nightshade, and turkey berry. In: Van Driesche, Roy; Lyon, Suzanne; Blossey, Bernd; Hoddle, Mark; Reardon, Richard, tech. coords. Biological control of invasive plants in the eastern United States. USDA Forest Service Publication FHTET-2002-04. [Washington, DC]: U.S. Department of Agriculture, Forest Service: 320-340. Available online: http://www.invasive.org/eastern/biocontrol/23SodaApple.html [2005, August 12]. 
28. Cuda, J. P.; Parker, P. E.; Goodson, R. A.; Gillmore, J. L. 1998. Evaluation of Ditylenchus phyllobius (Tylenchida: Anguinidae) as a potential biological control agent for Solanum viarum and Solanum tampicense (Solanaceae). Nematropica. 28(1): 107-111. 
29. D'Antonio, Carla M. 2000. Fire, plant invasions, and global changes. In: Mooney, Harold A.; Hobbs, Richard J., eds. Invasive species in a changing world. Washington, DC: Island Press: 65-93. 
30. D'Antonio, Carla M.; Vitousek, Peter M. 1992. Biological invasions by exotic grasses, the grass/fire cycle, and global change. Annual Review of Ecology and Systematics. 23: 63-87. 
31. Diaz, Rodrigo; Overholt, William A.; Samayoa, Ana; Sosa, Freddy; Cordeau, Diane; Medal, Julio. 2008. Temperature dependent development, cold tolerance, and potential distribution of Gratiana boliviana (Coleoptera: Chrysomelidae), a biological control agent of tropical soda apple, Solanum viarum (Solanaceae). Biocontrol Science and Technology. 18(2): 193-207. 
32. Dibble, Alison C.; Zouhar, Kristin; Smith, Jane Kapler. 2008. Fire and nonnative invasive plants in the Northeast bioregion. In: Zouhar, Kristin; Smith, Jane Kapler; Sutherland, Steve; Brooks, Matthew L., eds. Wildland fire in ecosystems: fire and nonnative invasive plants. Gen. Tech. Rep. RMRS-GTR-42-vol. 6. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 61-90. 
33. Dowler, Clyde C. 1995. Tropical soda apple growth and response to the herbicides in Georgia. Proceedings, Southern Weed Science Society. 48: 160-164. 
34. Duncan, Celestine A. 2005. Tropical soda apple--Solanum viarum Dunal. In: Duncan, Celestine L.; Clark, Janet K., eds. Invasive plants of range and wildlands and their environmental, economic, and societal impacts. WSSA Special Publication. Lawrence, KS: Weed Science Society of America: 188-197. 
35. Ferrell, J. A.; Sellers, B.; Mullahey, J. J. 2008. Tropical soda apple control: sorting through the options. SS-AGR-129. Gainesville, FL: University of Florida, Institute of Food and Agricultural Sciences Extension. 3 p. 
36. Ferrell, Jason A.; Mullahey, J. Jeffrey; Langeland, Kenneth A.; Kline, William N. 2006. Control of tropical soda apple (Solanum viarum) with aminopyralid. Weed Technology. 20(2): 453-457. 
37. Ferrell, Jason; Charudattan, Raghavan; Elliott, Mark; Hiebert, Ernest. 2008. Effects of selected herbicides on the efficacy of tobacco mild green mosaic virus to control tropical soda apple (Solanum viarum). Weed Science. 56(1): 128-132. 
38. Flinn, Marguerite A.; Wein, Ross W. 1977. Depth of underground plant organs and theoretical survival during fire. Canadian Journal of Botany. 55: 2550-2554. 
39. Florida Exotic Pest Plant Council. 2005. List of Florida's invasive species, [Online]. Florida Exotic Pest Plant Council (Producer) Available: http://www.fleppc.org/list/05List.htm [2005, November 1]. 
