dcsimg

Associations ( Inglês )

fornecido por BioImages, the virtual fieldguide, UK
Foodplant / gall
Eriophyes convolvuli causes gall of leaf of Convolvulus arvensis

In Great Britain and/or Ireland:
Foodplant / parasite
Erysiphe convolvuli parasitises live Convolvulus arvensis

Foodplant / open feeder
adult of Longitarsus pellucidus grazes on leaf of Convolvulus arvensis

Foodplant / internal feeder
larva of Melanagromyza albocilia feeds within stem of Convolvulus arvensis

Foodplant / spot causer
epiphyllous, immersed, brown pycnidium of Septoria coelomycetous anamorph of Septoria convolvuli causes spots on fading leaf of Convolvulus arvensis
Remarks: season: 7-8

Foodplant / spot causer
few, hypophyllous, immersed, pallid pycnidium of Stagonospora coelomycetous anamorph of Stagonospora calystegiae causes spots on fading leaf of Convolvulus arvensis
Remarks: season: 7-9

Foodplant / pathogen
immersed sorus of Thecaphora seminis-convolvuli infects and damages seeds (in capsule) of Convolvulus arvensis
Remarks: season: 8-10

Foodplant / feeds on
adult of Thrips atratus feeds on live flower of Convolvulus arvensis

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BioImages
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BioImages

Description ( Inglês )

fornecido por eFloras
Herbs perennial, with ± woody rhizomes. Stems prostrate or twining, to 1 m tall, glabrous or sparsely pubescent. Petiole 0.3-2 cm; leaf blade ovate-oblong to ovate, 1.5-5 X 1-4 cm, glabrous or pubescent, base hastate, sagittate, or cordate, apex obtuse, mucronulate; prominently 3-veined basally, upper parts pinnately veined. Inflorescences axillary, cymose, 1-3-flowered; peduncle 3-8 cm; bracts 2, linear, ca. 3 mm. Pedicel ca. 4 as long as calyx. Sepals unequal, 3.5-5 mm; outer 2 broadly oblong to obovate, shorter, abaxially sparsely pubescent or glabrous, margin ± ciliate, apex retuse; inner ones ovate-circular, margin membranous, apex obtuse or retuse. Corolla white or pink, broadly funnelform, 1.5-2.6 cm, midpetaline bands pubescent outside distally; limb shallowly 5-lobed. Stamens included, unequal; filaments minutely scaly basally. Disc cupular. Ovary ovoid, glabrous or sparsely pubescent. Stigmas cylindric. Capsule ovoid to subglobose, 5-8 mm, glabrous. Seeds 4 or fewer, dark brown or black, ovoid, 3-4 mm, tuberculate. Fl. Jun-Aug, fr. Jun-Sep. 2n = 24, 48, 50.
licença
cc-by-nc-sa-3.0
direitos autorais
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
citação bibliográfica
Flora of China Vol. 16: 291 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
fonte
Flora of China @ eFloras.org
editor
Wu Zhengyi, Peter H. Raven & Hong Deyuan
projeto
eFloras.org
original
visite a fonte
site do parceiro
eFloras

Distribution ( Inglês )

fornecido por eFloras
Temperate regions.
licença
cc-by-nc-sa-3.0
direitos autorais
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
citação bibliográfica
Annotated Checklist of the Flowering Plants of Nepal Vol. 0 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
fonte
Annotated Checklist of the Flowering Plants of Nepal @ eFloras.org
autor
K.K. Shrestha, J.R. Press and D.A. Sutton
projeto
eFloras.org
original
visite a fonte
site do parceiro
eFloras

Distribution ( Inglês )

fornecido por eFloras
Anhui, Gansu, Hebei, Heilongjiang, Henan, Hubei, Jiangsu, Jilin, Liaoning, Nei Mongol, Ningxia, Qinghai, Shaanxi, Shandong, Shanxi, Sichuan, Xinjiang, Xizang [Asia, Europe, North America, South America].
licença
cc-by-nc-sa-3.0
direitos autorais
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
citação bibliográfica
Flora of China Vol. 16: 291 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
fonte
Flora of China @ eFloras.org
editor
Wu Zhengyi, Peter H. Raven & Hong Deyuan
projeto
eFloras.org
original
visite a fonte
site do parceiro
eFloras

Elevation Range ( Inglês )

fornecido por eFloras
2600-4100 m
licença
cc-by-nc-sa-3.0
direitos autorais
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
citação bibliográfica
Annotated Checklist of the Flowering Plants of Nepal Vol. 0 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
fonte
Annotated Checklist of the Flowering Plants of Nepal @ eFloras.org
autor
K.K. Shrestha, J.R. Press and D.A. Sutton
projeto
eFloras.org
original
visite a fonte
site do parceiro
eFloras

Habitat ( Inglês )

fornecido por eFloras
Cultivated areas, wasteland, roadsides, grassy slopes; 600-4500 m.
licença
cc-by-nc-sa-3.0
direitos autorais
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
citação bibliográfica
Flora of China Vol. 16: 291 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
fonte
Flora of China @ eFloras.org
editor
Wu Zhengyi, Peter H. Raven & Hong Deyuan
projeto
eFloras.org
original
visite a fonte
site do parceiro
eFloras

Synonym ( Inglês )

fornecido por eFloras
Convolvulus arvensis var. angustatus Ledebour; C. arvensis var. crassifolius Choisy; C. arvensis var. linearifolius Choisy; C. arvensis var. sagittatus Ledebour; C. arvensis var. sagittifolius Turczaninow; C. chinensis Ker Gawler; C. sagittifolius (Fischer) Liou & Ling.
licença
cc-by-nc-sa-3.0
direitos autorais
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
citação bibliográfica
Flora of China Vol. 16: 291 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
fonte
Flora of China @ eFloras.org
editor
Wu Zhengyi, Peter H. Raven & Hong Deyuan
projeto
eFloras.org
original
visite a fonte
site do parceiro
eFloras

Broad-scale Impacts of Fire ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: seed, severity

While no information is available regarding the direct effects of fire on field
bindweed plants and seeds, some information on the effects of various heat
treatments on viability of field bindweed seed is available.

Harmon and Keim [57] tested the longevity of several weed
seeds after burial in horse and cow manure over a period of 1 to 4 months. The
temperature in the horse and cow manure reached 158
°F (66 °C) and 150
°F (70 °C),
respectively, in 2 weeks. Percent germination of field bindweed seed before
burial was 84%. In horse manure, germination was 6% after 1 month (without acid
treatment), 8% after 2 months (with acid treatment), and 0% thereafter. In cow
manure, germination was 4% after 1 month (without acid treatment), 22% after 2
months (with acid treatment), 1% after 3 months (1 weak bindweed seedling was
obtained), and 0% thereafter. Field bindweed seeds retained viability longer
than all other weed seeds tested.
Similarly, most weed seeds tested by Wiese and others [148] were
killed after 3 days or more exposure at
120 °F (49 °C) in compost; it required 7 days of
exposure at 180 °F (83 °C) to kill
all field bindweed seed in compost. In dry air, all species survived 140
°F (60 °C) for 30
days. All seeds except field bindweed were killed in dry air by 160
°F (72 °C) for 3 days,
while it took 7 days of exposure at 180 °F (83
°C) to reduce viability of field bindweed seed from
about 30% to 7%, and 30 days to reduce field bindweed seed viability to 5%.
Field bindweed seed was
killed by a 12-day exposure in an outside storage
pile of compost. Ensiling field bindweed seed seemed to have no effect on its viability [156].
These results suggest that field bindweed seed may survive low severity fire.

licença
cc-publicdomain
citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Common Names ( Inglês )

fornecido por Fire Effects Information System Plants
field bindweed

field
morning-glory

morning glory

small bindweed

devil's guts
licença
cc-publicdomain
citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Conservation Status ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: forest, natural, seed

As of this writing (2004), field bindweed is classified as a noxious or
prohibited weed or weed seed in 35 states in the U.S. and 5 Canadian provinces [139].
See the Invaders, Plants, or APHIS
databases for more information. The Eastern Region of the U.S. Forest Service ranks
field bindweed as a Category 3 plant: often restricted to disturbed ground and not
especially invasive in undisturbed natural habitats [136].
licença
cc-publicdomain
citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Description ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: capsule, fruit, phenology, seed, vine

The following description of field bindweed is based on descriptions found in several florae
[30,64,65,71,81,88,127]. It provides
characteristics that may be relevant to fire ecology, and is not meant for
identification. Keys for identification are available (e.g. [60,64,65,88,146,149]). Proper identification is
important if control strategies are planned, as
field bindweed may closely resemble some native morning-glories.


Field bindweed is a perennial vine arising from deep, persistent, spreading roots. It has slender, trailing to
somewhat twining, branched
stems, 8 to 79 inches (20-200 cm) long, sometimes forming tangled mats. Herbage is glabrous to
pubescent and leaves are variable, 0.4 to 4 inches (1-10 cm) long and 0.1 to 2.4
inches (0.3-6 cm) wide, with
petioles 5-40 mm long. Peduncles arise from leaf axils, range from 0.2 to 2.4
inches (0.5-6 cm)
long, and bear 1 to several flowers. Corollas are broadly funnelform, 0.6 to 1.2
inches (1.5-3 cm)
long and 0.9 to 1.4 inches (2.2-3.5 cm) broad. Fruit is a capsule, 5-10 mm long, bearing 1 to 4
seeds, each about 3-4 mm long. Kennedy and Crafts [74] provide a detailed description
of the anatomy of field bindweed.

Several authors describe variations in botanical characteristics of field
bindweed. A review by Weaver and Riley [144] indicates the leaves of field
bindweed vary greatly in size and shape with environmental factors such as light intensity,
soil moisture, and damage due to frequent cultivation or defoliation. Degennaro
and Weller [35] identified and characterized 5 biotypes among field bindweed
clones collected from a field in Indiana. Consistent variations in leaf
morphology, floral characteristics, flowering capacity, phenology, vegetative
reproduction potential, and accumulation of shoot and root biomass were found
between biotypes when grown in a controlled environment. Pollination studies
showed that presumed biotypes were self-incompatible. The variability in growth
and reproduction observed in field bindweed biotypes may explain the survival
and adaptability of a field bindweed population as environmental conditions and
control practices change.


Several researchers have described the anatomy and development of field
bindweed roots (e.g. [34,47,74,75]). The root system is characterized by a taproot with large numbers of
annual lateral roots that develop adventitiously throughout its length, and penetrate
the soil in all directions
(see Seedling establishment/growth for more detail).
Some laterals are ephemeral and some are persistent. It is by
these lateral roots that plants spread horizontally. Shoot buds arise on these
horizontal laterals and develop into rhizomes which, reaching the surface,
establish new crowns [47,74]. The ability to
produce buds, together with the root food reserves, favors vegetative
reproduction and makes field bindweed plants persistent [74]
(see Asexual regeneration for more detail).


Field bindweed taproots may be 2 to 10 feet (0.5-3 m) or more long. Other
vertical roots may penetrate to depths of 17 to 30 feet (5-9 m) [10,66,75],
depending on climate and soil type. Lateral roots are found primarily in the top
12 inches (30 cm) of soil, and most commonly in the upper 4 to 6 inches
[47,75,128]. In field bindweed plants grown from root cuttings in a sandy loam
soil in Oxford, England 70% of lateral root spread was in the top 3 to 6 inches
(7.5-15 cm) of soil, and none was below 12 inches (30 cm) [34]. Similarly, Swan
[128] notes that the lateral roots are generally found within the top 12 inches
(30 cm) of soil, but approximately 1 third of the total root system is in the vertical roots
below the 24 inch (60 cm) zone. Estimates of the amount of root by weight in the upper
24 inches (60 cm) of soil range
from 50% to 70% [133,144]. The concentration of food
reserves increases with root depth, and maximum percentages of reserves were
found in roots 6 to 8 feet (2-2.4 m) deep [10].


Field bindweed from an old-field site in Ontario was among the few plant
species observed in the laboratory that were not infected with native arbuscular
mycorrhizal fungi [76]. Field bindweed plants growing on disturbed sites in Utah were infected
with vesicular-arbuscular mycorrhizae [102].


Root exudations may decrease the germination of some crop seed (Grummer 1957, as cited by [128]).

licença
cc-publicdomain
citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Distribution ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: adventitious, cover, presence, seed

Field bindweed is native to Europe and Asia. Field bindweed is successful in many types of
climates, including temperate, tropical, and mediterranean, but is most
troublesome for agriculture throughout the temperate zone, from 60°N
to 45°S latitude. Fifty-four countries report
field bindweed as a weed in 32 different crops [66].

Field bindweed most likely arrived in the
U.S. as contaminant in farm and garden seeds. Some
plants were introduced intentionally and planted ornamentally as ground cover or
in hanging baskets. It was first noted in Virginia in 1739 and was found all
along the eastern seaboard, from Virginia to Maine, by the early 1800s. Western
migration of field bindweed may have been hastened by the building of railroads; however,
field bindweed seeds
continued to arrive whenever immigrants settled new areas or whenever crop seed
was imported. A "bindweed plague" in the Great Plains in 1877 was attributed to Ukrainian settlers who
inadvertently brought the weed seed in wheat (Triticum spp.) seed during
the early 1870s. Field bindweed reputedly established in the Pacific Northwest when an
Oregon settler used it as a cover crop in his orchard. Field bindweed was evidently present
in California as early as 1838. By the end of the 1st quarter of the 20th
century, field bindweed was considered the "worst weed" in several states and a "serious
pest" in several others, especially west of the Mississippi ([95] and references therein).


The current North American distribution of field bindweed extends from the agricultural
regions of all provinces in Canada (except Newfoundland and Prince Edward
Island) southward throughout the United States and into northern Mexico. It is common to abundant
in the U.S., except in the extreme Southeast and parts of southern Texas, New Mexico, and
Arizona ([144] and references therein). Field bindweed is adventitious in Hawaii [121]. Plants database
provides a state distribution map of field bindweed. Field bindweed is
especially common in cultivated fields and gardens [30,37,50,54,58,60,64,72,81,88,106,110,141,146,149], along roadsides [30,37,50,54,72,81,110,127,141,146,149], railroads [141,146],
"disturbed sites" [37,96,151,153], and "waste places" [50,106,127,141,146]. It is
reported from ballast heaps in Nova Scotia [110].


A survey of weed specialists and herbaria in the continental U.S., conducted
in 1994 and 1995, found that field bindweed occurs at "serious" densities (> 1,000 acres/county) in 957
counties, "moderate" densities (250-1000 acres/county) in 845 counties; and
"low" densities
(< 250 acres/county) in 573 counties, in 47 of the 48 contiguous states.
Only Florida and the southern parts of states from South Carolina to Texas did
not report its presence. The authors also report that field bindweed infestations have increased
in several western states since 1970, but have decreased in importance in most Great Plains states [18].


The following lists suggest ecosystems and vegetation types in which field
bindweed may be invasive, especially following disturbance. It is unclear from
the literature which vegetation types may be susceptible to invasion by field
bindweed in the absence of disturbance. These lists were derived from known or perceived
ecological tolerances of field bindweed, are largely speculative, and may not be
exhaustive.

licença
cc-publicdomain
citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Fire Ecology ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: cover, fire regime, fire suppression, forbs, grassland, invasive species, litter, natural, nonnative species, seed, shrub, species richness, woodland

Fire adaptations:
There is no information available in the literature regarding fire adaptations of field bindweed. Some inferences
can be made regarding the likely response of field bindweed to fire based on its
reproductive strategies. Field bindweed has a deep and extensive root system with abundant
food reserves and can sprout repeatedly following removal of aboveground
growth [74,75].

Goodwin and others [51] present the following generalization about
rhizomatous weeds and fire, although they provide no supporting evidence.
"Growth of rhizomatous weeds is especially enhanced through the survival of
underground reproductive structures that have access to large energy reserves.
When above-ground weed growth is removed, such as by fire, vegetative shoot
production is strongly stimulated, directly producing great numbers of
individual weeds. Because of the established root reserves, these shoots are
immediately aggressive and highly competitive.

Field bindweed also produces varying amounts of long-lived, durable seed that
survives passing through the digestive tracts of various animals [57,104,111], and long periods
of composting and ensilage [148,156]
(see Discussion and Qualification of Fire Effect).
Considering its survival under such conditions, one might predict that
field bindweed seed would survive low- to moderate-severity fires; however, more information is needed.

FIRE REGIMES:
There is no information on FIRE REGIMES in areas where field bindweed is native or on the effects of FIRE REGIMES on
field bindweed in areas where it is invasive. The response of field bindweed to native
and imposed FIRE REGIMES probably varies among geographic locations, plant
community types, fire adaptations of native species, and other disturbance and
management regimes imposed at a particular site. More information on the effects
of native and imposed FIRE REGIMES on the establishment, persistence, and spread
of field bindweed are needed.

