Authors: Victoria Nuzzo, Global Invasive Species Team, The Nature Conservancy
- 1 Overview
- 2 Description and diagnostic characteristics
- 3 Stewardship Summary
- 4 Resources
- 5 Information Sources
- 6 Images from Bugwood.org
- Lonicera japonica is a woody perennial, evergreen to semi-evergreen vine that can be found either trailing or climbing to over 80 ft. (24 m) in length. Young stems may be pubescent while older stems are glabrous.
- Leaves are opposite, pubescent, oval and 1-2.5 in. (2.5-6.4 cm) long. Margins are usually entire but young leaves may be lobed or toothed.
- Flowering occurs from April to July, when showy, fragrant, tubular, whitish-pink flowers develop in the axils of the leaves. The flowers turn cream-yellow as they age.
- The small shiny globular fruits turn from green to black as they ripen. Each fruit contains 2-3 small brown to black ovate seeds.
- Ecological Threat
- Lonicera japonica invades a wide variety of habitats including forest floors, canopies, roadsides, wetlands, and disturbed areas. It can girdle small saplings by twining around them, and can form dense mats in the canopies of trees, shading everything below. A native of eastern Asia, it was first introduced into North America in 1806 in Long Island, NY. Lonicera japonica has been planted widely throughout the United States as an ornamental, for erosion control, and for wildlife habitat.
Description and diagnostic characteristics
Lonicera japonica is a perennial trailing or climbing woody vine of the honeysuckle family (Caprifoliaceae) that spreads by seeds, underground rhizomes, and aboveground runners. It has opposite leaves that are ovate, entire (young leaves often lobed), 4-8 cm long, with a short petiole, and variable pubescence. In the southern part of the range the leaves are evergreen, while in more northern locales the leaves are semi-evergreen and fall off in midwinter. Young stems are reddish brown to light brown, usually pubescent, and about 3 mm in diameter. Older stems are glabrous, hollow, with brownish bark that peels in long strips. The woody stems are usually 2-3 m long, (less often to 10 m). Lonicera japonica creates dense tangled thickets by a combination of stem branching, nodal rooting, and vegetative spread from rhizomes.
Lonicera japonica (including the varieties) is easily distinguished from native honeysuckle vines by its upper leaves and by its berries. The uppermost pairs of leaves of Lonicera japonica are distinctly separate, while those of native honeysuckle vines are connate, or fused to form a single leaf through which the stem grows. Lonicera japonica has black berries, in contrast to the red to orange berries of native honeysuckle vines. The fruits are produced September through November. Each contains 2-3 ovate to oblong seeds that are 2-3 mm long, dark-brown to black, ridged on one side and flat to concave on the other.
The fragrant white (fading to yellow) flowers of Lonicera japonica are borne in pairs on solitary, axillary peduncles 5-10 mm long, supported by leaflike bracts. The species has white flowers tinged with pink and purple. Individual flowers are tubular, with a fused two-lipped corolla 3-4(-5) cm long, pubescent on the outside. Flowers are produced late April through July, and sometimes through October. Lonicera japonica var. halliana may be distinguished from the species by its pure white flowers (fading to yellow; ) and more vigorous growth. Lonicera japonica var. chinensis has purple, essentially glabrous leaves, red flowers, and a more limited range than the species, occurring north to New Jersey and Pennsylvania , with an outlier in southern Illinois.
Lonicera japonica invades fields, forest edges and openings, disturbed woods, and floodplains, in eastern North America, where it spreads rapidly and outcompetes native vegetation by vigorous above- and below-ground competition. Once established, the vine may literally engulf small trees and shrubs, which collapse under the weight, and few plants survive beneath the dense canopy. It has also escaped cultivation at scattered locations in California and in Hawaii where it has the potential to become a severe pest in mesic and wet forest areas.
Lonicera japonica has few natural enemies in North America and is difficult to control once established. Thus, the best and most effective control method is to prevent its establishment by surveying a site for its presence regularly and immediately destroying every plant located. Unfortunately Lonicera japonica is difficult to locate when small and without careful attention may go unnoticed until it is well established.
Because Japanese honeysuckle is so difficult to control once established, an appropriate control program goal is 100% kill of all plants in the target area. Removing above-ground stems by cutting pulling or burning will temporarily weaken, but not kill, Lonicera japonica as it will resprout from subterranean buds and roots, and from cut branchlets.