40. Florida Natural Areas Inventory. 1990. Guide to the natural communities of Florida, [Online]. In: Species and communities. Tallahassee, FL: Florida Natural Areas Inventory; Florida State University (Producer). Available: http://www.fnai.org/PDF/Natural_Communities_Guide.pdf [2009, June 2]. 
41. Frohne, Dietrich; Pfander, Hans Jurgen. 1984. A colour atlas of poisonous plants: a handbook for pharmacists, doctors, toxicologists, and biologists. London: Wolfe Publishing Ltd. 291 p. [Translated from 2nd German edition by Norman Grainger Bisset]. 
42. Geonvironmental Protection Agency, Washington, DC. Available: http://www.galvbayinvasives.org/ [2009, October 16]. 
43. Gonzalez, Lisa; Christoffersen, Bradley, eds. 2006. The quiet invasion: a guide to invasive plants of the Galveston Bay area, [Online]. The Woodlands, TX: Houston Advanced Research Center (Producer). In cooperation with: Texas Commission on Environmental Quality, Galveston Bay Estuary Program, Houston, TX; U.S. E June 2]. 
44. Goodwin, Kim; Sheley, Roger; Clark, Janet. 2002. Integrated noxious weed management after wildfires. EB-160. Bozeman, MT: Montana State University, Extension Service. 46 p. Available online: http://www.montana.edu/wwwpb/pubs/eb160.html [2003, October 1]. 
45. Gordon, Doria R. 1998. Effects of invasive, non-indigenous plant species on ecosystem processes: lessons from Florida. Ecological Applications. 8(4): 975-989. 
46. Hann, Wendel; Havlina, Doug; Shlisky, Ayn; [and others]. 2008. Interagency fire regime condition class guidebook. Version 1.3, [Online]. In: Interagency fire regime condition class website. U.S. Department of Agriculture, Forest Service; U.S. Department of the Interior; The Nature Conservancy; Systems for Environmental Management (Producer). 119 p. Available: http://frames.nbii.gov/frcc/documents/FRCC_Guidebook_2008.07.10.pdf [2008, September 03]. 
47. Heitlinger, Mark E. 1975. Burning a protected tallgrass prairie to suppress sweetclover, Melilotus alba Desr. In: Wali, Mohan K., ed. Prairie: a multiple view. Grand Forks, ND: University of North Dakota Press: 123-132. 
48. Hibbard, Ken. 2009. [Email to Melissa Waggy]. August 7. Regarding Solanum viarum control. Fort Pierce, FL: Florida Department of Agriculture and Consumer Services, Bureau of Methods Development, Division of Plant Industry. On file with: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory, Missoula, MT; FEIS files. 
49. Kartesz, John T. 1999. A synonymized checklist and atlas with biological attributes for the vascular flora of the United States, Canada, and Greenland. 1st ed. In: Kartesz, John T.; Meacham, Christopher A. Synthesis of the North American flora (Windows Version 1.0), [CD-ROM]. Chapel Hill, NC: North Carolina Botanical Garden (Producer). In cooperation with: The Nature Conservancy; U.S. Department of Agriculture, Natural Resources Conservation Service; U.S. Department of the Interior, Fish and Wildlife Service. 
50. LANDFIRE Rapid Assessment. 2005. Reference condition modeling manual (Version 2.1), [Online]. In: LANDFIRE. Cooperative Agreement 04-CA-11132543-189. Boulder, CO: The Nature Conservancy; U.S. Department of Agriculture, Forest Service; U.S. Department of the Interior (Producers). 72 p. Available: http://www.landfire.gov/downloadfile.php?file=RA_Modeling_Manual_v2_1.pdf [2007, May 24]. 
51. LANDFIRE Rapid Assessment. 2007. Rapid assessment reference condition models, [Online]. In: LANDFIRE. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Lab; U.S. Geological Survey; The Nature Conservancy (Producers). Available: http://www.landfire.gov/models_EW.php [2008, April 18] 
52. Langeland, Kenneth A.; Burks, K. Craddock, eds. 1998. Identification and biology of non-native plants in Florida's natural areas. Gainesville, FL: University of Florida. 165 p. 