Frequent fire may deter field bindweed and other nonnative invasive species in temperate
grasslands. According to Knapp and Seastedt [77], fire and
grazing are necessary, integral ecosystem processes that maintain productivity
of tallgrass prairie by removing standing and fallen litter. Similarly, Leach
and Givnish [84] recommend prescribed burning (with specific guidelines) in
Wisconsin prairie remnants to maintain native plant diversity. A review by Grace
and others [53] suggests fire is only 1 type of disturbance that may affect the
establishment and spread of invasive species in temperate grasslands. Since fire
return intervals have been and will continue to be heavily influenced by land
use, fire suppression, and grazing, these other disturbances can be expected to
continue to play important roles in the future.

A 15-year study in C4-dominated grasslands (dominated by big bluestem (Andropogon
gerardii) and indiangrass (Sorghastrum nutans) and supporting many
nonnative species, including field bindweed) in Konza Prairie Research Natural
Area in eastern Kansas, indicated that patterns of disturbance (i.e. grazing and
fire) strongly affected nonnative plant cover and richness. In particular,
long-term annually burned sites had low cover and few, if any, nonnative
species, whereas richness and cover of exotic species was as much as 5 times higher in long-term unburned sites.
Although the effects of
grazing could not be tested directly, higher nonnative species richness was
associated with both annually burned and unburned grazing treatments. The
authors suggest in their review that annual burning increases the dominance
(i.e. production and abundance) of C4 grasses and decreases
production and abundance of the subdominant grasses and C3 forbs in
this grassland, and may indirectly prevent establishment of nonnative species
[119].

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

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
maple-beech-birch Acer-Fagus-Betula > 1,000 [143]
bluestem prairie Andropogon gerardii var. gerardii-Schizachyrium scoparium 79,101]
Nebraska sandhills prairie Andropogon gerardii var. paucipilus-Schizachyrium scoparium < 10
bluestem-Sacahuista prairie Andropogon littoralis-Spartina spartinae < 10
sagebrush steppe Artemisia tridentata/Pseudoroegneria spicata 20-70 [101]
basin big sagebrush Artemisia tridentata var. tridentata 12-43 [113]
mountain big sagebrush Artemisia tridentata var. vaseyana 15-40 [4,25,94]
Wyoming big sagebrush Artemisia tridentata var. wyomingensis 10-70 (40**) [140,154]
desert grasslands Bouteloua eriopoda and/or Pleuraphis mutica 5-100 [101]
plains grasslands Bouteloua spp. 101,152]
blue grama-needle-and-thread grass-western wheatgrass Bouteloua gracilis-Hesperostipa comata-Pascopyrum smithii 101,112,152]*
blue grama-buffalo grass Bouteloua gracilis-Buchloe dactyloides 101,152]*
grama-galleta steppe Bouteloua gracilis-Pleuraphis jamesii < 35 to < 100
blue grama-tobosa prairie Bouteloua gracilis-Pleuraphis mutica 101]
cheatgrass Bromus tectorum 103,147]
California montane chaparral Ceanothus and/or Arctostaphylos spp. 50-100 [101]
sugarberry-America elm-green ash Celtis laevigata-Ulmus americana-Fraxinus pennsylvanica 143]
curlleaf mountain-mahogany* Cercocarpus ledifolius 13-1,000 [5,114]
mountain-mahogany-Gambel oak scrub Cercocarpus ledifolius-Quercus gambelii 101]
California steppe Festuca-Danthonia spp. 101,126]
juniper-oak savanna Juniperus ashei-Quercus virginiana < 35
Ashe juniper Juniperus ashei < 35
western juniper Juniperus occidentalis 20-70
Rocky Mountain juniper Juniperus scopulorum < 35
cedar glades Juniperus virginiana 3-7
Ceniza shrub Larrea tridentata-Leucophyllum frutescens-Prosopis glandulosa 101]
wheatgrass plains grasslands Pascopyrum smithii 101,105,152]
pinyon-juniper Pinus-Juniperus spp. 101]
Colorado pinyon Pinus edulis 10-400+ [44,52,73,101]
Jeffrey pine Pinus jeffreyi 5-30
Pacific ponderosa pine* Pinus ponderosa var. ponderosa 1-47 [3]
interior ponderosa pine* Pinus ponderosa var. scopulorum 2-30 [3,7,83]
Arizona pine Pinus ponderosa var. arizonica 2-15 [7,29,115]
galleta-threeawn shrubsteppe Pleuraphis jamesii-Aristida purpurea < 35 to < 100
eastern cottonwood Populus deltoides 101]
aspen-birch Populus tremuloides-Betula papyrifera 35-200 [39,143]
quaking aspen (west of the Great Plains) Populus tremuloides 7-120 [3,56,92]
mesquite Prosopis glandulosa 91,101]
mountain grasslands Pseudoroegneria spicata 3-40 (10**) [2,3]
California oakwoods Quercus spp. 3]
oak-hickory Quercus-Carya spp. 143]
oak-juniper woodland (Southwest) Quercus-Juniperus spp. 101]
northeastern oak-pine Quercus-Pinus spp. 10 to < 35 [143]
coast live oak Quercus agrifolia 2-75 [55]
white oak-black oak-northern red oak Quercus alba-Q. velutina-Q. rubra 143]
canyon live oak Quercus chrysolepis <35 to 200
blue oak-foothills pine Quercus douglasii-P. sabiniana <35
Oregon white oak Quercus garryana 3]
California black oak Quercus kelloggii 5-30 [101]
bur oak Quercus macrocarpa 143]
oak savanna Quercus macrocarpa/Andropogon gerardii-Schizachyrium scoparium 2-14 [101,143]
black oak Quercus velutina 143]
little bluestem-grama prairie Schizachyrium scoparium-Bouteloua spp. 101]
elm-ash-cottonwood Ulmus-Fraxinus-Populus spp. 39,143]


*fire return interval varies widely; trends in variation are noted in the species summary

**mean
licença
cc-publicdomain
citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Fire Management Considerations ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: cover, fire management, forbs, forest, grassland, nonnative species, phenology, prescribed burn, prescribed fire, presence, restoration, seed, severity, species richness, wildfire

Fire as a control agent:
Prescribed fire alone is not likely to control field bindweed,
but it may be useful in combination with other methods (Callihan and others
1990, as cited by [86]). The effectiveness of prescribed fire as a control
method for field bindweed may vary with the invaded plant community and interactions with
other types of disturbance.

In C4-dominated grasslands, for example, long-term annually burned
watersheds had lower cover of nonnative species (including field bindweed) than unburned watersheds,
and fire reduced nonnative species richness by 80% to 90% [119]. Langstroth [82] recorded the
presence of field bindweed on experimental plots in a California grassland that were grazed by
domestic sheep (short duration) in the summer, but unburned. All other plots
(ungrazed/unburned, spring grazed/unburned, and all burning treatments) had no
field bindweed present.


It is unclear from these results how fire and grazing affect field bindweed
populations over the long term.


Postfire colonization potential:
Field bindweed has the potential to invade an area following fire. Fire provides a suitable seedbed
for field bindweed [42] by removing shade and exposing mineral soil.
Therefore, if field bindweed is present on or near the site prior to burning, there is
potential for its establishment and spread. It is a good idea to survey the
surrounding area for field bindweed and control plants that may contain seed that could be dispersed
into the burn.


Preventing postfire establishment and spread: The USDA Forest
Service's "Guide to Noxious Weed Prevention Practices" [137] provides
several fire management considerations for weed prevention in general that apply
to field bindweed.


Preventing invasive plants from establishing in weed-free burned areas is the
most effective and least costly management method. This can be accomplished
through careful monitoring, early detection and eradication, and limiting
invasive plant seed dispersal into burned areas by [51,137]:






  • re-establishing vegetation on bare ground as soon as possible




  • using only certified weed-free seed mixes when revegetation is necessary




  • cleaning equipment and vehicles prior to entering burned areas




  • regulating or preventing human and livestock entry into burned areas until
    desirable site vegetation has recovered sufficiently to resist invasion by
    undesirable vegetation




  • detecting weeds early and eradicating before vegetative spread and/or seed
    dispersal




  • eradicating small patches and containing or controlling large infestations
    within or adjacent to the burned area



In general, early detection is critical for preventing establishment of large
populations of invasive plants. Monitoring in spring, summer, and fall is
imperative. Managers should eradicate established field bindweed plants and
small patches adjacent to burned areas to prevent or limit seed dispersal into
the site [51,137].


The need for revegetation after fire can be based on the degree of desirable
vegetation displaced by invasive plants prior to burning and on postfire
survival of desirable vegetation. Revegetation necessity can also be related to
invasive plant survival as viable seeds, root crowns, or rhizomes capable of
reproduction. In general, postfire revegetation should be considered when
desirable vegetation cover is less than about 30% [51].


When prefire cover of field bindweed is absent to low, and prefire cover
of desirable vegetation is high, revegetation is probably not necessary after
low- and medium-severity burns. After a high-severity burn on a site in this
condition, revegetation may be necessary (depending on postfire survival of
desirable species), and intensive monitoring for invasive plant establishment is
necessary to detect and eradicate newly established invasives before they spread
[51].


When prefire cover of field bindweed is moderate (20-79%) to high
(80-100%), revegetation may be necessary after fire of any severity if cover of
desired vegetation is less than about 30%. Intensive weed management is also
recommended, especially after fires of moderate to high severity [51].


Fall dormant broadcast seeding into ash will cover and retain seeds. If there
is insufficient ash, seedbed preparation may be necessary. A seed mix should
contain quick-establishing grasses and forbs (exclude forbs if broadleaf
herbicides are anticipated) that can effectively occupy available niches.
Managers can enhance the success of revegetation (natural or artificial) by
excluding livestock until vegetation is well established (at least 2 growing
seasons) [51]. See Integrated Noxious Weed Management after Wildfires
for more information.



When planning a prescribed burn, managers should preinventory the project
area and evaluate cover and phenology of any field bindweed and other
invasive plants present on or adjacent to the site, and avoid ignition and
burning in areas at high risk for field bindweed establishment or spread due
to fire effects. Managers should also avoid creating soil conditions that
promote weed germination and establishment. Weed status and risks must be
discussed in burn rehabilitation plans. Also, wildfire managers might consider
including weed prevention education and providing weed identification aids
during fire training; avoiding known weed infestations when locating fire lines;
monitoring camps, staging areas, helibases, etc., to be sure they are kept weed
free; taking care that equipment is weed free; incorporating weed prevention
into fire rehabilitation plans; and acquiring restoration funding. Additional
guidelines and specific recommendations and requirements are available [137].
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Growth Form (according to Raunkiær Life-form classification) ( Inglês )

fornecido por Fire Effects Information System Plants
More info on this topic.

More info for the terms: geophyte, hemicryptophyte

RAUNKIAER [107] LIFE FORM:


Hemicryptophyte
Geophyte
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Habitat characteristics ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: frequency, grassland, natural, nonnative species

Field bindweed is primarily an agricultural weed, and occurs in cultivated
fields and other disturbed sites such as pastures, gardens, lawns, and along
roadsides and railways. Natural area managers are most likely to find it in
moist locations (e.g. riparian corridors and irrigated areas) on tracts once
used for agriculture [86].

Field bindweed was among several nonnative
plant species identified in a tallgrass prairie study in Kansas, where
nonnative species were most common at the town site and along human and
livestock travel corridors. A gradient was observed with a high abundance of
nonnative species in town to low abundance in prairie sites, with the
distribution of native plants forming a reverse gradient. Sources of nonnative plant introduction were related
to early cattle trails through the community, railroad and stockyard locations,
gardens, cultivated fields, livestock and wildlife activity. Nonnative plants
occurred on truck trails
into the upland prairie but had not yet invaded the surrounding grassland [40]. On study sites on open annual grassland and
blue oak savannah in California, field bindweed was found on both serpentine
and nonserpentine soil types.
It was most frequent near roads on nonserpentine soils and its frequency of occurrence decreased with
increasing distance from the road. This pattern was not observed on serpentine
soils [68].



Field bindweed is found in dry or moderately moist soils and can survive long periods of
drought due to its extensive root system. It grows best on rich, fertile soils but persists on poor, gravelly soils as
well [66]. In Quebec, field bindweed is found primarily on sandy
soils in warm, dry areas (Rousseau 1968 as cited by [144]). In northern California and the Great
Plains, field bindweed persists into autumn under severely dry conditions when most other
plants are unable to sustain growth. Strong sunlight and moderate-to-low moisture
appear to be optimal conditions for field bindweed growth and reproduction [22,78].

Field bindweed appears to be somewhat cold tolerant. Plants extracted from frozen ground in
Michigan had roots that appeared to be severely injured or dead in the uppermost
layers of soil. However, a laboratory test indicated that about 30% of field
bindweed roots survived 21 °F (-6 °C)
for 8 hours, but were unable to survive
18 °F (-8 °C)
for any time period tested [36].

Elevation range: Field bindweed has reportedly been found in
the Himalayas at altitudes of 10,000 feet (3,000 m) ([95] and references therein).
Field bindweed is found in several plant communities in riparian corridors in Wyoming, at
7,000 to 7,500 feet (2,100-2,300 m). Elevation ranges are given by area as follows:



Area Elevation range Reference
CA generally < 5,000 feet (1,500 m) [60,99]
CO 4,000 to 8,000 feet (1,200-2,400 m) [58]
NV 2,200 to 6,500 feet (700-2,000 m) [71]
NM 4,000 to 8,000 feet (1,200-2,400 m) [88]
UT 3,100 to 9,200 feet (930-2,800 m) [146]
Intermountain usually below 6,600 feet (2,000 m) [30]
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Habitat: Cover Types ( Inglês )

fornecido por Fire Effects Information System Plants
More info on this topic.

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

More info for the term: cover

SAF COVER TYPES [43]:





16 Aspen

19 Gray birch-red maple

40 Post oak-blackjack oak

42 Bur oak

50 Black locust

68 Mesquite

109 Hawthorn

110 Black oak

209 Bristlecone pine

216 Blue spruce

217 Aspen

218 Lodgepole pine

219 Limber pine

220 Rocky Mountain juniper

233 Oregon white oak

235 Cottonwood-willow

236 Bur oak

237 Interior ponderosa pine

238 Western juniper

239 Pinyon-juniper

240 Arizona cypress

241 Western live oak

242 Mesquite

246 California black oak

247 Jeffrey pine

249 Canyon live oak

250 Blue oak-foothills pine

255 California coast live oak
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Habitat: Ecosystem ( Inglês )

fornecido por Fire Effects Information System Plants
More info on this topic.

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

More info for the term: shrub

ECOSYSTEMS [48]:





FRES10 White-red-jack pine

FRES11 Spruce-fir

FRES12 Longleaf-slash pine

FRES13 Loblolly-shortleaf pine

FRES14 Oak-pine

FRES15 Oak-hickory

FRES16 Oak-gum-cypress

FRES17 Elm-ash-cottonwood

FRES18 Maple-beech-birch

FRES19 Aspen-birch

FRES20 Douglas-fir

FRES21 Ponderosa pine

FRES22 Western white pine

FRES25 Larch

FRES26 Lodgepole pine

FRES28 Western hardwoods

FRES29 Sagebrush

FRES30 Desert shrub

FRES31 Shinnery

FRES32 Texas savanna

FRES33 Southwestern shrubsteppe

FRES34 Chaparral-mountain shrub

FRES35 Pinyon-juniper

FRES36 Mountain grasslands

FRES37 Mountain meadows

FRES38 Plains grasslands

FRES39 Prairie

FRES40 Desert grasslands

FRES41 Wet grasslands

FRES42 Annual grasslands

FRES44 Alpine
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Habitat: Plant Associations ( Inglês )

fornecido por Fire Effects Information System Plants
More info on this topic.