In northern states, Lonicera japonica retains some leaves through all or most of the winter (semi-evergreen or evergreen), when most native plants have dropped their leaves. This provides a windows of opportunity from mid-autumn through early spring when it is easier to spot and treat with herbicides, fire or other methods without damaging native species. The most effective treatment is a foliar application of glyphosate herbicide (trade names Roundup®, Rodeo® or Accord®; 1.5 v/v), applied after native vegetation is dormant and when temperatures are near and preferably above freezing. Applications within 2 days of the first killing frost are more effective than applications later in the winter. Lonicera japonica is less susceptible to herbicides after the first hard frost (-4° C). Combining fire and herbicides may prove to be more effective than either method by itself if late autumn or winter burns are used to reduce Japanese honeysuckle biomass and all resprouts are then treated with a foliar application of glyphosate about a month after they emerge. Prescribed burns may also be used to help prevent spread of Japanese honeysuckle because seedlings and young plants are most susceptible to fires. Soil disturbance should be avoided in infested areas to minimize germination of seed in the seedbank.
Imparts and Threats
Lonicera japonica damages natural communities it invades by outcompeting native vegetation for both light (shoot competition),  and below-ground resources (root competition,  and by changing forest structure. Lonicera japonica grows very rapidly, sending out numerous runners that give rise to still more runners. The vines overtop adjacent vegetation by twining about, and completely covering, small trees and shrubs. Dense Japanese honeysuckle growth can topple trees and shrubs due to its weight alone. As Lonicera japonica becomes established in forest openings it forms a dense blanket that excludes most shrubs and herbs. Few tree seedlings can penetrate the mat and those that do are often quickly overgrown and bent down by the vine, and consequently die. Forests invaded by Lonicera japonica gradually lose their natural structure as canopy openings are invaded, and understory herbs shrubs and replacement trees suppressed and killed by thick mats of honeysuckle. This results in a simplified, increasingly open understory. Lonicera japonica, in turn, becomes even more vigorous with the increased light. These openings also promote further invasion by other non-native species including aggressive vines like kudzu (Pueraria lobata) and English ivy (Hedera helix).
Shading under the extensive and rapid aerial growth of Lonicera japonica poses the most obvious threat to native species. However, Dillenburg et al. (1993a, 1993b)  demonstrated that in the early stages of invasion, below-ground competition by Lonicera japonica reduced tree growth, particularly leaf size and expansion rate, significantly and more than above-ground competition. After two growing seasons, Lonicera japonica root competition significantly reduced growth of young sweetgum trees (Liquidambar styraciflua) and greatly exceeded root competition from the native vine Parthenocissus quinquefolia. . The combined effects of above- and below-ground competition can suppress growth or result in direct mortality of trees and seedlings. Bruner (1967) documented that after five years of co-occurrence, 33% of yellow-poplar seedlings were dead, 22% were overwhelmed, and 45% were heavily draped with Lonicera japonica that germinated from seed in the first year.
Lonicera japonica has an additional competitive edge as it grows during part or all of the winter, when many native species are dormant. This evergreen or semi-evergreen character allows Lonicera japonica to photosynthesize at winter temperatures and light levels. The shade it casts during early spring may inhibit ephemeral herbs that complete their life cycle in the six weeks prior to deciduous tree leaf-out.
Alteration of forest understory and overstory structure by Lonicera japonica may lead to a decline or alteration in songbird populations. However, no studies have been conducted on interactions between Lonicera japonica and native animals, with the exception of white-tailed deer (Odocoileus virginianus) which favors Lonicera japonica leaves as food. In fact, wildlife managers in some states actively promoted growth of this aggressive vine to provide winter forage for deer. Japanese honeysuckle foliage is most digestible and nutritious in spring, but it is still relatively high in nutritional value in winter when other food sources are less available to deer. Seeds and leaves are eaten by cottontail rabbits, as well as birds, and the tangled thickets provide cover for birds and small mammals.
