Synonym(s): Convolvulus ambigens, Convolvulus incanus, Strophocaulos arvensis
Family: Convolvulaceae (Morning-Glory Family)
Duration and Habit: Perennial Vine
Viny perennial with an extensive system of deep creeping roots and rhizomes. Field bindweed is considered one of the most noxious weeds of agricultural fields throughout temperate regions of the world. Plants typically develop large patches and are difficult to control. It is troublesome in numerous crops, but is especially problematic in cereals, beans, and potatoes. Heavy infestations in cereal crops can reduce harvest yields 30-40% or more. In California, it is estimated that 770,000 hectares of agricultural land was infested in 1981. Plants can harbor the viruses that cause potato X disease, tomato spotted wilt, and vaccinium false bottom. Foliage contains tropane alkaloids and can cause intestinal problems in horses grazing on heavily infested pastures. Two biocontrol agents, the bindweed gall mite (Aceria malherbae) and bindweed moth (Tyta luctuosa), are cleared for release in the U.S. However, these biocontrol agents are not registered for use in California since uncommon native morningglory (Calystegia) species may also be susceptible to attack. Introduced from Europe.
Native Lookalikes: Currently no information available here yet, or there are no native Texas species that could be confused with Field bindweed.
Biology & Spread: Reproduces by seed and vegetatively from deep creeping roots and rhizomes. Most seeds fall near the parent plant, but some seeds may disperse to greater distances with water, agricultural activities, and animals. Seeds are hard coated and can survive ingestion by birds and other animals. Most seeds can imbibe water and germinate 10-15 days after pollination. However, seed coats mature 15-30 days after pollination, and ~ 80% of seeds become impermeable to water. Impermeable seeds require scarification or degradation of the seed coat by microbial action to imbibe water and germinate. Seeds germinate throughout the growing season, but peak germination usually occurs mid-spring through early summer. Germination can occur under various temperature regimes, from 5-40? C, but is highest and most rapid when temperatures fluctuate from 35-20? C. A 3-6 week period of chilling to ~ 5? C appears to increase germination. Light is not required. A large portion of the seed bank remains dormant from year to year. Under field conditions, seed can survive for 20 years or more. A high percent of seed under dry storage can survive for at least 50 years. Seed production is highly variable. Dry, sunny conditions and calcareous soils favor seed production. Frequent cultivation, rain, or heavy, wet soils can inhibit seed set. One plant can produce up to 500 seeds. In the field, young plants seldom produce seed the first season. Root starch reserves are highest from mid-summer through early fall, but then decline rapidly with conversion to sugars. Root carbohydrates are lowest in mid-spring before flowers develop. Maximum translocation of carbohydrates from shoots to roots occurs from the bud to full flower stages. Conditioned roots can survive temperatures as low as ? 6? C. Most new shoots appear in early spring. Undisturbed patches can expand their radius up to 10 m per year. Root fragments as small as 5 cm can generate new shoots.
Deep cultivation before flowering and repeated cultivation when new shoots appear for 1-several years, followed by rotation to competitive crops such as winter wheat or alfalfa, can control troublesome infestations in agricultural fields. Where practical, flooding fields with water to a depth of 15-25 cm for 60 to 90 days can effectively eliminate most field bindweed plants. Cultivation to a depth of at least 10 cm (4 in.) within 3 weeks after emergence can control seedlings. Stems and leaf surfaces have a texture that is difficult to wet. The addition of a wetting agent to certain herbicides may make them more effective. Some field bindweed biotypes are less susceptible to certain herbicides.
U.S. Habitat: Cultivated fields, orchards, vineyards, gardens, pastures, abandoned fields, roadsides, waste places. Grows best on moist fertile soils. Tolerates poor, dry, gravelly soils, but seldom grows in wet soils. Inhabits regions with temperate, Mediterranean, and tropical climates.
U.S. Nativity: Introduced to U.S.