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

More info for the terms: forest, shrub, woodland

KUCHLER [80] PLANT ASSOCIATIONS:




K015 Western spruce-fir forest

K016 Eastern ponderosa forest

K017 Black Hills pine forest

K018 Pine-Douglas-fir forest

K019 Arizona pine forest

K022 Great Basin pine forest

K023 Juniper-pinyon woodland

K024 Juniper steppe woodland

K026 Oregon oakwoods

K027 Mesquite bosques

K028 Mosaic of K002 and K026

K030 California oakwoods

K031 Oak-juniper woodland

K032 Transition between K031 and K037

K033 Chaparral

K034 Montane chaparral

K035 Coastal sagebrush

K036 Mosaic of K030 and K035

K037 Mountain-mahogany-oak scrub

K038 Great Basin sagebrush

K045 Ceniza shrub

K047 Fescue-oatgrass

K048 California steppe

K050 Fescue-wheatgrass

K051 Wheatgrass-bluegrass

K053 Grama-galleta steppe

K054 Grama-tobosa prairie

K055 Sagebrush steppe

K056 Wheatgrass-needlegrass shrubsteppe

K057 Galleta-threeawn shrubsteppe

K060 Mesquite savanna

K063 Foothills prairie

K064 Grama-needlegrass-wheatgrass

K065 Grama-buffalo grass

K066 Wheatgrass-needlegrass

K067 Wheatgrass-bluestem-needlegrass

K068 Wheatgrass-grama-buffalo grass

K069 Bluestem-grama prairie

K070 Sandsage-bluestem prairie

K074 Bluestem prairie

K075 Nebraska Sandhills prairie

K081 Oak savanna

K082 Mosaic of K074 and K100

K083 Cedar glades

K084 Cross Timbers

K085 Mesquite-buffalo grass

K086 Juniper-oak savanna

K087 Mesquite-oak savanna

K088 Fayette prairie

K098 Northern floodplain forest
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Habitat: Rangeland Cover Types ( Inglês )

fornecido por Fire Effects Information System Plants
More info on this topic.

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

More info for the terms: association, cover, forb, grassland, shrub, shrubland, vine, woodland

SRM (RANGELAND) COVER TYPES [118]:




101 Bluebunch wheatgrass

102 Idaho fescue

103 Green fescue

104 Antelope bitterbrush-bluebunch wheatgrass

105 Antelope bitterbrush-Idaho fescue

106 Bluegrass scabland

107 Western juniper/big sagebrush/bluebunch wheatgrass

109 Ponderosa pine shrubland

110 Ponderosa pine-grassland

201 Blue oak woodland

202 Coast live oak woodland

203 Riparian woodland

204 North coastal shrub

205 Coastal sage shrub

206 Chamise chaparral

207 Scrub oak mixed chaparral

208 Ceanothus mixed chaparral

209 Montane shrubland

210 Bitterbrush

214 Coastal prairie

215 Valley grassland

301 Bluebunch wheatgrass-blue grama

302 Bluebunch wheatgrass-Sandberg bluegrass

303 Bluebunch wheatgrass-western wheatgrass

304 Idaho fescue-bluebunch wheatgrass

305 Idaho fescue-Richardson needlegrass

306 Idaho fescue-slender wheatgrass

307 Idaho fescue-threadleaf sedge

309 Idaho fescue-western wheatgrass

310 Needle-and-thread-blue grama

311 Rough fescue-bluebunch wheatgrass

312 Rough fescue-Idaho fescue

314 Big sagebrush-bluebunch wheatgrass

315 Big sagebrush-Idaho fescue

316 Big sagebrush-rough fescue

317 Bitterbrush-bluebunch wheatgrass

318 Bitterbrush-Idaho fescue

319 Bitterbrush-rough fescue

320 Black sagebrush-bluebunch wheatgrass

321 Black sagebrush-Idaho fescue

322 Curlleaf mountain-mahogany-bluebunch wheatgrass

323 Shrubby cinquefoil-rough fescue

324 Threetip sagebrush-Idaho fescue

401 Basin big sagebrush

402 Mountain big sagebrush

403 Wyoming big sagebrush

404 Threetip sagebrush

405 Black sagebrush

406 Low sagebrush

407 Stiff sagebrush

408 Other sagebrush types

409 Tall forb

411 Aspen woodland

412 Juniper-pinyon woodland

413 Gambel oak

415 Curlleaf mountain-mahogany

416 True mountain-mahogany

417 Littleleaf mountain-mahogany

418 Bigtooth maple

419 Bittercherry

420 Snowbrush

421 Chokecherry-serviceberry-rose

422 Riparian

502 Grama-galleta

503 Arizona chaparral

504 Juniper-pinyon pine woodland

509 Transition between oak-juniper woodland and mahogany-oak association

601 Bluestem prairie

602 Bluestem-prairie sandreed

603 Prairie sandreed-needlegrass

604 Bluestem-grama prairie

605 Sandsage prairie

606 Wheatgrass-bluestem-needlegrass

607 Wheatgrass-needlegrass

608 Wheatgrass-grama-needlegrass

609 Wheatgrass-grama

610 Wheatgrass

611 Blue grama-buffalo grass

612 Sagebrush-grass

613 Fescue grassland

614 Crested wheatgrass

615 Wheatgrass-saltgrass-grama

701 Alkali sacaton-tobosagrass

702 Black grama-alkali sacaton

703 Black grama-sideoats grama

704 Blue grama-western wheatgrass

705 Blue grama-galleta

706 Blue grama-sideoats grama

707 Blue grama-sideoats grama-black grama

708 Bluestem-dropseed

709 Bluestem-grama

710 Bluestem prairie

712 Galleta-alkali sacaton

713 Grama-muhly-threeawn

714 Grama-bluestem

715 Grama-buffalo grass

716 Grama-feathergrass

717 Little bluestem-Indiangrass-Texas wintergrass

718 Mesquite-grama

720 Sand bluestem-little bluestem (dunes)

721 Sand bluestem-little bluestem (plains)

722 Sand sagebrush-mixed prairie

724 Sideoats grama-New Mexico feathergrass-winterfat

725 Vine mesquite-alkali sacaton

727 Mesquite-buffalo grass

729 Mesquite

730 Sand shinnery oak

731 Cross timbers-Oklahoma

732 Cross timbers-Texas (little bluestem-post oak)

733 Juniper-oak

735 Sideoats grama-sumac-juniper

801 Savanna

802 Missouri prairie

803 Missouri glades

804 Tall fescue

805 Riparian
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citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Immediate Effect of Fire ( Inglês )

fornecido por Fire Effects Information System Plants
There is no information available regarding the immediate effects of fire on
field bindweed.
It is likely that fire removes aboveground growth, while leaving the root system
and buried seeds undamaged. More research is needed to determine the effects of
fires of different severities under varied site conditions on field bindweed roots and seeds.
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citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Impacts and Control ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: competition, cover, fire management, fire suppression, forbs, forest, grassland, invasive species, natural, nonnative species, restoration, rhizome, seed, tree, vines

Impacts:
A 1998 review by Lyons [86] indicates that the impact of field bindweed on agricultural lands is well documented,
especially in the central U.S., but the threat it poses to rangelands and
natural areas is unclear. Almost all research on field bindweed pertains to agriculture.
When surveyed in 1982 and 1988, farmers and ranchers in north-central Idaho
considered field bindweed to be one of the 3 most serious weeds in their area [27]. The Eastern
Region of the U.S. Forest Service ranks field bindweed as a Category 3 plant:
often restricted to disturbed ground, and not especially invasive in undisturbed
natural habitats [136]. Natural area managers are most likely to find it in
moist locations (e.g. riparian corridors and irrigated areas) on tracts once
used for agriculture [86].

Field bindweed is found on several of The Nature Conservancy's preserves and may pose a
threat to restoration efforts. Stewards at the Phantom Canyon Preserve in
Colorado report that field bindweed is most likely to invade and reduce cover of native
grasses and forbs in areas that are degraded due to past land use, current human
activity, and fire suppression.
Stewards at Garden Creek Preserve in northern Idaho report that field bindweed threatens
native plant communities by "decreasing biodiversity," and is a direct
threat to several species [86]. At the Thousand Springs Preserve in Idaho,
field bindweed thrives under
cultivated and irrigated conditions, and managers there suggest that field
bindweed "outcompetes" native grasses
[86,109].

Field bindweed competition for nutrients and water may reduce productivity of native plants,
although this has only been studied with crop plants, where yield reductions
range from 0 to 100% [128]. Competition from field bindweed for soil moisture may have
greater impact in dry years [8].

It has been suggested that field bindweed may be mildly toxic to some grazing animals, and
that the amount of field bindweed that can be safely eaten by domestic sheep,
cattle, and goats is not known. It is reported to cause distress in domestic
pigs that eat it (Callihan and others 1990, as cited by [86]).
Field bindweed contains alkaloids that may be toxic to horses [134]. Other
authors report a history of using sheep and pigs to eat field bindweed and thereby help control infestations
[13,122] (see Biological control).

Control:
Field bindweed has a deep,
extensive root system that stores carbohydrates and proteins and allows it to sprout repeatedly following
removal of aboveground growth.
Field bindweed may also
produce abundant, long-lived seed. Strategies to control field bindweed infestations must
include removing established plants and preventing seed production and seedling
establishment. Alcock and others (1974, as cited by [86]) suggest the following as general goals
for field bindweed control:
1) reduce seed in soil 2) prevent seedling growth, 3) deplete food reserves in
the root system 4) prevent its spread.

Eradication of an established invader is rare, and control efforts vary
enormously in their efficacy. Successful control depends more on
commitment and continuing diligence than on the efficacy of specific tools
themselves. Control of biotic invasions is most effective when it employs a
long-term, ecosystem-wide strategy rather than a tactical approach focused on
battling individual invaders [87]. A long-term perspective is important where total eradication is not a
realistic short-term goal. Even with intensive management, field bindweed can
persist as seed for several years, and some authors suggest that 3 to 5 growing
seasons are required in agricultural settings to eliminate seedlings (Callihan
and others 1990, as cited by [86]). The key to implementing a successful control program is to continue
treatment even after it appears the infestations are seriously reduced
[86].

Successful control of field bindweed is most likely if aboveground
biomass is removed multiple times over at least 2 growing seasons (e.g. [13]), or
by planting of competitive species following aboveground removal and continuously monitoring for
and killing sprouts and seedlings. In agriculture, control has been most
successful where tillage is combined with herbicide application, although
herbicide application alone may also be effective
(see Chemical control) [86].

Prevention:
The most efficient and effective method
of managing invasive species is to prevent their invasion and spread [116].
Preventing the establishment of weeds in natural areas is achieved by
maintaining healthy natural communities and by conducting aggressive monitoring
several times each year. Monitoring efforts are best concentrated on the most
disturbed areas in a site, particularly along roadsides, parking lots,
fencelines, and waterways. When a field bindweed infestation is found, the
location can be recorded and the surrounding area surveyed to determine the size
and extent of the infestation, so these sites can be revisited on follow-up
surveys [67]. It is important to kill any field bindweed plants that are found,
followed by some combination of mechanical, chemical and/or biological control.
Prevention of new invasions is much less costly than postinvasion control
[87].

Avoid management activities that encourage invasion and be prepared to
eradicate small infestations that may follow such disturbances. Factors
indicated by Nature Conservancy managers as encouraging field bindweed invasion
include cultivation and irrigation in Idaho grassland and road grading and
haying in Oregon along roadsides and riparian areas [109]. Weed prevention and
control can be incorporated into all types of management plans, including
logging and site preparation, management of grazing allotments, recreation
management, research projects, road building and maintenance, and fire
management [137]. See the USDA "Guide to noxious weed prevention practices"
[137] for specific guidelines and recommendations for preventing the spread of weed
seeds and propagules under different management conditions.

Roads act as dispersal corridors for many invasive species. Avoid road building in nature reserves,
and when unavoidable, redeposit original
topsoil in roadside ditches. Road construction
projects should not be considered complete until native vegetation is fully
established. Road construction projects in nature reserves should be treated and
funded as 10- to 20-year biological projects rather than 1-2 year engineering
projects, with biologists and resource managers consulting on road construction.
Roadsides should be actively managed by regular monitoring for establishment of nonnative species,
and reseeding roadsides with natives [135].

Integrated management:
A combination of complementary control methods may
be helpful for effective control of field bindweed. Integrated management includes not only
killing the target plant, but establishing desirable species and discouraging
nonnative, invasive species over the long term. Components of any integrated
weed management program are sustained effort, constant monitoring and
evaluation, and the adoption of improved strategies. An integrated management
plan includes efforts to place continual stress on undesirable
plants.

In agriculture, most effective programs for the control of field bindweed
combine cultivation and crop rotation with the use of herbicides. A review by
Weaver and Riley [144] summarizes this information as follows: Cultivation at
frequent intervals results in a gradual and continuous reduction in the
concentration of total available carbohydrates and a decrease in root quantity.
However, 1 to 5 years of repeated tillage may be required to exhaust the root
reserves and effectively control populations of field bindweed. Competitive
crops such as winter wheat or perennial forages are able to reduce field
bindweed infestation after 3 to 5 years, particularly when combined with the
application of herbicides.

In North Dakota, 2 fields were prepared for planting to native grasses by
burning once and summer fallowing for 2 years. Summer fallowing effectively
killed all aboveground vegetation. Within 2 months after drill seeding native
grasses, perennial weeds, including field bindweed, were very dense. Fields were
then sprayed with 2 applications of 2,4-D. Results of these treatments are not
given [62].

Managers at
Thousand Springs Preserve in Idaho had success controlling field bindweed in an agricultural
site undergoing restoration, using a combination of tilling and planting
competitive plants. In the 1st year the field was burned and planted with peas
and oats. After the crop was harvested in the spring, the field was tilled and
irrigated to encourage germination of weeds. Glyphosate was applied in October,
although this had little effect because it was quickly followed by a killing
frost. Native perennial bunchgrass seeds were no-till drilled in late fall, and seedlings emerged in February and March. The native grasses were irrigated
and cheatgrass was suppressed using glyphosate. Annual weeds were controlled by
mowing around the bunchgrasses. Mowing and irrigation continued for 1
year. After 5 years the perennial grasses were well established, the annual
weeds continued to persist, and the perennial weeds (e.g. field bindweed) were minor
components. Field bindweed grows most successfully only where there are irrigation leaks and
generally does poorly if not irrigated. See the review by Lyons [86]
for more details.

In a greenhouse study on the combined effects of
the bindweed gall mite (Aceria malherbae) and herbicide (2,4-DB or glyphosate) on field bindweed height
and biomass, mite feeding alone reduced field bindweed shoot biomass 37% to 48% and root biomass 46%
to 50%. Herbicide alone reduced field bindweed root biomass 25% to 52%, and combining mite feeding
with either 2,4-DB or glyphosate reduced root biomass more than mites or either
herbicide alone. Combination of bindweed gall mite with sublethal doses of
herbicide may allow for field bindweed suppression while reducing potential herbicide injury
to desirable plants and maintaining mite populations. The herbicides did not appear to
negatively affect the mites [21].

Physical/mechanical:
Removing aboveground parts of
field bindweed repeatedly to starve the roots is commonly suggested as a control method in
agricultural settings (e.g. [11,13,17]). Common methods for removing top-growth
include tillage, hoeing, cutting, or mowing. Tillage is usually not recommended for natural areas,
as it may damage
desirable vegetation and/or increase soil erosion. On rangelands or natural areas
that were previously used for agriculture, tilling may be useful for ridding
infestations. For small areas this may be done using hand-held tools, but for
large areas machinery is often required [86].

The study and use of tillage or cultivation for control of field bindweed has a long history, particularly in
the midwestern United States, as reviewed by Bell [13]. The biological basis of
this research was that field bindweed could be killed if the roots were starved by cutting
off the leaves on a regular routine. Food reserves in the surface roots (upper
12 inches (30 cm)) are rapidly depleted by cultivation, but in deep roots (6 to 8 feet
(1.8-2.4 m) deep), reserves are exhausted only after long
continued cultivation at the emergence of new sprouts. Only a small quantity of
reserves is necessary to regenerate new growth [10].

Recommendations of intensive, repeated cultivation for control of field
bindweed are common. One recommendation was to cut off field bindweed plants about 3
inches (8 cm) below soil surface "for the whole season" (15-27 cultivations,
every 8-10 days, through the spring, summer, and early fall (until frost), and
another dozen cultivations the next year). Cultivations should extend 16.5 feet (5
m) from the population boundary because of invasive roots.
Another recommendation was to cultivate 8
days after the weed re-emerges, based upon careful studies of the rhizome system
that showed that the emerging shoots relied upon food stored in the root system
for 8 days before photosynthesis started to replenish the root. For a cultivation
tool, a duckfoot sweep was the desired implement [13].

Shallow hoeing and deeper
cultivations were equally effective when made every time the 1st shoots of
field bindweed emerged. Hoeing at regular 14-day
intervals was just as effective as hoeing every 7 or 10 days. All 3 techniques
eradicated field bindweed in 2 seasons (Sherwood and Fuelkeman 1948, and Timmons and Bruns
1951, as cited by [6]). The percentage of total sugars, carbohydrates, polysaccharides, starch,
and readily available carbohydrates in field bindweed roots cultivated at 3-week intervals
was markedly lower than that found in the roots of undisturbed plants.
Additional decreases were observed in the roots in the top 12 inches (30 cm) of
plants cultivated bi-weekly and weekly [12]. The relative depletion of food reserves, supplied by underground parts of the
plant, by cultivation every 7th day as compared with cultivation every 14th day,
was calculated. From this it appears that cultivation every 14 days would
destroy a 5th more of the readily available carbohydrates and more than double
the loss of protein nitrogen in the 2 parts as compared with 2 cultivations
at intervals of 7 days in the same unit of time [46]. Caution must be
used with cultivation, because much of the root system is concentrated near the surface of the soil
[34,133,144], and mechanical tillage may cut
and disseminate root fragments [78].