Lonicera japonica is a severe threat in the southeastern and eastern states (Florida to Texas, north to Kansas, Missouri, central Illinois and New York), and a severe potential threat in northern states outside the current (1995) range. On the northern edge of the range, Lonicera japonica flower production is inhibited by winter temperatures, and the vine is thus a moderate threat. For example, in Illinois, Lonicera japonica is not a serious pest in the colder, northern third of the state, but is increasingly common in the central part of the state. Lonicera japonica continues to spread gradually northward, possibly due to increasing cold tolerance, or to warm winters, or to other factors.
As of 1995 Lonicera japonica northern range was limited by winter temperatures, and its western range by drought-induced stress at the seedling stage. If atmospheric CO2 concentrations increase as predicted, resulting in a 3oC increase in average and minimum winter temperatures, the northern range of Lonicera japonica is predicted to shift up to 400 km north. Further westward expansion may be limited by decreased summer precipitation, although Lonicera japonica has improved water use efficiency and increased drought tolerance at higher CO2 levels. Lonicera japonica is also predicted to become a more serious competitor of native trees at higher CO2 levels, as it experiences much greater growth rates at higher CO2 levels than do native woody erect species.
Lonicera japonica is native to east Asia, including Japan and Korea. From this native range it has spread to Hong Kong, England, Wales , Portugal, Corsica, Hawaii , Brazil, Argentina, possibly the Ukraine, and the continental United States, primarily by way of horticultural introductions.
The species was introduced into the U.S. in 1806 on Long Island, NY , and the similar but more aggressive variety halliana was introduced to the country in 1862 in Flushing, N.Y. As with many invasive species, Japanese honeysuckle initially had a very gradual rate of spread, primarily to the south and east. Lonicera japonica was not included in Chapman's Flora of the Southern States (1884; in Hardt 1986) but in 1889 Wood and Willis included the variety chinensis in their flora of the eastern United States and a decade later Britton and Brown (1898) reported that the species ranged from New York and Pennsylvania to North Carolina and West Virginia. In 1899 Lonicera japonica was described in a wildflower book as the most widely planted of the honeysuckles. Lonicera japonica was reported from Florida in 1903, and from Texas in 1918. By 1912, it had "escaped from cultivation", and ranged from Connecticut to Florida, and within a few years was identified as an invasive problem species from the Gulf of Mexico to Massachusetts, creating "a network of tangled cords that covers the ground wherever this ruthless invader gets a foot hold".
Lonicera japonica now occurs throughout the eastern half of the United States, south of a line extending from Massachusetts west to Lake Michigan, Illinois, and Missouri, and then southwest through Texas to Mexico, an area encompassing 26 states. The northern range limit coincides with maximum 30-year winter temperatures of -25° C. The area of greatest infestation is in the center of this range, where annual precipitation averages 100-120 cm, and 30 year low temperatures are -8° C to -15° C. Lonicera japonica's range is limited to the north by severe winter temperatures, and to the west by insufficient precipitation and prolonged droughts which limit seedling establishment. At the northern edge of the range, plants have reduced growth due to a shorter growing season, and produce few or no flowers. Lonicera japonica continues to spread northward, however, possibly due to increasing cold tolerance or warmer winters. It may spread up to 400 km north if global temperature increases 3° C.
Japanese honeysuckle sporadically escapes from cultivation in California where it is present in scattered locations, primarily below 1000 m elevation. It has also escaped cultivation in scattered locations in the Hawaiian islands, particularly in mesic to wet forest in Kokee State Park on Kauai and near Volcano on the island of Hawaii. It apparently does not produce seed at most locations in Hawaii and will likely become a much more serious pest there if fertile strains develop. Unfortunately, most plants in an escaped population in Manoa Valley on Oahu reportedly set seed. A recent report from Kauai also indicates the Japanese honeysuckle population there may be spreading and has potential to become a severe pest in the Kokee area.
Lonicera japonica is native to east Asia. In Korea, Lonicera japonica is part of the understory in later successional forests dominated Carpinus cordata, Fraxinus rhynchophylla and Cornus controversa.
In North America, Lonicera japonica primarily occurs in disturbed habitat, including successional fields, roadsides, forest edges, and fence-rows. It is common in dry-mesic to wet-mesic upland forest, floodplain forest, and southern pine stands, and particularly common in forest openings created by disturbance, such as treefall, logging, or disease. Lonicera japonica continues to be planted for landscape purposes in gardens and along highways.