53. Littlefield, T. A.; Colvin, D. L.; Brecke, B. J.; Moore, J. E.; Mullahey, J. J.; Shilling, D. G. 1998. Herbicidal activity on tropical soda apple (Solanum viarum) seed during passage through the rumen. Proceedings, Southern Weed Science Society. 51: 203. Abstract. 
54. Mack, Richard N.; Simberloff, Daniel; Lonsdale, W. Mark; Evans, Harry; Clout, Michael; Bazzaz, Fakhri A. 2000. Biotic invasions: causes, epidemiology, global consequences, and control. Ecological Applications. 10(3): 689-710. 
55. Maiti, Satyabrata; Chandra, Ram; Geetha, K. A.; Mandal, Kunal. 2000. Production technology of some important medicinal and aromatic crops developed under the All India Coordinated Research Project. Indian Journal of Arecanut, Spices, and Medicinal Plants. 2(3): 88-98. 
56. McGovern, R. J.; Poston, J. E.; Mullahey, J. J. 1994. Solanum viarum: weed reservoir of plant viruses in Florida. International Journal of Pest Management. 40(3): 270-273. 
57. Medal, J. C.; Charudattan, R.; Mullahey, J. J.; Pitelli, R. A. 1996. An exploratory insect survey of tropical soda apple in Brazil and Paraguay. The Florida Entomologist. 79(1): 70-73. 
58. Medal, J.; Overholt, W.; Stansly, P.; Osborne, L.; Roda, A.; Chong, J.; Gaskalla, R.; Burns, E.; Hibbard, K.; Sellers, B.; Gioeli, K.; Munyan, S.; Gandolfo, D.; Hight, S.; Cuda, J. 2002. [Revised 2006]. Classical biological control of tropical soda apple in the USA. ENY-824. Gainesville, FL: University of Florida, Institute of Food and Agricultural Sciences; Florida Cooperative Extension Service, Entomology and Nematology Department. 4 p. 
59. Miller, James H. 2003. Nonnative invasive plants of southern forests: A field guide for identification and control. Gen. Tech. Rep. SRS-62. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southern Research Station. 93 p. Available online: http://www.srs.fs.usda.gov/pubs/gtr/gtr_srs062/ [2004, December 10]. 
60. Mislevy, P.; Martin, F. G. 1999. Tropical soda apple control as influenced by frost and herbicides. Soil and Crop Science Society of Florida. 58: 107-108. 
61. Mislevy, Paul; Mullahey, J. Jeffrey; Martin, Frank G. 1999. Preherbicide mowing and herbicide rate on tropical soda apple (Solanum viarum) control. Weed Technology. 13(1): 172-175. 
62. Monk, Carl D.; Brown, Timothy W. 1965. Ecological consideration of cypress heads in north-central Florida. The American Midland Naturalist. 74: 126-140. 
63. Mullahey, J. J.; Akanda, R. U.; Shilling, D. G. 1996. Integrated management strategies to control Solanum viarum. In: Proceedings, 2nd international weed control congress; 1996 June 25-28; Copenhagen, Denmark. [Corvallis, OR]: International Weed Science Society: 1009-1014. 
64. Mullahey, J. J.; Ferrell, Jay. 2005. Pasture equipment spreads tropical soda apple. The Florida Cattlemen and Livestock Journal. 69(5): 36. 
65. Mullahey, J. J.; Mislevy, P.; Brown, W. F.; Kline, W. N. 1996. Tropical soda apple, an exotic weed threatening agriculture and natural systems. Down to Earth. 51: 1-8. 
66. Mullahey, J. J.; Roka, F.; Fanning, M. D.; Akanda, R. 1999. Effect of tropical soda apple density on bahiagrass production. Proceedings, Southern Weed Science Society. 52: 76. Abstract. 