At the Bosque del Apache National Wildlife Refuge on the Rio Grande in
New Mexico, 3 techniques were employed in an effort to increase native chufa (Cyperus
esculentus) tuber production: 1) mowing early in the growing season; 2) shallow
disking 30 days after wetland drawdown; and 3) periodic sustained flooding
during the growing season. There was no control in this study. Field bindweed mass (g/m2)
appeared unaffected by mowing, and appears to have decreased slightly but not
significantly (p<0.10) after disking or flooding treatments [131].

Even under cultivation, field bindweed seedlings may continue to emerge for
many seasons. After 6 weeks, a new seedling has a root system
large enough to regenerate stems if it is cut [13]. Studies by Swan [129] indicate that
field bindweed seedlings can be killed by
tillage or cutting at a depth of 4 inches (10 cm) if done within 3 weeks of emergence.

Mulches are effective for controlling field bindweed if no light reaches the
soil surface. Black plastic is recommended. Complete death of field bindweed plants under mulch
takes about 3 to 5 years [13]. Similarly, 6 to 9 weeks of solarization in
California field plots
reduced the number of field bindweed seedlings, and regrowth from established
field bindweed plants was
suppressed for 6 weeks after treatment [41].

Fire:
See Fire Management Considerations.

Biological:
Several natural enemies of field
bindweed have been identified in its home range and several tested for
host-specificity. Unfortunately, nearly all of the biocontrol agents tested so
far also eat native morning-glories in California, some of which are rare or not
abundant [13]. According to Rees and Rosenthal [108], 2 biological control
agents have been released in the U.S.:

Agent Locations released or established References
bindweed gall mite MT, TX, AB [90,108]
bindweed moth (Tyta luctuosa) released in AZ, IA, MO, OK, and TX; not recovered (i.e. not
established) [108]

Larvae and adults of the Argus tortoise beetle (Chelymorpha casidea) feed on
the leaves of members of the morning-glory family. The Argus tortoise beetle is native to the U.S. and
also occurs in Canada. In New York, it has been observed to defoliate infestations of
field bindweed and false bindweed (Calystegia sepium) completely, while
leaving the associated rye and corn crops untouched. It was being investigated as a
potential biological control agent in 1979 (Selleck 1979, as cited by [144]);
the outcome of these investigations is unknown.

Grazing: In Minnesota, domestic sheep grazing on field bindweed infested land
sown to several crops (wheat, rye, and Sudan grass) consistently eliminated
bindweed in 2 seasons, while grazing of perennial pasture mixtures consisting of
alfalfa and brome grass or reed canary grass did not eliminate bindweed in any
of 3 experiments. Grazing of pure bindweed reduced the stand somewhat, but was
much less effective than was the grazing of infested land on which crops were
being grown [122]. According to a review by Bell [13], cattle do not eat field
bindweed, sheep will eat it but do not prefer it, and pigs are the field
bindweed gourmands. Pigs will eat the whole plant, given a chance. Pigs are said
to nearly eradicate the root system of bindweed if the field is plowed before
they are let into the field. However, their snouts must be free of nose rings or
slits.

Chemical:
Herbicides commonly recommended for the control of field
bindweed include 2,4-D (alone and in combination), glyphosate, dicamba, picloram, quinclorac, and
paraquat. See the Weed control methods handbook
or the field bindweed Element Stewardship Abstract
for more information on specific chemicals, their efficacy, and recommendations for use in controlling field bindweed.

In general, herbicides should be applied when they will be most effectively
absorbed and translocated to field bindweed roots, but before plants produce seed and new
buds. The optimum time for the
application of foliar-applied herbicides is the bud to full-bloom stage which
coincides with the maximum translocation of assimilates downward and root
metabolic activity. However, the application of herbicides
in late summer, if the vines are actively growing, may also be effective [86,144].

Moisture availability may impact the effectiveness of chemicals applied for
field bindweed control. A laboratory test indicated that field bindweed is more resistant to glyphosate action
when plants are drought stressed [33]. Similarly, a
review by Meyer [93] indicates that field bindweed growing in semiarid conditions (rainfall
of 11 to 20 inches (280-500 mm)) may be more resistant to weed control efforts
(herbicides and cultural control) than field bindweed growing in more humid conditions
(rainfall >25 inches (640 mm)). This is especially apparent for foliar-applied
herbicides, possibly due to lower leaf area, thicker cuticle with higher wax
content, slower biological processes, and smaller leaf:root ratios under
semiarid conditions. But it may also be due, in part, to different cropping and
cultural practices employed in the different areas.

According to a review by Lyons [86], repeated use of the same or similar herbicides can result in
herbicide-resistant strains of field bindweed. Investigators have
unsuccessfully tried to correlate the morphology of field bindweed strains with their
herbicide resistance. When planning on
using herbicides to control field bindweed, it is useful to know whether field
bindweed strains in the
area have demonstrated any herbicide resistance [86]. Evidence of resistance of
field bindweed to 2,4-D isooctylester after 3 consecutive years
of spraying is suggested by Zengin [157]. Field bindweed 1st demonstrated resistance to 2,4-D in Kansas in 1964, and apparently,
research has shown that these particular biotypes may be resistant to other
synthetic auxin herbicides. See the International Survey of Herbicide
Resistant Weeds
for more information.

Cultural:
In agricultural systems, smother crops
are often used to control invasive species such as field bindweed. Competition for light
reduces field bindweed vigor [9,13]. According to a review by
Lyons [86], light reaching field bindweed plants must be reduced to about 50% shade or more for 3
years to control field bindweed growth.

In agricultural systems suggested smother crops include millet, sorghum,
Sudan grass, or alfalfa [66,86]. Winter wheat is often a good competitor with
field bindweed because it grows rapidly during the early spring when
bindweed is not using soil moisture (Wiese and Rea 1959, as cited by [144]). Summer-planted crops that grow
vigorously and provide early shade offer competition to field bindweed at a time when it is normally making its best
growth [66].

It may be difficult to find native species that can compete effectively with
field bindweed. The outcome of competition between species can be complicated and unpredictable.
Managers at Phantom Canyon Preserve were unable to establish
native species to compete with field bindweed, while those at Thousand Springs Preserve
successfully established perennial grasses [86].

A review by Lyons [86] suggests that, in general, species that grow vigorously during the winter and early spring
may offer the best competition to field bindweed, because they force field
bindweed plants to compete
for light later in the season. Competitive crops may be most effective in
humid/shady areas where solar radiation is diminished and shading has larger
consequences (Wilson and others 1955, as cited by [86]). Therefore competitive planting or
restoration efforts in low light riparian habitats, where the available light is
reduced by tree canopies, may work to control field bindweed [86].
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Importance to Livestock and Wildlife ( Inglês )

fornecido por Fire Effects Information System Plants
Very little information is available regarding the use of field bindweed by
livestock and wildlife. According to Bell [13], various research reports
published by the Experiment Stations of Kansas, Iowa, Utah and Texas from 1920
to 1952 suggest that farm animals, including sheep and pigs, were used to eat
bindweed as a control method in some places during that time, but that cattle
are "nearly useless" for this purpose (see Biological control). In Minnesota,
sheep grazed bindweed in preference to wheat, rye (Secale spp.), or Sudan grass
(Sorghum bicolor ssp. drummondii), and they grazed alfalfa
(Medicago sativa), brome grass (Bromus spp.),
or bindweed without discrimination but preferred these to reed canarygrass (Phalaris
arundinacea) [122].

Field bindweed comprised 1.7 percent of mule deer diets during the spring-summer-fall
grazing season on a central Colorado ponderosa pine-bunchgrass
range [31]. Field bindweed was found in the rumens of white-tailed deer in
summer and fall on Missouri River bottomlands in north-central Montana [1].

Palatability/nutritional value:
According to a review by Bell [13], field bindweed is highly palatable to pigs,
while sheep will eat it but do not prefer it, and cattle do not eat it.

The palatability of field bindweed for wildlife species in Montana and
Utah is rated as follows [38]:

  MT UT   
Pronghorn fair good
Elk --- good
Mule deer --- good
White-tailed deer poor good
Small mammals poor fair
Small nongame birds poor fair
Upland game birds poor fair
Waterfowl --- fair
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Key Plant Community Associations ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: association, bog, codominant, competition, cover, forb, forbs, frequency, grassland, herbaceous, natural, shrub

Field bindweed is invasive primarily in agricultural areas, although some
authors indicate that it is also invasive in natural areas (e.g. [28,86,109]). Natural area managers are most
likely to find it in moist locations (e.g. riparian corridors and irrigated
areas) on tracts once used for agriculture [86]. Field bindweed is normally found in
open communities in association with annual, biennial, and short-lived perennial
weeds [144]. Habitats that are most like agricultural
lands (little competition, repeated disturbance, and high light intensity) are ideal for
growth of field bindweed (Cox (1915) as cited by [86]).

California: Field bindweed establishes locally in vernal pools in
Sacramento County, and in large pools in Tehama County. These habitats support populations of endangered hairy Orcutt
grass (Orcuttia pilosa) and Hoover's spurge (Chamaesyce hooveri),
and also support thriving field bindweed and cocklebur (Xanthium strumarium var. canadense) populations. Field bindweed occurs in open
annual grassland and oak savannah sites. Dominant natives include blue oak (Quercus douglasii) and chamise (Adenostoma
fasciculatum). Grassland natives include purple needlegrass (Nassella pulchra),
Sandberg bluegrass (Poa secunda),
California melic grass (Melica californica), small fescue (Vulpia microstachys),
and many native forbs [68]. At Sugarloaf Ridge
State Park, field bindweed is occasional in disturbed
places such as campgrounds and horse corrals [19].

In Nevada, field bindweed occurs on disturbed, moist soil of cultivated fields, near springs, roadsides, and
homesteads with pinyon (Pinus spp.), juniper (Juniperus spp.), and
saltbush (Atriplex spp.) [71].


At the Thousand Springs Preserve, Idaho, field bindweed thrives under
cultivated and irrigated conditions, and managers there suggest that field
bindweed outcompetes native grasses [86,109]. At Garden Creek Preserve in northern Idaho, managers report that
field bindweed threatens bunchgrass and forb-dominated habitats [86].



Wyoming: Olson and Gerhart [100] describe a field
bindweed vegetation type in a Wyoming riparian area with an overstory dominated by quaking aspen (Populus
tremuloides), and blue spruce (Picea pungens), and shrub layer
dominated by russet buffaloberry (Shepherdia canadensis) and willow (Salix
spp.), with rose (Rosa spp.), shrubby cinquefoil (Dasiphora floribunda),
and bog birch (Betula glandulosa) also present. They describe 2 other habitat types
with herbaceous plant communities dominated by field bindweed, bluegrass (Poa spp.),
western wheatgrass (Pascopyrum smithii), and an unknown annual forb, with
coniferous overstories dominated by blue spruce, lodgepole pine (Pinus
contorta), and white fir (Abies concolor).

In Colorado, field bindweed has been identified in "seemingly remote, undisturbed
aspen stands" in Rocky Mountain National Park [28]. At the Phantom
Canyon Preserve, field bindweed is most problematic in
riparian corridors and mountain-mahogany (Cercocarpus spp.) shrubland/grassland [86].

Midwest: Field bindweed occurs with purple loosestrife (Lythrum salicaria) in wetland sites in the
Midwest [132]. It occurs in Theodore Roosevelt National Park in North Dakota [26], and occurs in the understory in
eastern cottonwood (Populus deltoides) stands along the Missouri River in southeastern South Dakota [150].
Field bindweed had relatively high (compared with other regulated noxious weeds)
frequency and canopy cover on study areas in the glaciated prairie pothole
region of the Northern Great Plains [61].

Canada: Field bindweed is a dominant species in some disturbed riverbank areas in the Montréal
area of Québec. Codominant species include
common wormwood (Artemisia vulgaris), common dandelion (Taraxacum officinale), and
bird vetch (Vicia cracca) [97].

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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Life Form ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: forb, vine

Vine-forb
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Other uses and values ( Inglês )

fornecido por Fire Effects Information System Plants

Dioscorides (circa A.D. 50) recommended drinking tea made from field bindweed
seeds for 40 days to cure spleen problems, weariness, and hiccups. However, he
warned, it had the inconvenient side effects of causing one to urinate blood
after the 6th day and making one permanently sterile after the 37th (as cited by
[95]). According to Kearney and others [72], an antihemorrhagic substance has been discovered in
field bindweed, although the source of this information is not given.


Extracts from field bindweed leaves and stems show high larvacidal activity against mosquito larvae [20].

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citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Phenology ( Inglês )

fornecido por Fire Effects Information System Plants
More info on this topic.

More info for the terms: adventitious, rhizome

Seeds of field bindweed germinate throughout the growing season when adequate moisture
is available, and a germination peak usually occurs in late spring or early summer.
In southern Ontario, seedlings usually emerge in early May and quickly develop a
taproot followed by lateral roots and numerous thin feeding roots.
Rapid growth of rhizomes and shoots begins when day temperatures are near 57 °F (14 °C) and night
temperatures at least 36 °F (2 °C) (Whitesides, 1979 as cited by [144]).

Flowering dates are given by area as follows:

Area Dates References
AZ May-July [72]
CA May-October [99]
FL spring-summer [153]
IL May-September [96]
NV May-September [71]
NM May-July [88]
ND June 17-July 6 [123]
TX May-July, less freely later [37]
WV June-August [127]
Blue Ridge (NC, SC, TN, VA) May-October [151]
Carolinas June-frost [106]
Great Plains June-August [54]
Intermountain June-August [30]
Northeast May-September [50]
Pacific Northwest mid-spring-late fall [65]
Baja CA April-August [149]

In southern Ontario, plants begin flowering in late June and continue as long
as conditions permit [144]. Flowers last for only one day,
opening in the morning and wilting by early afternoon [142].

Field bindweed roots and rhizomes develop
winter hardiness during autumn. The shoots are killed back to the roots by freezing temperatures, but hardened
roots will withstand temperatures
as low as 21 °F (-6
°C) [36]. Field bindweed overwinters by means of its root and rhizome system as well as by seeds on or
below the surface of the soil.

In the 2nd and subsequent years new growth arises from endogenous root
buds formed in the fall on the vertical roots and on any lateral roots that
survive
winter. The endogenous root buds, unlike adventitious buds, may remain dormant
or develop into shoots or roots.  While Davidson [34] found developing buds at all times of the year on
field bindweed
plants grown from root cuttings in Oxford, England, others suggest that
regenerative capacity of root buds varies throughout the year (e.g. [130,144]). Buds on the larger roots begin to enlarge
and develop rhizomes in early spring [144]. The
number of shoots formed from lateral root segments is greatest in early spring
and least in late summer [130]. Davison observed new shoots
emerging until late October, with those emerging after late August accounting
for half the annual radial increase in shoot emergence of 10 feet (3 m) [34].

Storage capacity of field bindweed roots and rhizomes also varies throughout
the year. The percentage of starch in
the roots reaches a maximum in August or September and thereafter rapidly
declines as it is converted to sugar. The percentage of sugars in the roots
reaches a maximum in late October and a minimum in May (Barr 1940, as cited by
[144]). The percentage of root carbohydrates is lowest at the prebloom stage of
growth (Gigax 1978, as cited by [144]).

Frazier [45] provides details on the amount, distribution, and seasonal trend
of carbohydrate and nitrogen fractions in the root system of field bindweed in Kansas. All of the carbohydrate
fractions, except the reducing sugar fraction,
reached low points in all of the root portions during the interval of 15 April to
15 May. Sugars attained a seasonal maximum the 1st of November in most parts
of the root system; starch-dextrin fraction attained maximum levels in all
root parts between mid-August and the 1st of October; the readily available
carbohydrate fraction followed the trend of the starch-dextrin fraction closely.
The general trend of the nitrogen fractions in practically all portions of the
plant showed an early season rise to 15 April (from 1 April), followed by a
decline to a low point sometime between 15 May and 15 June. See Frazier [45]
for further details.
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Plant Response to Fire ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: competition, litter

There is no information available regarding field bindweed response to fire.
Field bindweed probably sprouts from roots and rhizomes if top-killed by fire. Response of field bindweed populations to
fire depends on a number of factors, including
native and imposed FIRE REGIMES, site conditions (e.g. soil, moisture,
temperature), associated plant communities, management history, and disturbance
regimes at a particular site.

In a study on the effects of litter on
germination and establishment of cheatgrass and medusahead, field bindweed germinated and grew well without litter,
suggesting that field bindweed may do well in a
postfire environment. When litter was present, and with increased competition from grasses, yields of
field bindweed were
"drastically curtailed" [42].