Lonicera japonica grows most vigorously in full sun and on rich soil, but is shade and drought tolerant and therefore able to grow in a wide variety of habitats. It develops high frequency and cover in young forests while densely shaded, mature forests support fewer, and smaller, colonies (Robertson et al. 1994). Lonicera japonica usually invades disturbed communities and rarely colonizes deeply shaded, mature forests unless canopy openings are created by human disturbances or natural processes (disease, wind throw, drought, etc.). In Virginia Lonicera japonica quickly invaded a former forest site destroyed by avalanche, and it grew vigorously in a forest opening in Arkansas. This species can persist in low numbers in relatively undisturbed forest and then "break out" following disturbances that open the canopy, e.g.; windthrow, ice storm, disease, scouring flood, or drought. Once established, Lonicera japonica's dense canopy inhibits establishment of later successional species. Lonicera japonica rarely invades deeply shaded, mature forests unless the canopy is somehow opened.
In Pennsylvania, Lonicera japonica is a major component of the third stage of succession in old fields, increasing after fields have been abandoned for four years. In New Jersey Lonicera japonica invaded an oldfield 13 years after abandonment, and was present for at least 18 years. In Virginia Lonicera japonica, is most abundant in the piedmont and coastal plant forests. In Illinois Lonicera japonica grows where overstory canopy provides filtered light, especially oak forests, cedar glades, and barrens, and along the banks of streams where the natural break in canopy creates a light opening. Plants then spread into adjacent shaded forest. Lonicera japonica has been found on Michigan sand dunes, and persists near abandoned homesites in the Chicago region. In Indiana, Lonicera japonica is abundant in urban forest preserves, but is absent from woodlots isolated by agricultural fields and distant from urban areas.
Lonicera japonica is a strong competitor due to wide seed dispersal, rapid growth rate, extended growing season, ability to capture resources both above- and below-ground, wide habitat adaptability, and lack of natural enemies. Some of these factors have received considerable study, while others have been given little or no attention.
Lonicera japonica blooms most prolifically in full sun, and decreases flowering activity as light decreases; in 8% of full light no flowers are produced. The blooming period extends from April to December in Georgia, late May to October in Kentucky (Sather, personal communication), May to June in Illinois, and June in Michigan. Flowers open a few hours before sunset, and remain open for approximately three days. In Wales, the majority of flowers are pollinated the day after opening by bumblebees (Bombus lucorum and B. pascuorum). Other bee species may be potential pollinators, as nectar is available to species with tongues less than or equal to 4 mm long. Flowers remain open at night, indicating the possibility for moth pollination. In the United States Lonicera japonica is probably pollinated by a variety of insects, due to its extended blooming season and wide geographical range.
Relatively few studies have documented seed production, seed viability, germination requirements, or seedling establishment.
The inconspicuous black berries contain 2-3 seeds. Fruit production is much higher in full sun than in shade (average 222 vs. 11 g seeds per plant, respectively) in Texas. Fruit production decreases as soil nitrogen increases. Seed viability is highly variable. Leatherman (1955) determined that 85% of seed were viable, and obtained 63% germination. Haywood (1994) attempted to study long-term seed viability, but seed was unsound when collected. This variation is typical of the Lonicera genus, which is characterized by having variable seedcoat dormancy, embryo dormancy, and/or no dormancy both within and among species. Bruner (1967) reported rapid growth from seed in South Carolina, and Carter and Teramura (1988b) stated that Lonicera japonica reproduces abundantly from seed. Berries are consumed by a number of birds including robin, turkey, quail, bluebird, and goldfinch, which then disseminate the seeds.
Rate of growth from the seedling stage is not known; most researchers and nurseries propagate Lonicera japonica from stem cuttings, particularly the var. halliana, which forms roots "wherever the canes touch moist ground". Leatherman (1955) suggested that seedlings likely photosynthesize shortly after germination, due to the low food reserves in each seed. Seedlings are known to establish in shaded understories, which implies that light may not be necessary for seed germination. Seedling growth is apparently slow for the first two years. Lonicera japonica is drought sensitive, particularly at the seedling stage. Biomass appears to decline with summer drought.