67. Mullahey, J. Jeffrey. 1995. Tropical soda apple campaign in Florida. In: Proceedings of the 50th southern pasture and forage crop improvement conference; 1994 May 23-25; Knoxville, TN. [Mississippi State, MS]: Southern Pasture and Forage Crop Improvement Conference: 112-119. 
68. Mullahey, J. Jeffrey. 1996. Tropical soda apple (Solanum viarum Dunal), a biological pollutant threatening Florida. Castanea. 61(3): 255-260. 
69. Mullahey, J. Jeffrey; Cornell, John. 1994. Biology of tropical soda apple (Solanum viarum) an introduced weed in Florida. Weed Technology. 8(3): 465-469. 
70. Mullahey, J. Jeffrey; Nee, Michele; Wunderlin, Richard P.; Delaney, Kris R. 1993. Weed alert! Tropical soda apple (Solanum viarum): a new weed threat in subtropical regions. Weed Technology. 7(3): 783-786. 
71. Mullahey, J. Jeffrey; Shilling, Donn G.; Mislevy, P.; Akanda, R. A. 1998. Invasion of tropical soda apple (Solanum viarum) into the U.S.: lessons learned. Weed Technology. 12(4): 733-736. 
72. Muss, Jordan D.; Austin, Daniel F.; Snyder, James R. 2003. Plants of the Big Cypress National Preserve. Journal of the Torrey Botanical Society. 130(2): 119-142. 
73. Myers, Ronald L. 2000. Fire in tropical and subtropical ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 161-173. 
74. NatureServe. 2009. Comprehensive report: Solanum viarum--tropical soda-apple, [Online]. In: NatureServe Explorer: An online encyclopedia of life. Version 7.1. Arlington, VA: NatureServe (Producer). Available:
&paging=home&save=true&startIndex=1&nextStar [2009, September 28]. 
75. Nee, Michael. 1991. Synopsis of Solanum section Acanthophora: a group of interest for glycoalkaloids. In: Hawkes, J. G.; Lester, R. N.; Nee, M.; Estrada, N., eds. Solanaceae III: Taxonomy, chemistry, evolution. Richmond Surrey, UK: Royal Botanic Gardens, Kew; London: Linnean Society of London: 257-266. 
76. Olckers, T.; Medal, J. C.; Gandolfo, D. E. 2002. Insect herbivores associated with species of Solanum (Solanaceae) in northeastern Argentina and southeastern Paraguay, with reference to biological control of weeds in South Africa and the United States of America. The Florida Entomologist. 85(1): 254-260. 
77. Overholt, W. A.; Markle, L.; Rosskopf, E.; Manrique, V.; Albano, J.; Cave, E.; Adkins, S. 2009. The interactions of tropical soda apple mosaic tobamovirus and Gratiana boliviana (Coleoptera: Chrysomelidae), an introduced biological control agent of tropical soda apple (Solanum viarum). Biological Control. 48(3): 294-300. 
78. Patterson, David T.; McGowan, Mike; Mullahey, J. Jeff; Westbrooks, Randy G. 1997. Effects of temperature and photoperiod on tropical soda apple (Solanum viarum Dunal) and its potential range in the U.S. Weed Science. 45(3): 404-408. 
79. Pemberton, Robert W.; Wheeler, Gregory S. 2006. Orchid bees don't need orchids: evidence from the naturalization of an orchid bee in Florida. Ecology. 87(8): 1995-2001. 
80. Pingle, A. R.; Dnyansagar, V. R. 1980. Solanum viarum as a source of solasodine. Indian Drugs. 17: 366-370. 
81. Platt, William J.; Schwartz, Mark W. 1990. Temperate hardwood forests. In: Myers, Ronald L.; Ewel, John J., eds. Ecosystems of Florida. Orlando, FL: University of Central Florida Press: 194-229. 
82. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. 
83. Sahoo, S.; Dutta, P. K. 1984. Solanum viarum: A plant for the steroid drug industry. Indian Horticulture. 28: 15-18. 
84. Sellers, B. A.; Ferrell, J. A. 2009. Weed management in pastures and rangeland - 2009. SS-AGR-08. Gainesville, FL: University of Florida, Institute of Food and Agriculture Sciences; Florida Cooperative Extension Service, Department of Agronomy. 13 p. 
85. Sellers, Brent; Ferrell, Jay; Mullahey, J. Jeffrey; Hogue, Pat. 2009. Tropical soda apple: biology, ecology, and management of a noxious weed in Florida. SS-AGR-77. Gainesville, FL: University of Florida, Institute of Food and Agriculture Sciences; Florida Cooperative Extension Service, Department of Agronomy. 5 p. 
86. Stickney, Peter F. 1989. Seral origin of species comprising secondary plant succession in Northern Rocky Mountain forests. FEIS workshop: Postfire regeneration. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT. 10 p. 
87. Stocker, Randall; Hupp, Karen V. S. 2008. Fire and nonnative invasive plants in the Southeast bioregion. In: Zouhar, Kristin; Smith, Jane Kapler; Sutherland, Steve; Brooks, Matthew L., eds. Wildland fire in ecosystems: fire and nonnative invasive plants. Gen. Tech. Rep. RMRS-GTR-42-vol. 6. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 91-112. 
88. Suryawanshi, Y. B.; Patil, R. B.; Moholkar, N. D. 2001. Study on seed germination procedures in some medicinal plant species. Seed Research. 29(2): 141-144. 
89. Tennessee Exotic Pest Plant Council. 2001. Invasive exotic pest plants in Tennessee, [Online]. In: Invasive exotic plants. Fairview, TN: Tennessee Exotic Pest Plant Council (Producer) Available: http://www.tneppc.org/Invasive_Exotic_Plant_List/The_List.htm [2009, June 12]. 
90. Texas A&M University, Department of Biology. 2004. Specimens representing Solanaceae--Solanum viarum, [Online]. In: TAMU vascular plant specimen listing. In: Department of Biology herbarium specimen data. College Station, TX: Texas A&M University, Department of Biology Herbarium (Producer). Available: http://botany.csdl.tamu.edu/FLORA/tamu/tamusol.htm [2009, September 28]. 
91. Trenholm, L. E.; Sturgis, A. K.; Ninaji, A.; Gallaher, R. N.; Akanda, R. U.; Mullahey, J. J. 1995. Growth and nutrient accumulation in tropical soda apple (Solanum viarum Dunal). Agronomy Research Report AY-95-04. Gainesville, FL: University of Florida, Department of Agronomy. 27 p. 
92. Tu, Mandy; Hurd, Callie; Randall, John M., eds. 2001. Weed control methods handbook: tools and techniques for use in natural areas. Davis, CA: The Nature Conservancy. 194 p. 
93. U. S. Department of Agriculture, Animal and Plant Health Inspection Service. 2000. Public Law 106-224--June 20, 2000: Title IV--Plant Protection Act, [Online]. Washington, DC: U.S. Department of Agriculture, Animal and Plant Health Inspection Service (Producer). Available: http://www.aphis.usda.gov/brs/pdf/PlantProtAct2000.pdf [2009, September 28]. 
94. U.S. Department of Agriculture, Animal and Plant Health Inspection Service (APHIS). 2006. Federal noxious weed list, [Online]. In: Plant health--Noxious weeds program. Washington, DC: U.S. Department of Agriculture, Animal and Plant Health Inspection Service (Producer). Available: http://www.aphis.usda.gov/plant_health/plant_pest_info/weeds/downloads/weedlist2006.pdf [2009, April 8]. 