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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Post-fire Regeneration ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: geophyte, ground residual colonizer, herb, initial off-site colonizer, rhizome, secondary colonizer, seed

POSTFIRE REGENERATION STRATEGY [124]:




Rhizomatous herb, rhizome in soil

Geophyte, growing points deep in soil

Ground residual colonizer (on-site, initial community)

Initial off-site colonizer (off-site, initial community)

Secondary colonizer (on-site or off-site seed sources)
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Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Regeneration Processes ( Inglês )

fornecido por Fire Effects Information System Plants
More info for the terms: capsule, competition, litter, natural, scarification, seed

Field bindweed reproduces both sexually and vegetatively.

Breeding system:
Field bindweed is self-incompatible [98] and thus an
obligate out-crosser, which may play an important role in maintaining the high
degree of phenotypic variation observed in this species.

Pollination:
Field bindweed flowers persist only 1 day and are insect pollinated [144]. Observations in
Kansas determined that field bindweed flowers were fully open by 8 am during
late June and early July. Nectar, produced at the base of the tube of fused
petals, attracted various pollinators including Halictid bees, honeybees, bumblebees,
butterflies, and moths. Halictid foraging was highest from 8:30 to 11:30 am. The
flowers wilted by early afternoon [142].

Seed production:
Seed production by field bindweed is variable and dependent upon environmental conditions. There is little
information on the amount and relative reproductive importance of seeds produced by
field bindweed. Literature reviews and observations over 3 years in Iowa [22] indicate that seed set
in field bindweed is favored in seasons of high temperature and low rainfall, especially on
calcareous soils. Periods of cloudy weather and fine-textured, poorly drained
soils restrict blossoming and seed production. Individual flowers may fail to
set seed or to mature seed that has been set, and capsules that appear normal
frequently contain no viable seed. Under favorable conditions the number of
seeds per capsule varies from 1 to 4 with an average of 2; however, 10
seeds per capsule have been reported from Russian material. Seed is often not produced by plants in frequently
cultivated soils. In one count, 157 capsules collected from plants in cultivated
fields yielded 41 seeds. Few estimates of seed production per plant are
available, as the spatial limit of an individual plant is often difficult to
determine due to the extensive root system. Estimates of 12 to 300 seeds per
plant are reported, and estimates of number of seeds produced per unit area in a
pure field bindweed stand range from 50,000 to 20 million seeds per hectare, though it is
unclear under what conditions these estimates were made [22,144].

According to a review by Weaver and Riley [144], field bindweed seldom sets
seed during the 1st year of growth, although plants grown in the greenhouse will
flower within 6 weeks of emergence based on unpublished data of the author.
According to Brown and Porter [22], germinability of field bindweed seeds began
10 to 15 days after pollination, when moisture content was 81%. Sripleng and Smith [120] provide a
detailed description of the anatomy and development of field bindweed seed,
and their observations suggest that field bindweed seeds mature about 25 days after
fertilization.

Seed dispersal:
Field bindweed seeds generally fall near the parent plant but can be dispersed by water [22], as contaminants in crop seed [66],
by animals after ingestion [57,104,111], by animals' feet, and by vehicles or machinery. Long-distance dispersal by birds is
possible because seeds of field bindweed can remain viable in the digestive tracts of some birds for up to 144 hours [104].

Harmon and Keim [57] tested the viability of weed seeds recovered in the
feces of several domestic animals. Field bindweed had the highest percentage
recovery and germination of all weed seeds tested, resulting in an average of
11.7% viable seeds recovered from all animals. Percent germination of field
bindweed seeds before feeding and without acid scarification, after a 2-week
germination period, was 9.3%; and with acid scarification, after a 4-week
germination period was 84%. Some data are as follows:

Animal % of 1000 field bindweed seeds recovered % germination (2 weeks, no acid treatment) % germination (4 weeks, with acid treatment)
calves 38.7 4.5 57.5
horses 10.4 11.0 60.0
domestic sheep 15.4 8.0 59.0
domestic pigs 51.2 18.0 41.0
chickens 0 -- --
average 23.1 10.4 54.4

Seed banking:
Field bindweed produces impermeable seed, giving it a physical exogenous dormancy which may or may not
be combined with other dormancy mechanisms [22,111]. A review by Rolston [111] indicates that seed longevity is often,
but not always, associated with impermeable seed, so that impermeable seeds are
distributed in time as well as space. Rolston describes in detail
the anatomy of the seed coat of field bindweed seed and other seeds with impermeable seed
coats. Seed impermeability varies with time and place of collection [22] as a result of differences in relative
humidity, temperature, light, soil fertility, and genetic factors [111].

Many impermeable seeds survive ingestion, allowing dispersal by animals and
birds (see Seed dispersal above). Under natural conditions increments of a seed
population become permeable to water and germinate in successive intervals [111]. Permeability in field
bindweed seeds is increased by various laboratory treatments,
including storage at both high 104 °F (40
°C) and low 33
°F (0.5 °C) temperatures, soaking in
concentrated H2SO4 for 45 to 60 minutes, immersion in hot
water at temperatures ranging from 126 to 212 °F
(52-100 °C), soaking in ethyl alcohol, and
mechanical scarification [22,111]. Rolston [111] speculates that in the
field, field bindweed's seed coat may be broken down or punctured by mechanical abrasion,
especially during cultivation, by passage through the digestive tract of
mammals and birds, by high temperatures or temperature fluctuations, by fire,
and possibly by microbial degradation. However, results presented
by Leishman and others [85] suggest that fungi do not play a
major role in field bindweed seed degradation. Other data indicate that as much as 48% of
impermeable field bindweed seeds may become permeable in 1 winter if the seeds are
not more than 3 inches (8 cm) deep in the soil. Impermeable seeds of field bindweed retained a
considerable degree of viability and impermeability for 4 years after burial at 6 and 18 inches
(15-46 cm) [22].

It is generally accepted that field bindweed seeds remain viable in the soil seed bank
for many years, with estimates ranging from 20 to 50 years [14,78,86,144]. Timmons [133] wrote in
1949 "the ability of seed of field bindweed,
to remain dormant in cultivated soil for a considerable time and eventually
germinate is quite generally known." Brown and Porter [22] found that as much as 62% of 50-year-old
field bindweed seeds stored and tested in the laboratory were viable, with 8% germinable, 54%
impermeable, and 38% dead. Timmons [133] observed field bindweed seedlings emerging
in a field from which field bindweed plants had been eradicated 20 years earlier,
and suggested that the seed had survived in the seed bank for those 20 years.
However, it is not clear whether there may have been seed or root fragments
imported from off-site. Timmons also observed
seedling emergence and adult plant establishment under different cropping
systems, and he concluded that completely ridding infested
land of field bindweed may require 30 years or more of persistent attention to a rigid
program of field management until all dormant seeds have been germinated and
destroyed [133]. Research is needed to better understand field
bindweed seed longevity under various field conditions, especially in natural areas.

Field bindweed was among many plants that emerged from soil samples taken from a
blue grama-needle-and-thread grass-western wheatgrass (Bouteloua gracilis-Hesperostipa
comata-Pascopyrum smithii) mixed grass community
in eastern Montana and incubated to determine seed bank composition. It was not
reported whether adult field bindweed plants were present on the site [63].

Germination:
Differences in percent germination, impermeability, and viability have been noted for seed lots
of field bindweed collected in different years and from different sites. The mean percentage of germinable
seeds produced by field bindweed plants varies from 5% to 25%, of impermeable seeds from 60% to 80%,
and of viable seeds from 87% to 99% [22,144]. Germination of impermeable seeds can be
promoted by chemical or mechanical scarification. Seeds of field bindweed that have been scarified will
germinate over a wide range of temperatures (41 to 104
°F (5-40 °C)) with maximum and most rapid
germination at alternating temperatures of 95/68 °F
(35/20 °C) [22].
Exposure to light does not much improve germination of freshly
harvested seeds (Weaver, unpublished data cited in [144]). According
to Brown and Porter [22], exposure to both high (104
°F (40 °C)) and
low (33 °F (0.5
°C)) temperatures promotes germination in field bindweed.
Similarly, Jordan and Jordan [69] ran tests in which field
bindweed seeds were prechilled in the dark at 41°F (5
°C) for 21 to 42 days and then
moistened and germinated at 84 °F (29
°C) at 96% relative humidity, in darkness.
Percentage seed germination increased as the prechilling time increased. The
increase in germination was accompanied by morphological changes in the seed
coat, as observed with scanning electron microscopy [69].
Conversely, viability of field bindweed seed was not reduced, nor was permeability
increased, after 50 days in loosely stacked, composting chicken manure where
temperatures reached approximately 149 to 158 °F
(65-70 °C). Viability and permeability were
also unchanged after 4 months in moistened, compacted chicken manure, where
temperatures reached about 113 °F (45
°C) [125].

Over 5 years of dry storage in the laboratory at room temperature, the
percentage of germinable seeds did not vary greatly, although the average
percentage of dead seeds increased from 8% to 47% as the percentage of impermeable
seeds decreased from 87% to 38% during the 5 years. The percentage of total live
seed decreased from 87% to 49%. Germination rate averaged 31.8% in field
bindweed seeds that had overwintered in the
soil at 3 inches (8 cm) depth, an increase of 17.8% over average germination
rate (14%) in a laboratory test. Seeds buried 4 to 6 inches (10-15 cm) deep had
germination rates that ranged from 0.4% to 6.8%. Oxygen
concentrations below 10.5% and above 53% are unfavorable, and concentrations
between 21% and 53% are favorable for field bindweed seed germination. Impermeable seeds of
field bindweed were not affected by changes in the amount of oxygen [22]. Germination of field bindweed seeds
was low (mostly between 0.2% and 9%) before, during,
and after both dry storage and storage in water (up to 22 months) [23]. In a 2nd, similar study, the
percentage germination of field bindweed
seed appeared to increase with the length of time in water storage [24].

Field bindweed germinated and
established better on bare ground than on sites with litter on rangeland in
western Nevada [42].

Seedling establishment/growth:
The ability of field bindweed to establish from seed
may be underestimated. Seeds are
usually responsible for the introduction of field bindweed to a new area, and
lateral roots and rhizomes play the primary role in spreading an infestation
locally [144].

By 6 weeks after emergence a field bindweed taproot may reach a depth of 18 to 24 inches
(45-62 cm) and have 3 to 6
lateral roots, usually within 12 inches (30 cm) of the soil surface (Riley, unpublished
data as cited by [144]). Seeds of field bindweed, scarified
and planted in Iowa at 2-week intervals from
25 April to 26 September, germinated and produced seedlings at each planting. Emergence was greatest in the spring (60-75%) and late
summer (43-57%) and least in midsummer (1-10%). Roots of field bindweed seedlings emerging in the spring
and early summer penetrated to depths of 51 to 67 inches (1.3-1.7 m) by November, whereas
seedlings produced in August and September had a maximum root penetration of
10 to 20 inches (25-50 cm) [22].

In Saskatchewan, Best [16] found that 25 shoots
had emerged from a 2 inch (5 cm) root fragment 4 months after planting. The
nearest shoot was 18 inches (46 cm) from the parent plant and the furthest 52 inches
(132 cm). After 15 months a shoot was observed 114 inches (290 cm) from the
parent plant.

Frazier [47] describes, in detail, the growth of a field bindweed plant growing
in a deep silt loam soil in Kansas, under known climatic conditions, with little
or no competition (none from other plant species). The taproot rapidly
penetrated directly down from the germinating seed. Many branch roots arose
throughout the length of the taproot, a few of which grew extensively and became permanent lateral roots.
Permanent lateral roots tended to radiate away from the point of origin, thus
together occupying an area somewhat circular in shape. All shoot development was
derived from root-borne stem buds that developed on any part of the permanent
root system. Regardless of where these root-borne buds formed, if they developed
underground they gave rise to rhizomes. If the buds were borne at or above the soil
surface they gave rise to leafy shoots. By 120 weeks after emergence, practically all the vertical roots observed
penetrated the 34- to 39-inch (86-99 cm) layer. No soil layer was found in this
study that impeded vertical penetration of the roots [47]. Other descriptions of field
bindweed growth and development are available from England [34] and Nebraska [75].

Asexual regeneration:
Field bindweed reproduces vegetatively by means of endogenous root buds that develop
into rhizomes and establish new shoots upon reaching the soil surface. Root buds
at or above the soil surface develop into shoots [47,74]. Roots develop on rhizomes, allowing daughter plants to survive
if severed from the parent plant [74]. New field bindweed plants may also
develop from root fragments [16,17,75,117]

In cultivated fields and in old, well-established areas of bindweed, field
bindweed's creeping roots are often inconspicuous. Because of their slenderness and their
proximity to the surface, they are easily destroyed by cultivating tools and by
heavy freezing. New growth after cultivation is made from the vertical root
immediately below the point of injury [75]. Whenever the taproot has
become broken or cut, as in deep cultivation or plowing, the rhizomes
connect it to the growing shoots. Field bindweed rhizomes vary in
length from a few inches to several feet. Roots severed at various depths below
the soil surface often develop rhizomes several feet
in length. In many instances, old roots that have been cut off successively for
several years may produce a thousand or more slender rhizomes from the severed
end and give rise to a peculiar and striking bunchy form of leafy growth above
ground. In localities where there is a high water table, the taproot may branch
at a depth of 2 feet (0.6 m) or less, while in other localities, it may penetrate to a
depth of 10 feet (3 m) or more before branching profusely [74].
Seedlings grown in the greenhouse were regenerated from the root when
the aboveground portion was removed 19 days after emergence (Weaver, unpublished
data as cited by [144]).

Sherwood [117] conducted experiments to determine if new field
bindweed infestations could be initiated by root fragments. The larger the diameter
and/or length of the root section, the more likely it is to grow. Fragments less
than 3 inches in length were weak or failed to grow, and fragments obtained from
below the plow depth were more likely to grow than those taken from shallower
depths. Fragments from starved roots with low root reserves (i.e. roots
from plants whose top growth was prevented for a growing season) had poor
growth. Root fragments from previously disturbed plants are less
likely to grow than are those from undisturbed plants [117]. Results presented by Swan and Chancellor [130] suggest
that regeneration of field bindweed from root fragments varies by season, and is highest in
spring and lowest in late summer. Interpretation of results presented by Swan and Chancellor suggest that
regeneration is primarily from fragments of vertical roots and rhizomes (more so than
horizontal root fragments) [78].
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citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Regional Distribution in the Western United States ( Inglês )

fornecido por Fire Effects Information System Plants
More info on this topic.

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

BLM PHYSIOGRAPHIC REGIONS [15]:





1 Northern Pacific Border

2 Cascade Mountains

3 Southern Pacific Border

4 Sierra Mountains

5 Columbia Plateau

6 Upper Basin and Range

7 Lower Basin and Range

8 Northern Rocky Mountains

9 Middle Rocky Mountains

10 Wyoming Basin

11 Southern Rocky Mountains

12 Colorado Plateau

13 Rocky Mountain Piedmont

14 Great Plains

15 Black Hills Uplift

16 Upper Missouri Basin and Broken Lands
licença
cc-publicdomain
citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

States or Provinces ( Inglês )

fornecido por Fire Effects Information System Plants
(key to state/province abbreviations)


UNITED STATES


AL AZ AR CA CO CT DE FL GA HI
ID IL IN IA KS KY LA ME MD MA
MI MN MS MO MT NE NV NH NJ NM
NY NC ND OH OK OR PA RI SC SD
TN TX UT VT VA WA WV WI WY DC



CANADA

AB BC MB NB NS ON PE PQ SK



MEXICO

B.C.N.
licença
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citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Successional Status ( Inglês )

fornecido por Fire Effects Information System Plants
More info on this topic.

More info for the terms: competition, forest, hardwood, litter, rhizome, seed

Field bindweed tends to be an early successional species, as it establishes well on bare
ground under open conditions. Disturbed sites are common habitat for field
bindweed
throughout its range (e.g. [37,50,96,106,127,141,146,151,153]). On a site in
western Nevada, field bindweed germinated and established better on microsites with bare
ground than on microsites with litter, and occupied
early successional stages (mostly grazing disturbance) in
some rangeland plant communities [42].

It is unclear how long field bindweed plants may persist in native plant communities.
Field bindweed plants were still present in an abandoned farm field 30 years after it was
last farmed in tallgrass mixed hardwood forest in Minnesota [59].


A review by Holm and others [66] suggests
that competition for sunlight places field bindweed at a disadvantage, and that, if adequate soil moisture is present,
several crop plants will force
it into abnormal growth and dormancy by shading. When crop plants are removed,
field bindweed resumes active growth [66]. Similarly, on a site in western
Nevada, scattered plants of field bindweed were observed growing intermixed with, but suppressed by a
medusahead (Taeniatherum caput-medusae) population. When medusahead was reduced by a variety of methods
(herbicide, disk-harrow, furrow), medusahead reduction was
followed by heavy infestations of field bindweed [155].