Once established, Lonicera japonica is capable of extremely vigorous growth. In a moist bottomland forest vines overtopped a 4.5 m tree in one year, although growth rates of 1.5 m/year may be more typical. Bell et al. (1988) recorded a maximum shoot elongation of 4.6 mm/day in Maryland. This rapid growth rate allows Lonicera japonica to outcompete native trees; In one year, Lonicera japonica overtopped three-year old sweetgum (Liquidambar styraciflua) trees. Lonicera japonica vines spread both vertically and horizontally.
Individual vines have numerous long vegetative runners; the combined length of lateral and sublateral runners from one sprout in one year exceeded 15 m. Vines in high light have been recorded with > 7 runners, each over 60 cm long. The runners develop roots at nodes in contact with soil, and thus form dense mats. If the above ground parts are severed, each new root system develops into a separate, but genetically identical, plant. The root system has been recorded at up to 3 m across and 1 m deep. Roots are highly competitive with native species (Carter and Teramura 1988b).
Lonicera japonica's climbing architecture is adapted to early successional forest, which typically has small diameter trees and a dense understory. The vines twine about vegetation in closely spaced spirals, thus creating a strong support structure that permits them to remain upright after the host tree is killed. Individual shoots may be very long, but due to the numerous spirals, a vine's height above the ground may not be great. Japanese honeysuckle vines typically climb stems <15 cm diameter. Larger stems are rarely used as hosts, as Lonicera japonica cannot climb wide boles unless small branches or other vines are present to provide support.
Longevity of individual plants has not been measured. As Lonicera japonica reproduces vegetatively, life span of individual stems or roots is not a measure of genet longevity.
Lonicera japonica is adapted to growing in 25-100% of full light, and grows vigorously in full sun. Stem density is greatest in full light, and decreases with increasing shade: In Pennsylvania, Robertson et al. (1994) recorded mean stem densities of 25.4/m2 in an oldfield, 15/m2 in a thicket, 13.6/m2 in a woodland, and 8.6/m2 and 8.1/m2 in riparian forest and upland mature forest, respectively. Stem density was similarly high in both oak and maple associations. In Washington D.C. Lonicera japonica produced good growth at 47% of full sun. In this location winter light measurements in closed forest range from 49% to 86% of full light. Lonicera japonica is able to persist in deciduous forest at low summer light intensities, and put on growth in winter, or when canopy gaps occur.
Lonicera japonica tolerates low light conditions, and may spread vegetatively, but rarely produces flowers or fruits under low light (25% of full light). Honeysuckle plants are severely stressed in low light, and lose substantial amounts of aboveground biomass after long periods of low light: Blair (1982) reported that leaf biomass declined 94% after two years at very low light (8% of full sunlight), and plants suffered stem dieback and leaf loss, but did not die. Leatherman (1955) similarly reported that half of her experimental cuttings survived at 10% of full light, and the majority survived at 25% of full light. Once established, Lonicera japonica can persist at low light levels with little or even negative growth, and respond to winter sun and canopy openings with more vigorous growth. Interestingly, as a twining vine Lonicera japonica is less physiologically adapted to low light levels than native tendril climbing vines, such as Parthenocissus quinquefolia, which can rapidly climb up supporting trees to reach higher light levels.
Lonicera japonica has a long photosynthetic season due to its evergreen nature and its ability to grow in cold temperatures. Lonicera japonica shoots grow until the first frost, apparently because they are able to lignify rapidly, which gives them greater cold-hardiness than more tender species. In southern locales Lonicera japonica retains its old leaves over winter permitting year-round photosynthesis. In these areas, Lonicera japonica leaves are physiologically active during the winter and can grow when minimum predawn air temperatures are at or above -3° C. At these temperatures, net photosynthetic rates on warm winter days are comparable to those in summer. The presence of old leaves during the period of new-leaf formation (January - March), combined with the higher photosynthetic rates in new leaves, increases total carbon gain and thereby growth rate and invasiveness. Shoots produce an early burst of growth in spring, before native species leaf out.