Native Origin: Europe, Asia (Bailey, L.H. and E.Z. Bailey, Hortus Third: A Concise Dictionary of Plants Cultivated in the United States and Canada, MacMillan Publishing Co., Inc., New York , (1977).); NatureServe Explorer
U.S. Present: AL, AR, AZ, CA, CO, CT, DE, FL, GA, HI, IA, ID, IL, IN, KS, KY, LA, MA, MD, ME, MI, MN, MO, MS, MT, NC, ND, NE, NH, NJ, NM, NV, NY, OH, OK, OR, PA, RI, SC, SD, TN, TX, UT, VA, VT, WA, WI, WV, WY
Distribution: Throughout West.
List All Observations of Convolvulus arvensis reported by Citizen Scientists
Western morningglory [Calystegia occidentalis (A. Gray) Brummitt] is a native perennial that closely resembles field bindweed. It is a desirable component of the vegetation in natural communities, but is sometimes weedy in agricultural or managed forest systems. Unlike field bindweed, western morningglory typically has flowers 2.5-4 cm long, calyxes greater than 7 mm long, stigma lobes flattened, and bracts mostly attached less than 10 mm below the flowers. In addition, western morningglory is hairy throughout, and the basal lobes of leaves are often squared to slightly indented or 2-lobed. Western morningglory grows on dry slopes in chaparral and pine forests throughout California, except the Mojave and Sonoran deserts, to 2700 m (8900 ft). Hollyhock bindweed [Convolvulus althaeoides L.][Bayer code: none] is a showy perennial with purple to deep pink flowers introduced from the Mediterranean region. Hollyhock bindweed is distinguished by having some upper leaves deeply lobed. It grows in localized populations on disturbed sites in the northern Sierra Nevada foothills (Nevada Co.), Transverse Ranges, Peninsular Ranges, and Southwest region, to 1000 m (3300 ft).
Biology and Prevention: Field bindweed is a very serious perennial vine that may reduce crop yields, increase irrigation costs, and interfere with harvesting. Field bindweed is an excellent competitor for soil moisture and thrives in dryland agricultural systems. Its extensive root system utilizes deep soil moisture and allows the plant to withstand serious drought. Additionally, the plant is capable of summer dormancy and new shoots emerge from adventitious buds on vertical and lateral roots when rainfall returns.
Field bindweed also occurs in disturbed rangelands and wildlands. In these areas it may establish in open grasslands above riparian areas where frequent disturbance occurs such as that caused by feral pigs. It may form small patches but generally does not constitute a serious threat. It is also frequently found in conservation or restoration areas that were historically farmed. These previously established patches are extremely difficult to eliminate and inhibit restoration efforts. In rangelands, field bindweed rarely overlaps with winter and spring grazing systems due to its emergence in late spring. It provides very little green summer forage, as sheep and cattle generally avoid it.
Field bindweed is also a serious weed of many irrigated crops, young orchards and vineyards. It establishes along irrigation drip lines in vineyards and uses soil moisture and nutrients applied for the crop. It is strongly competitive with many seedling vegetables and establishes in perennial crops such as alfalfa or asparagus. Field bindweed is also a frequent problem in landscaping and ornamental areas. Rootstocks and seeds are often transported in soil and mulch to new areas.
When dealing with field bindweed, the farmer, land manager or home owner must recognize that there are no "quick fix" solutions to eliminate it. It is possible to bring bindweed to a manageable level, but it requires intensive effort and a watchful eye. Additionally, even when infestations are reduced to a minimal level, care must be take to prevent reestablishment from seed, which are capable of persisting in the soil for 30-50 years. There are several keys for field bindweed management.
1. Use tillage cautiously around patches to avoid spreading it. Always clean tillage equipment before moving to new fields.
2. Always follow good production practices to get a competitive, healthy, crop stand established, i.e. fertilize according to soil testing recommendations, plant at optimum row spacing, plant populations, and planting dates.
3. A severe infestation of field bindweed will be very difficult to control in broadleaf crops, due to a lack of selective herbicides. Incorporating winter annual cereals into the rotation will increase competitive suppression and allow for better herbicide selection for field bindweed control.
4. Any lax in management for even one year may allow field bindweed to rapidly recover. A long-term plan should be developed if sustainable control is desired.
5. Additionally, severe infestations of field bindweed may suppress the germination of other weed seeds in the seedbank. When field bindweed is controlled, several other species may "suddenly appear." Knowing the field history may assist in preparing for this potential problem.