Bakke (1939, as cited by [9]) reports that shaded
field bindweed plants lose their prostrate habit and become twining plants. In general, the
lower the light intensity reaching field bindweed plants, the more rapid the elimination of
above- and belowground parts and the more reduction of available root
carbohydrates [9]. Dall'Armellina and Zimdahl [32] found that flower production, leaf area, and dry matter of shoots,
roots, and rhizomes
of field bindweed grown from seed declined as light level decreased. The only response
to reduced light levels of plants grown from rhizome segments was complete inhibition of rhizome
production [32]. A study by Mashhadi
and others [89] characterized the photosynthetic rate of
field bindweed under varied
light levels, measured as photosynthetic photon flux
(PPF). Field bindweed showed a linear response to PPF levels. Photosynthesis and transpiration both decreased at the
same rate in response to
decreasing PPF. There was a small amount of transpiration in darkness. The
authors also noted that field bindweed
growing under a dense juniper canopy had mostly abscised or chlorotic lower
leaves and long internodes on stems far from sunlight. They speculated that
field bindweed plants were able to establish in this low light environment
either because the leaves had adapted to low light and/or root reserves were
used to support the initial growth stages.


The competitive ability of field bindweed is due largely to its extensive root system. One
plant is able to reduce the available soil moisture in the top 24 inches (60 cm) of soil
below the "wilting point" (Wiese, unpublished data in [144]). Bakke [8] characterized the competitive
interaction between corn and field bindweed in Iowa,
noting that field bindweed is a superior competitor for water under conditions of low soil
moisture, and that corn plants growing with field bindweed were smaller and had lower
yields. How the competitive ability of field bindweed might affect successional trajectories
native plant communities is unknown.

licença
cc-publicdomain
citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Taxonomy ( Inglês )

fornecido por Fire Effects Information System Plants
The currently accepted name for field bindweed is Convolvulus arvensis L.
It is a member of the morning-glory family (Convolvulaceae)
[30,37,50,54,60,64,70,71,81,88,96,110,145,146,149,153].
licença
cc-publicdomain
citação bibliográfica
Zouhar, Kris. 2004. Convolvulus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/vine/conarv/all.html

Distribution ( Espanhol; Castelhano )

fornecido por IABIN
I, II, III, IV, V, RM, VI, VII, VIII, IX, X, Juan Fernandez
licença
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direitos autorais
Universidad de Santiago de Chile
autor
Pablo Gutierrez
site do parceiro
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Convolvulus arvensis ( Asturiano )

fornecido por wikipedia AST
Pa ver otros usos d'esti términu, Carihuela y Cuerda.

Convolvulus arvensis L. (correhuela o cahiruela) ye una especie de planta trepadora del xéneru Convolvulus, nativa d'Europa y Asia.

 src=
Vista de la planta
 src=
Fueyes

Localización

Anque son natives d'Europa y la zona templada d'Asia, naturalizáronse n'otres zones del mundu.

Introducióse en Norteamérica, onde ta considerada como especie invasora en delles árees.

Descripción

Ye una planta perenne yerbácea rastrera y esguiladora que se desenvuelve hasta un altor de 0,5 a 2 metros. Les sos fueyes distribuyir n'espiral, son lliniales con forma terminal de punta de flecha, d'unos 2 a 5 centímetros de llargu, con un peciolu de 1 a 3 cm. Les flores con forma de trompeta, con un diámetru de 1 a 2,5 cm, de color rosa maciu o blancu, con cinco rayes radiales rosaes llevemente más escures.

Variedaes

  • Convolvulus arvensis var. arvensis. De fueyes amplies.
  • Convolvulus arvensis var. linearifolius. De fueyes estreches allargaes.

Usos

Anque produz flores curioses, ye de cutiu una planta incómoda nos xardinos considerada como una fadiosa meruxa por cuenta de la so crecedera y que pueden esgañar rápido a otres plantes cultivaes.

Ocupa bien fácilmente grandes superficies y enriédase a les plantes debilitándoles yá que-yos fai la competencia pola lluz, l'agua y los nutrientes. Cuando se desenvolvió dafechu, la gran masa de tarmos y de fueyes puede enzancar o torgar la recueya mecánica. La correhuela ye bien propensa a ser infectada pol fungu del oidio.

Control

Pelos medios mecánicos de llabranza ye malo d'esaniciar porque anque s'esanicien les partes aérees de los tarmos tien munches y fondos raigaños de les que vuelve viltar la correhuela.

Les yerbicíes que pueden emplegase son los de tipu sistémico que son absorbíos poles fueyes y actúen sobre los raigaños.

Taxonomía

Convolvulus arvensis foi descritu por Carlos Linneo y espublizóse en Species Plantarum 1: 153. 1753.[1]

Etimoloxía

Convolvulus: nome xenéricu que procede del llatín convolvere, que significa "enredar".[2]

arvensis: epítetu que procede del llatín arva, que significa "campu de llabranza", esto ye, que se trata d'una especie qu'apaez en campos cultivaos.

Sinonimia
  • Convolvulus ambigens House
  • Convolvulus incanus auct. non Vahl
  • Strophocaulos arvensis (L.) Small[3]
  • Convolvulus arvensis subsp. crispatus Franco
  • Convolvulus arvensis var. linearifolius Choisy
  • Convolvulus auriculatus Desr.
  • Convolvulus cherleri Agardh ex Roem. & Schult.
  • Convolvulus corsicus Roem. & Schult.
  • Convolvulus longipedicellatus Sa'ad[4][5]

Denominación popular

Altabaquillo, campanica, campaniella, campaniella de probe, campaniella de probes, campaniella probe, campanielles, campaniella montesa, campanuzas, campánula menor, carihuela, carregüela, carrehuela, carreuela, carrigüela, carrigüela fina, carrihuela, carrijuela, cerrihuela, cornihuela, corrayuela, corredora, corregüela, corregüela menor, correguela, correhuela, correhuela de los campos, correhuela menor, correjuela, correvuela, correyuela, corribuela, corrigüela, corrigüela cantu, corrigüela fina, corrigüela muerta, corrigüela viva, corriguala, corruela, corriola, corriola blanca, corrivuela, corriyuela, corroyuela, corrugüelas, corruhuela, corruviela, corruyuela, curriol, currujuela, curruyuela, enredadera, enredadera de los campos, enredadera, escarigüela, escarrigüelo, escoriegüela, escorigüela, escorrigüela, garrotilla, garrotiyu, gorrotilla, guniolas, hiedra de llagartu, filandera, filanderes, marañuela, maroma, panes, raízdecilla, torregüela, trababedarri de les pieces, yerba del muriu, zaramalla.[4]

Ver tamién

Referencies

  1. «Convolvulus arvensis». Tropicos.org. Missouri Botanical Garden. Consultáu'l 8 d'abril de 2014.
  2. En Flora de Canaries
  3. Llistáu de sinónimos de Convolvulus arvensis.[1].
  4. 4,0 4,1 «Convolvulus arvensis». Real Xardín Botánicu: Proyeutu Anthos. Consultáu'l 27 de payares de 2009.
  5. Convolvulus arvensis en The Plant List

Galería d'imáxenes

Referencies

Enllaces esternos

Cymbidium Clarisse Austin 'Best Pink' Flowers 2000px.JPG Esta páxina forma parte del wikiproyeutu Botánica, un esfuerciu collaborativu col fin d'ameyorar y organizar tolos conteníos rellacionaos con esti tema. Visita la páxina d'alderique del proyeutu pa collaborar y facer entrugues o suxerencies.
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wikipedia AST

Convolvulus arvensis: Brief Summary ( Asturiano )

fornecido por wikipedia AST
Convolvulus arvensis Pa ver otros usos d'esti términu, Carihuela y Cuerda.

Convolvulus arvensis L. (correhuela o cahiruela) ye una especie de planta trepadora del xéneru Convolvulus, nativa d'Europa y Asia.

 src= Vista de la planta  src= Fueyes
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Wikipedia authors and editors
original
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Çöl sarmaşığı ( Azerbaijano )

fornecido por wikipedia AZ
 src=
Convolvulus arvensis


Çöl sarmaşığı (lat. Convolvulus arvensis)[1] - sarmaşıq cinsinə aid bitki növü.[2]


Mənbə

  1. Nurəddin Əliyev. Azərbaycanın dərman bitkiləri və fitoterapiya. Bakı, Elm, 1998.
  2. Elşad Qurbanov. Ali bitkilərin sistematikası, Bakı, 2009.
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Vikipediya müəllifləri və redaktorları
original
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wikipedia AZ

Çöl sarmaşığı: Brief Summary ( Azerbaijano )

fornecido por wikipedia AZ
 src= Convolvulus arvensis


Çöl sarmaşığı (lat. Convolvulus arvensis) - sarmaşıq cinsinə aid bitki növü.


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Vikipediya müəllifləri və redaktorları
original
visite a fonte
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wikipedia AZ

Corretjola de conradís ( Catalão; Valenciano )

fornecido por wikipedia CA
 src=
Convolvulus arvensis

La corretjola, corretjola de conradís, corriola o campaneta (Convolvulus arvensis) és una planta de la família Convolvulaceae (la família del moniato) i del gènere Convolvulus.

Distribució

Té una distribució pràcticament cosmopolita, ja que no és gaire exigent pel que fa al clima ni a les condicions del sòl. Originària d'Europa i Àsia, s'ha introduït a l'Amèrica del Nord i del Sud. Està generalitzada a tots els Països Catalans. És una mala herba molt freqüent.[1] És una planta ruderal que creix en erms i terrenys degradats o alterats; també forma part de la vegetació espontània forestal.

Descripció

 src=
Corretjoles dominants a l'estiu a Castelltallat
 src=
Convolvulus arvensis

És una herba vivaç amb tiges i pecíols volubles que s'estenen per terra o s'enfilen per qualsevol suport. Les fulles són alternes, simples i amb forma de punta de llança. Les flors tenen els pètals soldats formant una campana de color blanc, rosat o amb estries d'aquests dos colors. El fruit és una càpsula arrodonida.

Danys

Ocupa molt fàcilment grans superfícies i s'enreda a les plantes i les debilita, ja que els fa la competència per la llum, l'aigua i els nutrients. Quan ha crescut molt, la gran massa de tiges i fulles pot dificultar o impedir la recol·lecció mecànica. La corretjola és molt susceptible de ser envaïda pel fong de l'oidi i pot encomanar aquesta malaltia a les plantes conreades.

Control

Amb les llaurades és difícil d'eliminar, perquè, encara que es talli la planta, l'arrel queda a dins de terra i la corretjola rebrota. Amb les tècniques de mínim conreu encara s'estén més. Els herbicides que cal fer servir són els de tipus sistèmic, que són absorbits per les fulles de la mala herba i penetren a tota la planta, que així mor des de l'arrel.

L'eruga del borinot gris (Agrius convolvuli) menja voraçment les fulles de corretjola, per això es coneix també com a borinot de les corretjoles.

Vegeu també

Referències

 src= A Wikimedia Commons hi ha contingut multimèdia relatiu a: Corretjola de conradís Modifica l'enllaç a Wikidata
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original
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wikipedia CA

Corretjola de conradís: Brief Summary ( Catalão; Valenciano )

fornecido por wikipedia CA
 src= Convolvulus arvensis

La corretjola, corretjola de conradís, corriola o campaneta (Convolvulus arvensis) és una planta de la família Convolvulaceae (la família del moniato) i del gènere Convolvulus.

licença
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Autors i editors de Wikipedia
original
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wikipedia CA

Cwlwm y cythraul ( Galês )

fornecido por wikipedia CY

Planhigyn blodeuol siap twmffat yw Cwlwm y cythraul sy'n enw gwrywaidd. Mae'n perthyn i'r teulu Convolvulaceae. Yr enw gwyddonol (Lladin) yw Convolvulus arvensis a'r enw Saesneg yw Field bindweed.[1] Ceir enwau Cymraeg eraill ar y planhigyn hwn gan gynnwys Cwlwm y Cythraul, Cynghafog Fechan, Cynghafog Lleiaf, Cynghafog y Maes, Llwyth y Clymlys, Perfedd y Cythraul, Taglys.

Mae gan y blodyn bump sepal, pump petal a pump brigeryn.

Gweler hefyd

Cyfeiriadau

  1. Gerddi Kew; adalwyd 21 Ionawr 2015
Comin Wikimedia
Mae gan Gomin Wikimedia
gyfryngau sy'n berthnasol i:
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Cwlwm y cythraul: Brief Summary ( Galês )

fornecido por wikipedia CY

Planhigyn blodeuol siap twmffat yw Cwlwm y cythraul sy'n enw gwrywaidd. Mae'n perthyn i'r teulu Convolvulaceae. Yr enw gwyddonol (Lladin) yw Convolvulus arvensis a'r enw Saesneg yw Field bindweed. Ceir enwau Cymraeg eraill ar y planhigyn hwn gan gynnwys Cwlwm y Cythraul, Cynghafog Fechan, Cynghafog Lleiaf, Cynghafog y Maes, Llwyth y Clymlys, Perfedd y Cythraul, Taglys.

Mae gan y blodyn bump sepal, pump petal a pump brigeryn.

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Awduron a golygyddion Wikipedia
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Svlačec rolní ( Checo )

fornecido por wikipedia CZ
 src=
Zobrazení lodyhy svlačce rolního

Svlačec rolní (Convolvulus arvensis) je vytrvalá, středně vysoká, narůžověle kvetoucí, ovíjivá rostlina známá jako houževnatý plevel polí a zahrad. Je jedním z mnoha druhů globálně se vyskytujícího rodu svlačec a v české floře je považován za archeofyt.

Rozšíření

Druh je rozšířen téměř po celé Evropě, neroste pouze v nejsevernějších oblastech. Jeho původní výskyt sahá z Evropy přes Malou Asii, jižní Sibiř a Střední Asii až na Dálný východ a do severozápadních oblastí Afriky. Zavlečen byl do Severní i Jižní Ameriky, Austrálie a na Nový Zéland. V České republice je, vyjma nejvyšších oblastí, hojně rozšířený po celém území.

Ekologie

Svlačec rolní roste jako plevelný druh téměř na všech typech půd, zvláště častý bývá na půdách vápnitých. Vyskytuje se na polích, pastvinách, v zahradách, ve vinicích, u cest a nezřídka na stanovištích dotčených lidskou činností, od nížin až po horní hranici pěstování polních kultur. Je náročný na světlo a proto se vyskytuje většinou v řídkých plodinách.

Popis

Vytrvalá bylina s poléhavými nebo vlevo se ovíjivými lodyhami až metr dlouhými. Vyrůstají z trvalého, dlouhého, plazivého, silně se větvícího oddenku s mnoha postranními kořeny, které společně vytvářejí mohutný kořenový systém sahající až 3 m hluboko. Větvené, tupě šestihranné lodyhy, lysé nebo řídce chlupaté, jsou střídavě porostlé dlouze řapíkatými listy které se směrem k vrcholu lodyhy zmenšují. Jejich průměrně 4 cm dlouhé čepele jsou úzce vejčité až kopinaté, vespod mají dva špičaté laloky, na konci jsou tupě špičaté a po obvodě celokrajné, žilnatinu mají zpeřenou. Mladé rostliny po poranění roní bílé mléko.

Vonné, srostloplátečné, oboupohlavné květy vyrůstají po jednom až třech z úžlabí listů na dlouhých stopkách se dvěma listenci. Vytrvalý kalich je tvořen pěti cípy 5 mm dlouhými, tři jsou o málo delší. Široce nálevkovitá koruna je pěticípá, asi 2 cm dlouhá a bývá bílá nebo narůžovělá. V květu je pět tyčinek, s nitkami spodem přirostlými ke koruně, s extrorzními prašníky a svrchní semeník nesoucí na vrcholu dlouhou čnělku s dvoulaločnou bliznou.

Květy se otevírají jen za slunného počasí, ráno mezi sedmou a osmou hodinou a zavírají se tentýž den v 13 až 14 hodin, tehdy jsou již odkvetlé. Kvetou od května do září, opylovány jsou létajícím hmyzem hledajícím na dně květu nektar. V případě neopylení hmyzem se květy při zavírání obvykle opylí autogamně.