In the northern states Lonicera japonica retains its leaves until late December or January (semi-evergreen), while native trees lose their leaves in October. The vines continue to photosynthesize for several months after overstory trees have dropped their leaves, which allows them to maintain presence in low light communities. In Maryland, Lonicera japonica is physiologically active for 9 weeks after native deciduous vines have gone dormant (Parthenocissus quinquefolia and Vitis vulpina). In spring Lonicera japonica begins growth some two months earlier than native species, from the period when temperatures are above freezing, until deciduous trees produce new leaves. Thomas (1980) calculated that in the Washington D.C. area there are an average of 52 days/year between first and last frost when temperature and light conditions in closed canopy forests are adequate for Lonicera japonica photosynthesis.
Lonicera japonica leaves are unaffected by minimum temperatures of -0.6° C, and continue to function, at lower efficiency, until temperatures drop below -3.0° C. The relatively high rate of leaf gas exchange in autumn, winter, and spring indicates that carbon gain during this period may contribute substantially to Lonicera japonica's rapid growth rate. Although Lonicera japonica leaves photosynthesize in winter, the lowered activity reduces effectiveness of foliar herbicides applied after the first frost. In Tennessee, defoliation occurred at -26° C, but plants were not apparently killed.
Lonicera japonica is spread primarily by birds, which consume the fruits and pass the seeds, carrying them from landscape plantings to natural areas and disseminating them in forest openings and disturbance zones. Once established, Lonicera japonica can develop a large seedbank that germinates when the soil is disturbed. This attribute led to a dramatic increase in southern states in the 1950's, when timber companies promoted intensive site preparations (discing, burning, bush-hogging) to facilitate tree regeneration after clearcutting. Honeysuckle grew so rapidly from both seedbank and top-killed plants that tree seedlings were outcompeted. Consequently, forest companies have conducted much of the research to identify herbicides that control Lonicera japonica.
Originally introduced as a landscape plant, Lonicera japonica is still considered a desirable species by some landscapers, highway designers, and wildlife managers. Wildlife managers promote increased growth of Lonicera japonica to provide winter forage, particularly for deer. Landscape architects plant Lonicera japonica for its fragrant flowers and rapid growth, and highway designers use the plant for erosion control and bank stabilization.
In China Lonicera japonica is a valued medicinal herb that contains anti-complementary polysaccharides. Polyphenolic compounds isolated from Lonicera japonica inhibit human platelet activation and provide protection from cellular injury, and thus help maintain human vascular homeostasis. Aden I, a mixture of Lonicera japonica flower buds and parts of other plants, has both antibiotic and antiviral effects, comparable to results produced by standard antibiotics. Leaves and flowers are used in the therapy of chicken pox, and may be used as a food additive to increase productivity of broiler chickens in Korea.
In Illinois, the sale and distribution of Lonicera japonica is prohibited under the Illinois Exotic Weed Act (1988).
The only technique that could control Lonicera japonica on a regional scale is biological control, but as of 1997 no formal program had been established. Interestingly, in China, a biocontrol program using Sclerodermus spp. was established to protect Lonicera japonica from the cerambycid Xylotrechus grayi. Lonicera japonica is utilized by some insects in its native habitat and the U.S. In Sichuan, China, Lonicera japonica growing near cottonfields is an early spring host for aphids that feed on crops later in the growing season. In North Carolina, the two-spotted spider mite (Tetranychus urticae), an agricultural pest in corn and peanut fields, overwinters on Lonicera japonica growing on field margins.  Lonicera japonica is also a suitable host for the cicadellid cotton pest (Empoasca biguttula) in Hunan, China, and may be a host for tobacco leaf curl virus, which was detected in the horticultural variety Lonicera japonica var. aureo-reticulata. The vine is susceptible to honeysuckle latent virus, and to tobacco leaf curl bigeminivirus (TLCV) transmitted by whiteflies.