95. U.S. Department of Agriculture, Forest Service. 2001. Guide to noxious weed prevention practices. Washington, DC: U.S. Department of Agriculture, Forest Service. 25 p. Available online: http://www.fs.fed.us/rangelands/ftp/invasives/documents/GuidetoNoxWeedPrevPractices_07052001.pdf [2005, October 25]. 
96. U.S. Department of Agriculture, Natural Resources Conservation Service. 2009. PLANTS Database, [Online]. Available: http://plants.usda.gov/. 
97. University of Florida, Institute of Food and Agricultural Sciences, Biological Control Research& Containment Laboratory. 2009. Gratiana release results: Excel spreadsheet of Gratiana release results in October 2007, [Online]. In: Biological control of tropical soda apple. Gainesville, FL: University of Florida, Institute of Food and Agricultural Sciences, Biological Control Research & Containment Laboratory (Producer). Available: http://bcrcl.ifas.ufl.edu/GratianaForm_files/ [2009, October 23]. 
98. Van Driesche, Roy; Lyon, Suzanne; Blossey, Bernd; Hoddle, Mark; Reardon, Richard, tech. coords. 2002. Biological control of invasive plants in the eastern United States. USDA Forest Service Publication FHTET-2002-04. [Washington, DC]: U.S. Department of Agriculture, Forest Service. 413 p. Available online: http://www.invasive.org/eastern/biocontrol/index.html [2005, August 12]. 
99. Vasconcellos-Neto, Joao; Monteiro, Ricardo Ferreira. 1993. Inspection and evaluation of host plant by the butterfly Mechanitis lysimnia (Nymph., Ithomiinae) before laying eggs: a mechanism to reduce intraspecific competition. Oecologia. 95(3): 431-438. 
100. Wade, Dale D.; Brock, Brent L.; Brose, Patrick H.; Grace, James B.; Hoch, Greg A.; Patterson, William A., III. 2000. Fire in eastern ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 53-96. 
101. Wade, Dale; Ewel, John; Hofstetter, Ronald. 1980. Fire in south Florida ecosystems. Gen. Tech. Rep. SE-17. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station. 125 p. 
102. Weber, Ewald. 2003. Invasive plant species of the world: a reference guide to environmental weeds. Cambridge, MA: CABI Publishing. 548 p. 
103. Westbrooks, Randy G. 1998. Invasive plants: changing the landscape of America. Fact Book. Washington, DC: Federal Interagency Committee for the Management of Noxious and Exotic Weeds. 109 p. 
104. Wilson, Linda M.; McCaffrey, Joseph P. 1999. Biological control of noxious rangeland weeds. In: Sheley, Roger L.; Petroff, Janet K., eds. Biology and management of noxious rangeland weeds. Corvallis, OR: Oregon State University Press: 97-115. 
105. World Book. 2009. North American climate, [Online]. In: World Book: Encyclopedia and learning resources--Climates around the world. World Book (Producer) Available: http://www.worldbook.com/wb/Students?content_spotlight/climates/north_american_climate [2009, July 10]. 
106. Wunderlin, R. P.; Hansen, B. F. 2008. Atlas of Florida vascular plants, [Online]. In: PlantAtlas.org. Tampa, FL: University of South Florida, Institute for Systematic Botany (Producer). Available: http://www.florida.plantatlas.usf.edu/ [2009, October 15]. 
107. Wunderlin, Richard P.; Hansen, Bruce F. 2003. Guide to the vascular plants of Florida. 2nd edition. Gainesville, FL: The University of Florida Press. 787 p. 
108. Wunderlin, Richard P.; Hansen, Bruce F.; Delaney, Kris R.; Nee, Michael; Mullahey, J. Jeffrey. 1993. Solanum viarum and S. tampicense (Solanaceae): two weedy species new to Florida and the United States. Sida. 15(4): 605-611. 
109. Zomlefer, Wendy B. 1994. Guide to flowering plant families. Chapel Hill, NC: The University of Carolina Press. 430 p.