Plodem je vejčitá dvoupouzdrá tobolka, asi 6 mm velká, která jen částečně vyčnívá z vytrvalého kalichu. Obsahuje zpravidla 4 semena v obrysu nepravidelně hruškovitá, 3 mm dlouhá a matně šedočerně zbarvená. Ploidie druhu 2n = 50.

 src=
Květ

Rozmnožování

Rostlina se rozmnožuje semeny a hlavně kořenovými výhonky. Z jedné rostliny se získá až 500 semen, která si podržují klíčivost i 20 let. Tobolky pukají až po dokonalém vyschnutí a proto jen menší část semen vypadá na pole hned, větší část zůstane až do jara v tobolkách na suchých rostlinách nebo se sklidí s plodinami. Semena mají tvrdé osemení a proto po uzrání klíčí jen ojediněle, většinou potřebují k narušení osemení přezimovat a na jaře pak klíčí spolehlivě. Průchod trávicím traktem zvířat jejich klíčivost zvyšuje. Semena jsou nejčastěji roznášena zaplevelenými komposty, půdou nebo stroji či nářadím.

Po vyklíčení se kořenový systém rostliny rychle rozrůstá a již za dva měsíce dosahuje přes metr hluboko. Na podzim se na oddencích zakládají pupeny, ze kterých na jaře vyrůstají nové lodyhy. Oddenky se silně větví, vytvářejí složitou síť a jejich poškození znásobuje množství pupenů. Část těchto lodyh však nevyjde na povrch, ale vytváří v půdě spirály. V kořenech se ukládají zásobní látky a pupeny jsou schopné vyklíčit i za dva roky. Orba a kypření půdy způsobuje rozšiřování křehkých kořenových úlomků po celém poli, mají velkou regenerační schopnost a mohou rašit až z hloubky 80 cm.

Rostliny mají své přirozené nepřátele, řídce se vyskytující motýly tmavoskvrnku svlačcovou (Tyta luctuosa) a pernatušku svlačcovou (Emmelina monodactyla), jejichž larvy se živí listy, květy a dozrávajícími semeny.

Význam

Svlačec rolní je stará léčivá rostlina, obsahující v listech mnohé alkaloidy, živice, projímavé pryskyřice a třísloviny. V lidovém léčitelství se používá ve směsích s jinými bylinami pro zvýšení vylučování žluče a zlepšení peristaltiky střev. Působí též jako silné projímadlo.

Je znám jako nebezpečný plevelný druh škodící kulturním rostlinám. Hlavní škodlivost nespočívá v odebíraní živin – ty získává z větších hloubek, kam kořeny pěstovaných rostlin nesahají –, ale v oplétání lodyh rostlin, které následně za deště polehají a tím se snižují výnosy. V pícninách zhoršuje kvalitu krmiva. Při silnějším zaplevelení půdy jej lze potlačit jen herbicidy.

Popínání

Popínavé lodyhy se nepřichycují úponky, ale ovíjejí se okolo opory. Vrchol stonku průběžně vykonává „pátrací pohyby“, otáčí se proti směru hodinových ručiček v kruhu o průměru několika centimetrů. Otáčku dokončí za příznivých podmínek za jednu až dvě hodiny. Toto otáčení je způsobováno nestejně velkým přirůstáním po stranách vrcholu stonku.[1][2][3][4][5][6]

Galerie

Reference

  1. HOSKOVEC, Ladislav. BOTANY.cz: Svlačec rolní [online]. O. s. Přírodovědná společnost, BOTANY.cz, rev. 15.08.2007 [cit. 2015-10-14]. Dostupné online. (česky)
  2. VONDRÁŠKOVÁ, Šárka. Ochrana kultur proti pleveli svlačci rolnímu [online]. Ústav zemědělské ekonomiky a informací, Praha, rev. 09.04.2004 [cit. 2015-10-14]. Dostupné online. (česky)
  3. MIKULKA, Jan; CHODOVÁ, D.; MARTINKOVÁ, Z. et al. Obrazový atlas plevelů: Svlačec rolní [online]. Výzkumný ústav rostlinné výroby, odbor Agroekologie, Praha – Ruzyně [cit. 2015-10-14]. Dostupné v archivu pořízeném dne 2016-06-16. (česky)
  4. POLÍVKA, František. Názorná květena zemí koruny české: Svlačec rolní [online]. Wendys, Zdeněk Pazdera, 1901 [cit. 2015-10-14]. S. 236. Dostupné online. (česky)
  5. BERTOVÁ, Lydia. Flóra Slovenska IV/4: Pupenec roľný [online]. VEDA, Vydavateľstvo Slovenskej akadémie vied, Bratislava, SK, 1988 [cit. 2015-10-14]. S. 537-538. Dostupné online. (slovensky)
  6. DEYL, Miloš. Plevele polí a zahrad. Ilustrace Otto Ušák. Praha: Československá akademie věd, 1956. 336-338 s. HSV 38873/55/SV3/6423. Kapitola Svlačec rolní, s. 220-221.

Externí odkazy

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Svlačec rolní: Brief Summary ( Checo )

fornecido por wikipedia CZ
 src= Zobrazení lodyhy svlačce rolního

Svlačec rolní (Convolvulus arvensis) je vytrvalá, středně vysoká, narůžověle kvetoucí, ovíjivá rostlina známá jako houževnatý plevel polí a zahrad. Je jedním z mnoha druhů globálně se vyskytujícího rodu svlačec a v české floře je považován za archeofyt.

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Agersnerle ( Dinamarquês )

fornecido por wikipedia DA

Agersnerle (Convolvulus arvensis), ofte skrevet ager-snerle, er en flerårig, slyngende eller nedliggende plante i snerle-familien. Bladene er spyd- eller pilformede og 2,5 centimeter lange. De hvide eller lyserøde blomster sidder på lange stilke og er vellugtende og 2,5-3,5 centimeter lange. På blomsterstilken findes to små, linjeformede forblade et stykke neden for blomsten. Agersnerle er udbredt over det meste af Jorden, borset fra troperne og arktis. Den er formodentlig hjemmehørende i Middelhavsområdet og har spredt sig med såsæd og lignende.

I Danmark er agersnerle almindelig på næringsrig jord i marker, haver, vejkanter, affaldspladser og på strandvolde. Den blomstrer i juni til september.[1] Blomsterne er kun åbne en enkelt dag og lukker sig kun op i solskinsvejr.

Kilder og eksterne henvisninger

  1. ^ Signe Frederiksen et al., Dansk flora, 2. udgave, Gyldendal 2012. ISBN 8702112191.


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Agersnerle: Brief Summary ( Dinamarquês )

fornecido por wikipedia DA

Agersnerle (Convolvulus arvensis), ofte skrevet ager-snerle, er en flerårig, slyngende eller nedliggende plante i snerle-familien. Bladene er spyd- eller pilformede og 2,5 centimeter lange. De hvide eller lyserøde blomster sidder på lange stilke og er vellugtende og 2,5-3,5 centimeter lange. På blomsterstilken findes to små, linjeformede forblade et stykke neden for blomsten. Agersnerle er udbredt over det meste af Jorden, borset fra troperne og arktis. Den er formodentlig hjemmehørende i Middelhavsområdet og har spredt sig med såsæd og lignende.

I Danmark er agersnerle almindelig på næringsrig jord i marker, haver, vejkanter, affaldspladser og på strandvolde. Den blomstrer i juni til september. Blomsterne er kun åbne en enkelt dag og lukker sig kun op i solskinsvejr.

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Acker-Winde ( Alemão )

fornecido por wikipedia DE

Die Acker-Winde (Convolvulus arvensis) ist eine in Europa weit verbreitete Pflanze aus der Familie der Windengewächse (Convolvulaceae).

Beschreibung

Es ist eine windende, mehrjährige, krautige Pflanze. Sie bildet im Boden ein dichtes Netzwerk von knotig verdickten „Wurzelsträngen“ aus, die immer wieder neue Sprossen hervortreiben, selbst wenn man die Pflanze oberflächlich gejätet hat. Die Spitzen der Sprossachsen führen kreisförmige Suchbewegungen durch (als Linkswinder von oben gesehen entgegen dem Uhrzeigersinn), um sich an einer geeigneten Unterlage emporwinden zu können.

Von der sehr ähnlich aussehenden Echten Zaunwinde (Calystegia sepium) unterscheidet sich die Acker-Winde durch die Blüten, die bei der Zaunwinde gut doppelt so groß wie bei der Acker-Winde werden können. Bei der Zaunwinde sind sie durchgehend strahlend weiß, während sie bei der Acker-Winde zartrosa oder bläulich getönt sein können und außen an den Nahtstellen der zusammengewachsenen Blütenblätter dunkle, keilförmig auf dem Blütenrand zulaufende Streifen aufweisen. Die Blüte der Zaunwinde hat außen zwei deutlich ausgeprägte grüne Vorblätter, die bei der Acker-Winde fehlen. Die Blütezeit ist zwischen April und Oktober.

Auch die Blätter unterscheiden sich bei beiden Arten: Bei der Zaunwinde sind sie eher rundlich, während sie bei der Acker-Winde länglich mit einer Spitze und zwei spitzen Ecken sind.

Blütezeit ist von Juni bis September.

Die Chromosomenzahl beträgt 2n = 48 oder 50.[1]

Ökologie

 src=
Kapselfrucht und Samen

Die Acker-Winde ist ein Rhizom- und Wurzelknospengeophyt, dessen Wurzeln zur Sprossbildung fähig sind. Sie ist eine linkswindende Kletterstaude und eine typische Trockenheitspflanze. Ihr Wurzelwerk reicht bis zwei Meter tief.[1] Abgeschnitten verwelkt sie jedoch rasch, weil ihre Wurzeln mit hoher Saugkraft für das Überleben unentbehrlich sind.

Die Blüten der Acker-Winde sind homogame „Große Trichterblumen“, die nur einen Tag geöffnet sind (Eintagsblumen). Bei kühlem Wetter kommt es zu Schließbewegungen (Thermonastie). Bei Regenwetter bleiben die Blüten geschlossen und gelten daher auch als Wetterpropheten. Der Nektar wird am Grunde des Fruchtknotens gebildet und ist von der Basis der Staubfäden bedeckt; deshalb führen nur fünf enge Spalten zum Nektar hin. Bestäuber sind Insekten aller Art, aber besonders treten Spiralhornbienen (Systropha) auf, die auf Windengewächse spezialisiert sind. Sie wälzen sich in den Blüten. Es findet aber auch Selbstbestäubung statt.

Während des Wachstums führt die Spitze des Triebes windentypische kreisende Bewegungen (Nutation) aus, wobei für einen Kreis nur wenige Stunden benötigt werden.

Die Früchte sind unauffällige, zur Reife nach unten hängende, 2-klappige Kapseln mit 4 oder 5 Samen. Der Samenansatz ist meist gering. Hauptausbreitung erfolgt durch den Menschen über Ackergeräte usw. Außerdem tritt Schwerkraftausbreitung, Zufallsausbreitung durch Weidetiere und Ausbreitung der Rollsamen als Bodenroller auf. Fruchtreife ist von August bis Oktober.

Die vegetative Vermehrung erfolgt durch Ausläufer und Wurzelsprosse. Bei der Bodenbearbeitung wachsen kleinste unterirdische Teile zu ganzen Pflanzen heran. Obwohl sie hübsche, zarte, rund 4–5 cm große Trichterblüten besitzt, ist sie in Gärten, auf Feldern und Weinbergen nicht gerne gesehen, weil sie sich an Kultur- und Zierpflanzen emporrankt und mit ihrem eigenen raschen Wachstum deren Entwicklung hemmt. Sie ist ein lästiges Acker- und Gartenunkraut.

Vorkommen

 src=
Variante der Acker-Winde mit kräftiger Färbung
 src=
Blüte, Detail
 src=
Acker-Winde (Convolvulus arvensis)

Außer auf Äckern findet man die Acker-Winde auf Wegen, Wiesen und Schuttplätzen. Sie gedeiht in Mitteleuropa auf frischen bis mäßig trockenen, nährstoff- und basenreichen, meist humusarmen Lehm- oder Tonböden.[1] Die Acker-Winde ist eine Charakterart des Convolvulo-Agropyretum aus dem Verband der Quecken-Halbtrockenrasen (Convolvulo-Agropyrion repentis).[1]

Ursprünglich in Eurasien und Nordafrika beheimatet, kommt sie heute fast weltweit in den gemäßigten bis subtropischen Zonen vor.[2]

Taxonomie

Convolvulus arvensis L. hat die Synonyme Convolvulus arvensis subsp. crispatus Franco und Convolvulus arvensis var. linearifolius Choisy[2]

Verwendung

Die Acker-Winde enthält in ihren Blättern Herz-Kreislauf-Glykoside und ist deshalb eine altbekannte Heilpflanze. Außerdem enthält die Pflanze psychoaktive Alkaloide, wie sie früher beispielsweise in „Hexensalben“ verwendet wurden.

Die Blüten bieten reichlich Nektar und Pollen für Bienen, Käfer und Schmetterlinge, insbesondere für den Windenschwärmer (Agrius convolvuli). Auch vom Vieh werden die Pflanzen als Bestandteil von Heu gerne gefressen. Für das Ackerwinden-Bunteulchen (Emmelia trabealis), einen stark spezialisierten Kleinschmetterling, sind die Blüten der Acker-Winde die einzige Raupennahrung. Die beiden heimischen Spiralhornbienen leben oligolektisch von der Acker-Winde.

Rezeption

Laut einer Kinderlegende der Brüder Grimm trank die Mutter Gottes aus der Blüte der Feldwinde einen Schluck Wein, indem sie es als Trinkglas benutzte. Daher kommt der Beiname Muttergottesgläschen.[3]

Trivialnamen

Für die Acker-Winde bestehen bzw. bestanden auch die weiteren deutschsprachigen Trivialnamen: Ackerwinde (Schlesien, Schweiz), Bedewinde (Schlesien), Erdwinde (Schlesien), Hergottkedelcher (Siebenbürgen), Kornwinde (Schlesien, Schweiz), Mittelwind, Pädewinde (Potsdam), Pathenwinde (Tübingen), Snerrkrut (Holstein, Fallersleben), Snirrkrut (Holstein, Fallersleben), Strumpfe (Österreich), Strupfe (Österreich), Teufelsdarm (Schlesien), Omspunnen Tüch (Helgoland), Wäwinde (Altmark), Waidach (Kärnten), Waen (Eifel bei Nürburg), Kleu Wedewinde (mittelniederdeutsch), Klen Wedewindeblom (mittelniederdeutsch), Klen Wedewindeglocken (mittelniederdeutsch), Weegbinn (Holstein), Wegewinne (Mecklenburg), Wewinne (Göttingen, Fallersleben), Wewinneke (Göttingen), Winda, Windel (Oberhessen), Kleine Winde (Schlesien), Weiß Winde und Windglöckchen (Schlesien).[4] Sie wird auch Windling oder Feldwinde genannt.

Literatur

Einzelnachweise

  1. a b c d Erich Oberdorfer: Pflanzensoziologische Exkursionsflora für Deutschland und angrenzende Gebiete. Unter Mitarbeit von Angelika Schwabe und Theo Müller. 8., stark überarbeitete und ergänzte Auflage. Eugen Ulmer, Stuttgart (Hohenheim) 2001, ISBN 3-8001-3131-5, S. 772.
  2. a b Rafaël Govaerts (Hrsg.): Convolvulus arvensis. In: World Checklist of Selected Plant Families (WCSP) – The Board of Trustees of the Royal Botanic Gardens, Kew, abgerufen am 20. November 2017.
  3. Jacob und Wilhelm Grimm: Kinder- und Hausmärchen: Kinderlegenden: Muttergottesgläschen. auf Zeno.org
  4. Georg August Pritzel, Carl Jessen: Die deutschen Volksnamen der Pflanzen. Neuer Beitrag zum deutschen Sprachschatze. Philipp Cohen, Hannover 1882, S. 109 (online).
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Acker-Winde: Brief Summary ( Alemão )

fornecido por wikipedia DE

Die Acker-Winde (Convolvulus arvensis) ist eine in Europa weit verbreitete Pflanze aus der Familie der Windengewächse (Convolvulaceae).

licença
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Autoren und Herausgeber von Wikipedia
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Czeliszczi Matczi Bòsczi ( Cassúbio )

fornecido por wikipedia emerging languages
 src=
Czeliszczi Matczi Bòsczi
 src=
Convolvulus arvensis - semińce i 3 semiona

Czeliszczi Matczi Bòsczi (Convolvulus arvensis L.) - wielelatnô roscëna z rodzëznë pòwijôczowatëch (Convolvulaceae Juss.). Òne roscą m. jin. na Kaszëbach.

Lëteratura

  • Przewodnik do rozpoznawania roślin i zwierząt na wycieczce / tekst Ute E. Zimmer, Alfred Handel ; oprac. całości Wilhelm i Dorothee Eisenreich ; [przekł. Ewa Rachańska, Piotr Kreyser] Warszawa : Multico, 1996, s. 154.
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Czeliszczi Matczi Bòsczi: Brief Summary ( Cassúbio )

fornecido por wikipedia emerging languages
 src= Czeliszczi Matczi Bòsczi  src= Convolvulus arvensis - semińce i 3 semiona

Czeliszczi Matczi Bòsczi (Convolvulus arvensis L.) - wielelatnô roscëna z rodzëznë pòwijôczowatëch (Convolvulaceae Juss.). Òne roscą m. jin. na Kaszëbach.