Fire removes above-ground vegetation, and reduces new growth, but does not kill most Lonicera japonica roots, and surviving roots produce new sprouts that return to pre-burn levels of cover within a few years. A single spring fire reduced Japanese honeysuckle cover 50% in Illinois. Two sequential fires topkilled Lonicera japonica, reducing crown volume (m3/ha) by 80%, but new growth from root sprouts maintained Lonicera japonica as a dominant groundcover species in North Carolina. In Virginia burning is used to reduce abundance of Lonicera japonica, and inhibit spread for 1-2 growing seasons. Prescribed burning significantly reduced Lonicera japonica biomass in Tennessee, by 93% when burned in October, and by 59% when burned January - March. Top-killed honeysuckle resprouted in spring (March - April), apparently from roots or runners just below the unburned litter layer. In this situation, follow-up application of 2% glyphosate in spring, 2 - 6 months after burning, appeared to control honeysuckle better on unburned than burned plots, possibly because tall herbaceous vegetation that grew up after the fire on the burned plots intercepted the herbicide before it could reach the shorter honeysuckle resprouts. In Texas, burning in February removed all above ground foliage, but did not kill plants. However, burned plants produced fewer and shorter runners than unburned plants, and fire therefore reduced total vegetative growth.
Combining fire and herbicides may prove to be more effective than either method by itself if late autumn or winter burns are used to reduce Japanese honeysuckle biomass when most native species are dormant and all resprouts are then treated with a foliar application of glyphosate about a month after they emerge. Prescribed burns may also be used to help prevent spread of Japanese honeysuckle because seedlings and young plants are most susceptible to fires.
The evergreen and semi-evergreen nature of Lonicera japonica allows application of herbicides when many native species are dormant. Timing of application is critical to effectiveness; in general, applying herbicide shortly after the first killing frost, and before the first hard frost (ca. -4.0° C) is most effective. Herbicide effectiveness can be reduced in areas where large stones or fallen logs protect root crowns from soil-active herbicides or where overtopping vegetation intercepts foliar herbicides. Many herbicides produce a short-term reduction in foliar coverage, but do not kill the plant and buds left undamaged by the herbicide can produce new growth that often exceeds growth from untreated plants within a year. A foliar application of 1.5% glyphosate shortly after the first frost appears to be the most effective treatment. Treated plants should be re-examined at the end of the second growing season, as plants can recover from herbicide application.
GLYPHOSATE (brand names include: Roundup®, Rodeo®, Accord®)
- October applications of 0.75% and 1.5% v/v glyphosate killed 99% of treated Lonicera japonica within six months in Delaware, and few plants resprouted within 30 months of treatment. The two application rates were equally effective. The same experiment conducted in December resulted in 68% mortality at the lower concentration, and 86% mortality at the higher concentration, and regrowth from buds was much greater than in plants treated in October. The authors concluded that timing of application was critical; applying glyphosate within 2 days of the first frost resulted in very high mortality. After the first frost, higher concentrations of glyphosate were needed to achieve somewhat lower mortality. Defoliation after glyphosate treatment was very slow; only 5-15% of leaves were gone one month after treatment, although 78-90% of stems were dead.
- A mid-August application of 2.2 kg/ha glyphosate controlled 83% of actively growing Lonicera japonica in North Carolina; control was reduced under drought conditions. Glyphosate (2 lb active ingredient/gal) at 1 to 1.5 gallons/acre controlled "most" Lonicera japonica in Alabama.
- In Arkansas, a 6.72 kg active ingredient/ha application resulted in 85% control after one growing season, and 80% control after two growing seasons. Lower application rates were less effective two years after treatment.
- Effectiveness of glyphosate increased linearly with increasing herbicide concentration (0.48-4.8% w/w), but no concentration gave complete control with one application; repeated treatment with 4.8% glyphosate produced complete shoot necrosis in only 50% of plants.
- Efficacy of glyphosate was not increased by addition of surfactants.
DICHLORPROP + 2,4-D
- Dichlorprop mixed with 2,4-D at 3.6 grams active ingredient/liter (1.5% v/v) resulted in 94% mortality when applied within two days of the first frost in October, but only 46% mortality when applied in December. Thirty months after treatment, 14% of stems sprayed in October resprouted, and 75% of stems sprayed in December produced new growth.
2,4-D + PICLORAM (brand names include: Tordon®)
- Picloram is a restricted use soil-active herbicide that is prohibited in California, as it is relatively persistent and subject to leaching.
- Tordon 101® (4:1 2,4-D amine + picloram, at 1 to 2 gal/acre) "reduced existing honeysuckle to a few surviving crowns". Tordon 10K® at 50 lb/acre had similar effectiveness.