Mechanical: Tillage systems have generally provided negative results for field bindweed control. Field bindweed responds to plowing, discing, and rod weeding by increasing bud formation just below the tillage layer. New shoots rapidly emerge and carbohydrate reserves are replenished in a few weeks. Tillage is clearly effective on seedlings. However, plants may form perennial buds within six weeks of emergence. Tillage used for seedling control should be conducted within the first few weeks to prevent plants from surviving. Infrequent tillage used in fallowed fields or within orchards may actually promote field bindweed infestations by eliminating annual weed competition and spreading root fragments around. If field bindweed patches are evident, avoid tilling them to prevent spread of the rootstocks. In this case, spot treatment herbicide applications will be more effective. Intensive cultivation was historically used for field bindweed control. This entailed cultivating at least every two weeks to exhaust carbohydrate supplies in the roots. This type of tillage strategy is not recommended, due to the increased potential for erosion and soil moisture loss. Other intensive mechanical strategies include hand pulling or grubbing. These must be done repeatedly to be effective.
Biological: There are currently no registered biological control agents for field bindweed in California. However, there are two insects that are used in the Great Plains: the bindweed moth (Tyta luctuosa) was released in Arizona, Iowa, Missouri, Oklahoma, and Texas and the bindweed gall mite (Aceria malherbae) was released in Texas.
Chemical: Chemical control of field bindweed generally requires a multiple year approach. There are few herbicides that provide effective control. Always refer to the herbicide label for specific instructions and plantback restrictions. Treatments work best when applied to actively growing, healthy bindweed with 6-18 inch runners. When bindweed is under drought stress, the effectiveness of these treatments will likely be significantly reduced. Finally, it cannot be stressed enough that field bindweed management must be practiced on a continuous, year to year basis, even with the above recommended herbicide applications. No single treatment will eradicate field bindweed. However, these treatments will suppress bindweed populations to a manageable level.
Buhler, D. D., D. E. Stoltenberg, R. L. Becker, and J. L.Gunsolus. 1994. Perennial weed populations after 14 years of variable tillage and cropping practices. Weed Sci. 42:205-209.
DeGennaro, F. P. and S. C. Weller. 1984. Differential susceptibility of field bindweed (Convolvulus arvensis) biotypes to glyphosate. Weed Sci. 32:472-476.
Enloe, S. F., P. Westra, S. J. Nissen, S. D. Miller, and P. W. Stahlman. 1999. Use of quinclorac plus 2,4-D for controlling field bindweed (Convolvulus arvensis) in fallow. Weed Tech. In press.
Fenster, C. R. and G. A. Wicks. 1982. Fallow systems for winter wheat in western Nebraska. Agron. J. 74:9-13.
Frasier, J. C. 1948. Principal noxious perennial weeds of Kansas, with emphasis upon their root systems in relation to control. Kansas. Agric. Exp. Stn. Bull. 331. 45 pp.
Froud-Williams, R. J., R. J. Chancellor, and D. S. Drennon. 1981. Potential changes in weed floras associated with reduced-cultivation systems for cereal production in the temperate region. Weed Res. 21:99-109.
Phillips, W. M. and F. L. Timmons. 1954. Bindweed-how to control it. Kansas Agric. Exp. Stn. Bull. 366, Manhattan.
Rashed, M. H. and L. C. Haderlie. 1980. The relationship between anatomical and physiological aspects of field bindweed under water stress conditions. North Cent. Weed Control Conf. 35:26.
Stahler, L. M. 1948. Shade and soil moisture as factors in competition between selected crops and field bindweed, Convolvulus arvensis. J. Am. Soc. Agron. 40:490-502.
Westra, P., P. Chapman, P. W. Stahlman, S. D. Miller, and P. K. Fay. 1992. Field bindweed (Convolvulus arvensis) control with various herbicide combinations. Weed Technol. 6:949-955.
Whitworth, J. W. and T. J. Muzik. 1967. Differential response of selected clones of bindweed to 2,4-D. Weeds 15:275-280.
Wiese, A. F. and D. E. Lavake. 1985. Control of field bindweed (Convolvulus arvensis) with postemergence herbicides. Weed Sci. 34:77-80.
Encycloweedia, California Department of Food and Agriculture
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