- Tordon 101® at 10 gal acre reduced foliage by 72.5% one year after treatment; a second application of Tordon 101® reduced foliage by a total of 90% one year after re treatment
- A foliar spray of Tordon 101® at 2.8-8.4 kg/ha gave 84-94% control in a pine stand, similar to control provided by amitrole at 2.24 and 4.48 kg/ha.
TEBUTHIURON (brand names include: Spike®)
- Spike 80W® (80% tebuthiuron) and Spike 20p® (20% tebuthiuron) provided very effective control when applied at 4-5 lbs active ingredient/acre, "resulting in essentially bare plots with yellowing sprigs of vegetation".
DICAMBA (brand names include: Banvel®, Brushkiller®)
- Banvel® 720 (2 lb 2,4-D and 1 lb dicamba) was very effective when applied at 4 gal/acre, but had only partial effectiveness at 3 gallons/acre.
- Lower rates of Dicamba, as in Brushkiller® 4-41 and 10-51, resulted in limited or no mortality. In fact, Lonicera japonica growth was stimulated by application of Brushkiller® 10-51.
SULFOMETURON (brand names include: Oust®)
- A February application of sulfometuron methyl in South Carolina at .25 lb/acre active ingredient, applied when vegetation is less than 30-45 cm high, is recommended for control of Lonicera japonica in loblolly pine stands.
- In Georgia, Lonicera japonica was not controlled by a late application of Sulfometuron applied at 3 oz/acre 
- Lonicera japonica was almost completely killed (99% mortality) by a May application of 2 oz metsulfuron-methyl + 0.25% surfactant in central Georgia 
- In Illinois, herbicides that are not used by the Department of Conservation due to ineffectiveness or environmental persistence are: picloram; amitrole; aminotriazolel atrazine; dicamba; dicamba + 2,4-D; 2,4-D; DPX 5648; fenac; fenuron; simazine; and triclopyr (brand names for triclopyr include Garlon 3A®, Garlon 4® and Brush-B-Gone®).
- Hexazinone at 2.24 and 6.72 kg Active ingredient/ha was ineffective, as was application at 1 or 2 lb active ingredient/acre. Hexazinone pellets at 8 lb active ingredient/acre reduced Lonicera japonica cover from 100% to 25% cover after three years, while a 2 lb/acre rate resulted in a decrease in cover from 100% to 52% over the same time period.
- Oryzalin is apparently ineffective, as it is recommended for use in controlling weeds that threaten Lonicera japonica planted as a groundcover
- Brushkiller® 10-51 at 1.5 gal/acre "encouraged" growth of Lonicera japonica. Brushkiller® 170 resulted in a 45% decrease in foliar cover one year after June treatment.
- June application of 2,4-D (4 lb active ingredient/acre at 10 gal/acre) increased foliar growth of Lonicera japonica by 48% one year after treatment (control plants increased by 0.9%).
- June application of Banvel® resulted in increased foliar growth one year after treatment.
- Triclopyr in both ester and salt formulations (3 and 4lb/gal, respectively) and as an ester combined with 2,4-D (1 and 2lb/gal respectively) failed to control Lonicera japonica one year after treatment.  However, in Illinois the latter formulation is reputedly effective.
Mowing, Discing and Pulling
Removing the above-ground portion of Lonicera japonica reduces current-year growth but does not kill the plant, and generally stimulates dense regrowth. Cut material can take root and should therefore be removed from the site (not practical with most infestations).
Mowing is an ineffective control method, stimulating growth and encouraging formation of dense, albeit shorter, mats. Plants mowed in February formed a dense, 20 cm tall mat within two months, growing from cut stems and rooting from severed runners; by the following November (21 months later) mowed plants were 60 cm high. Twice-yearly mowing in Virginia slowed vegetative spread but increased stem density.
Bush-hogging is an ineffective control, as Lonicera japonica re-invades within one growing season.
Discing is apparently an effective control method: McLemore (1985) reported that "control of the honeysuckle was still effective after two years". Discing depth was not indicated. Discing is a highly destructive procedure that destroys native groundlayer species, and may stimulate Lonicera japonica seed bank germination.
Hand-pulling is a time-consuming procedure with limited effectiveness, as the entire plant (roots and shoots) must be removed. Pulling may be a practical method to remove small patches of seedlings.
- Munger, Gregory T. 2002. Lonicera japonica. Fire Effects Information System, U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory
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