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Junaine ( Vepsiano )

fornecido por wikipedia emerging languages

Junaine (latin.: Convolvulus arvensis) om äivozne heinäsine kazmuz. Erik mülüb Junaiženvuiččed-sugukundha.

Kazmuz om levitadud Evrazijas, sidä kesken Evropas, Kavkazal, Sibiriš, Edahaižes Päivnouzmmas i Keskuzazijas. Invazivine erik Pohjoižamerikas, om todud sihe läz 1739 vot.

Ujelii jurišt sarakoičese. Junaižen seikh om kerdui hoik, sase 0,5..2 metrad pitte da sen enamba. Lehtesed kazdas 2..5 sm pitte. Vauktan vai ruskedvauvhan vižpalaižen änikon diametr oleleb 10..25 mm.

Sättub sötlemha maižanduzživatoid heinäl. Mülütab psihoaktivižid alkaloidid, ka Keskaigan ottihe junašt noidvoišken tehmižen aigan.

Homaičendad

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Junaine: Brief Summary ( Vepsiano )

fornecido por wikipedia emerging languages

Junaine (latin.: Convolvulus arvensis) om äivozne heinäsine kazmuz. Erik mülüb Junaiženvuiččed-sugukundha.

Kazmuz om levitadud Evrazijas, sidä kesken Evropas, Kavkazal, Sibiriš, Edahaižes Päivnouzmmas i Keskuzazijas. Invazivine erik Pohjoižamerikas, om todud sihe läz 1739 vot.

Ujelii jurišt sarakoičese. Junaižen seikh om kerdui hoik, sase 0,5..2 metrad pitte da sen enamba. Lehtesed kazdas 2..5 sm pitte. Vauktan vai ruskedvauvhan vižpalaižen änikon diametr oleleb 10..25 mm.

Sättub sötlemha maižanduzživatoid heinäl. Mülütab psihoaktivižid alkaloidid, ka Keskaigan ottihe junašt noidvoišken tehmižen aigan.

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Pispotjen (Convolvulus arvensis) ( Nds Nl )

fornecido por wikipedia emerging languages
 src=
Pispötjes

't Pispotjen (Latien: Convolvulus arvensis, Nederlaans: akkerwinde) is een plaante uut de wiendefemilie (Convolvulaceae). 't Pispotjen kump veur op grezige plekken, bouwlaand, langes wegen en in de dunen. De stengels wienen zich tegen de wiezers van de klokke in um plaanten of veurwarpen hinne.

Beschrieving

De bloeme is roze of wit en hef an de butenkaante donkerdere strepen. De bloemen hem een deursnee van 1,5 tot 3 centimeter. Der bin vuuf kelkblaojen mit ronde tanen. De bloemen hem een lekkere geur.

Een tot dree bloemen bleuien an een lange steel mit halverwegen twee schutblaojen. De bleuitied is van juni tot de harres.

De blaojen bin eierrond tot langwarpig en hem uutstaonde slippen an de voot. 't Pispotjen hef een onbehaoren deusvruch.

Fotogalderieje

Nedersaksisch

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Pispotjen (Convolvulus arvensis): Brief Summary ( Nds Nl )

fornecido por wikipedia emerging languages
 src= Pispötjes

't Pispotjen (Latien: Convolvulus arvensis, Nederlaans: akkerwinde) is een plaante uut de wiendefemilie (Convolvulaceae). 't Pispotjen kump veur op grezige plekken, bouwlaand, langes wegen en in de dunen. De stengels wienen zich tegen de wiezers van de klokke in um plaanten of veurwarpen hinne.

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Rolna pówitka ( Baixo Sorábio )

fornecido por wikipedia emerging languages

Rolna pówitka (Convolvulus arvensis) jo rostlina ze swójźby pówitkowych rostlinow (Convolvulaceae).

Wopis

 src=
Běłe kwiśonki z cerwjenymi flackami
 src=
Kapslowy płod a semjenja.

Rolna pówitka jo trajne zele, kótarež dośěgnjo wusokosć wót 20 až do 80 cm.

Kijaški su śańke a dołojce lažece, lězece abo nalěwo wijuce.

Łopjena

Łopjena su wutšobojte až šypojte a 3 až 6 raz tak dłujke kaž šyroke. Wóni dośěgnu dłujkosć wót 3 až do 4 cm.

Kwiśonki

Kwiśo wót junija až do septembra. Kwiśonki su lejkojte, běłe abo rožojte a dośěgnu dłujkosć wót 1,5 až do 2,5 cm. Wóni sejźe na dłujkich wogonkach w łopjenowych rozporach.

Stojnišćo

Rosćo na rolach, winicach, w zagrodach, na wótpadkowych městnach, drogowych kšomach a pustych płoninach. Ma lubjej małohumozne zemje.

Rozšyrjenje

Rostlina jo w Europje rozšyrjona.

Wužywanje

Nožki

  1. Starosta: Dolnoserbsko-nimski słownik, Niedersorbisch-deutsches Wörterbuch, Bautzen 1999, ISBN 3-7420-1096-4, bok 339
  2. W internetowem słowniku: Winde

Žrědła

  • Schauer - Caspari: Pflanzenführer für unterwegs, ISBN 978-3-8354-0354-3, 2. nakład, 2008, strona 220 (nim.)
  • Spohn, Aichele, Golte-Bechtle, Spohn: Was blüht denn da? Kosmos Naturführer (2008), ISBN 978-3-440-11379-0, strona 54 (nim.)

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Rolna pówitka: Brief Summary ( Baixo Sorábio )

fornecido por wikipedia emerging languages

Rolna pówitka (Convolvulus arvensis) jo rostlina ze swójźby pówitkowych rostlinow (Convolvulaceae).

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Vītoulė ( Samogitiano )

fornecido por wikipedia emerging languages
 src=
Vītoulės žėidā

Vītoulė (da kėtap: vītoulis, vītorie, vītorė, vītoris, vėjuoklė, vėjuoklis, vėjūns, vėjorks, ruoželė, ruožėkė, luotīnėškā: Convolvulus arvensis) ī tuokis augals, žuolie vėjorkė.

Vītoulė ī vėins tonkiausiu Lietovuos vėjorkiu. Tasā augals daugiametis ī, anou stiombris so šešiuom briaunuom, ožaug lėgo 170 cm ėlgoma, vīniuojas ont kėtū augalū, štolpū, aug pažemiou, ont takū. Lapā ėšėlgi, šuoblės skvarmas, 2–5 cm ėlgoma. Žiedā būn balti, rūžavi, margi, gardē kvepa, 1,9–2,5 cm skersmenė.

Vītoulė ikīrė piktžuolė ī. Aug laukūs, daržūs, tīrūs, suodnūs, smėltīsė, ont saulietu šlātū. Vejas ont rogiū, agrastu, lėnū, agounu, avėžū ė kėtū augalū, anūs sotrauk, golda. Vītoulės sonkē ravietė, ba nēn atpintė nū kėtū žuoliū.

Vītoulės jied kiaulės, avis, bet dėdlis šmuots gal' būtė kap trocīzna.

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Wegewinne ( Baixo-Saxão )

fornecido por wikipedia emerging languages

De Wegewinne (Convolvulus arvensis) is en mehrjöhrige Plant ut de Familie vun de Winnen. Se kümmt vör up Grasland, Boland, langs de Wege un up Dünen. Unner de Eer wasst en dicht Wuddelwarks. Dor kaamt jummers wedder nee Spraten vun tostanne, ok, wenn de Plant över de Eer utreten warrt. De Stengels winnt sik gegen den Wieser vun de Klock um Saken hen. Ofschoonst de Blomen smuck an to kieken sünd, will numms jem geern up'n Acker hebben, vunwegen datt de Wegewinne an Kulturplanten hoochklimmen deit un düsse bi dat Wassen stöört. Wenn dat för de Plant goot steiht, bruukt de Wegewinne bloß man 1,5 Stunnen, bit de Toppen vun en Spraat 3 cm in'n Krink wussen sünd.

De Blöte is rosa oder witt un hett an de Butenkant wat düstere Striepen. De Döörsnitt vun de Blöte is vun 1,5 cm bit 3 cm groot. De Blöte besteiht ut fiev Kroonblöer mit en rund Enn. Se röökt goot. Een bit dree Blöten bleiht an en langen Stengel. In de Midden vun den Stengel sitt twee Blöer an. Bleihen doot de Wegewinnen vun Juni bit to'n Harfst. Dat Veeh mag de Planten ganz geern freten.

Wo de Wegewinne mit dör'annersmeten weern kann

In'n Tuun gifft dat hüdigendags faken de Rickelwinn. De sütt meist akraat so ut, as de Wegewinne, bloß dat se man wat gröttere Blöten hett. De sünd ok witt un nich rosa.

Wo de Wegewinne vörkummt

Fröher hett dat de Wegewinne bloß man in Europa geven. Hüdigendags is se meist in all Länner vun'e Welt insleept wurrn.

Plattdüütsche Naams

In de plattdüütschen Gemarken hett düsse Plant ganz verschedene Naams:

  • Wegewinne, Wewinne, Wehewind
  • Pisspottje
  • Klimmup
  • Düvels Neihgaarn
  • Düvelsdarm
  • Slengelkruut
  • Fallbloom

Kiek ok bi

Weblenken

Commons-logo.svg . Mehr Biller, Videos oder Audiodateien to’t Thema gifft dat bi Wikimedia Commons.
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Wegewinne: Brief Summary ( Baixo-Saxão )

fornecido por wikipedia emerging languages

De Wegewinne (Convolvulus arvensis) is en mehrjöhrige Plant ut de Familie vun de Winnen. Se kümmt vör up Grasland, Boland, langs de Wege un up Dünen. Unner de Eer wasst en dicht Wuddelwarks. Dor kaamt jummers wedder nee Spraten vun tostanne, ok, wenn de Plant över de Eer utreten warrt. De Stengels winnt sik gegen den Wieser vun de Klock um Saken hen. Ofschoonst de Blomen smuck an to kieken sünd, will numms jem geern up'n Acker hebben, vunwegen datt de Wegewinne an Kulturplanten hoochklimmen deit un düsse bi dat Wassen stöört. Wenn dat för de Plant goot steiht, bruukt de Wegewinne bloß man 1,5 Stunnen, bit de Toppen vun en Spraat 3 cm in'n Krink wussen sünd.

De Blöte is rosa oder witt un hett an de Butenkant wat düstere Striepen. De Döörsnitt vun de Blöte is vun 1,5 cm bit 3 cm groot. De Blöte besteiht ut fiev Kroonblöer mit en rund Enn. Se röökt goot. Een bit dree Blöten bleiht an en langen Stengel. In de Midden vun den Stengel sitt twee Blöer an. Bleihen doot de Wegewinnen vun Juni bit to'n Harfst. Dat Veeh mag de Planten ganz geern freten.

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original
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wikipedia emerging languages

Печак ( Tajique )

fornecido por wikipedia emerging languages

Печак, ашақа, лаблоб (лот. Convōlvulus arvēnsis) — рустаниест аз хонадони печакиҳо. Печак гиёҳи печандаи бисёрсола аст. Растании доруворӣ. Дар илми тиб истифода бурда мешавад.

Макон

Ин гиёҳ қариб, ки дар ҳама ҷо — дар киштзорҳо (ҳамчун гиёҳи бегона ва зиёновар), кӯҳу дашт, қад-қади роҳҳо ва ҷӯйборҳо вомехӯрад. Гули хушбӯйи карнаймонанди пайвастабаргаш ранги сафед ё гулобӣ дорад. Миёни мардуми авом печак ҳамчун воситаи хунбанд ва таскинбахши ҷароҳатҳо ба кор меравад. Печак ғизои беҳтарини бузу гӯсфанд аст, вале барои чорвои калон, ба вижа асп, заҳролудкунандаву исҳоловар аст. Акнун ба «Канзи шифо»-и Ҳомидҷон Зоҳидов муроҷиат мекунем. Печак — ин гиёҳест, ки ҳар чӣ наздикаш бошад, ба он мепечад. Намудаш гуногун: сафед, сурх, зард ва бунафш аст. Тухмаш дар ғилофи сиёҳи моил ба сурхӣ ва қисме аз он бесамар мебошад. Биёраи ҳамаи навъҳои печак ширдор аст. Беҳтарини печакҳо қисми майдаи он аст. Мизоҷи навъи калони он мураккаб-ул-қувват, Ҷолинус дар дараҷаи дуввум сард ва хушк гуфтааст, вале табиб Юҳано бинни Мосавия гарм донистааст.

Сифати доругӣ

• инро бихӯранд, гиреҳҳои баданро мекушояд, дарунро мулоим мекунад, исҳол меоварад. Агар инро дар об биҷӯшонанд, қуввати гиреҳкушояш зиёда, вале дар овардани исҳол заиф мегардад бинобар он ки рутубатҳояш дар вақти ҷӯшондан таҳлил меёбанд. Аммо оби фишурдаи он акси ин хосиятро дорад. • Оби гиёҳи тару тозаи онро бо решаи савсани кӯҳӣ, натрун (танакори арманӣ) ва асал даромехта, дар бинӣ бирезанд, дарди сари кӯҳнаро шифо мебахшад. • Усораи онро, яъне оби гиёҳи тару тозаи онро дар офтоб ғафс гардонида, бо равғани зайтун даромехта чаконанд ва ё пахтаро ба он олонда дар гӯш гузоранд, дарди гӯшро таскин медиҳад ва даруни онро аз чирк пок мегардонад. • Барги печаки калони навъи сафеди онро биёшоманд, дарди сар, бемориҳои узвҳои даруни сина ва шушро шифо мебахшад, инчунин гиреҳи ҷигарро мекушояд. Агар обашро бинӯшанд, сурфаеро, ки аз баста шудани дарун мегирифта бошад ва кулинҷи аз моддаи гарм баамаломадаро дафъ мекунад, сафрои сӯхтаро бо воситаи исҳол аз бадан меронад. • 10,5 грамм гулашро кӯфта бихӯранд, захми рӯдаҳоро шифо мебахшад. • Барги тарашро бо сирко пухта гузошта банданд, дарди сипурзро дафъ мекунад. • Гули қисми печаки бесамарро бихӯранд ё кӯфтаи онро занҳо аз таг бардоранд, ҳайзро равон мегардонад. Агар онро сӯхта, занҳо баъд аз пок шудан аз ҳайз дудашро ба поёни шикам ва миёни пойҳои худ бигиранд, ҳомила шуданро манъ мекунад. • Баргашро кӯфта, бо асал сиришта, занҳо аз таг бардоранд, ҳайзи бандшударо равон мекунад. Бо оби баргаш занҳо андоми шарм ва даруни онро бишӯянд, бадбӯйии даруни бачадонро дафъ мекунад. • Оби барги тари печаки сафеди калонро бимоланд, варамҳои гарми буғумҳоро таҳлил медиҳад, пучак ва чиртакҳоро мекафонад. • Барги тари онро дар равған пухта гузошта банданд, варамҳоро таҳлил ва дардҳоро таскин медиҳад, мондагиро дафъ месозад, вале нопухтаи онро кӯфта гузошта банданд, ҷароҳатҳои калон ва сӯхтагии оташро шифо мебахшад. • Усораи онро, яъне оби онро, ки дар офтоб ғафс гардонда бошанд, бо мумравған сиришта гузошта банданд, низ сӯхтагии оташро сиҳат мекунад. • Қисми сиёҳи онро, яъне печаки гулаш бунафшро кӯфта гузошта банданд, захмҳои хабисаро (злокачественные язвы) шифо мебахшад. • Барги қисми бесамари онро пухта гузошта банданд, ҷароҳатҳои бадфиол ва раддиро ба ҳам оварда, сиҳат мебахшад ва сӯхтагии оташро ба ибро меоварад. • Усораи печаки сиёҳро ба мӯй бимоланд, онро сиёҳ мекунад. • Қисми печаки бесамарро кӯфта, бо шароб сиришта гузошта банданд, газидани ғундаро даво мешавад. Мизоҷи қисми ПЕЧАКИ КАЛОН, ки баргаш моил ба сиёҳӣ, дароз ва шахшӯл мебошад, хунук ва хушк аст. ХИСЛАТҲОИ ШИФОБАХШИ ОН: • агар инро бихӯранд, дарди узвҳои даруни сина, сурфа, бемориҳои сипурз, кулинҷ ва табҳои кӯҳнаро шифо мебахшад. • 75 грамм оби гиёҳи тари онро бо 35 грамм гули сурх бихӯранд, хунравиро аз ҳар як узве, ки бошад, қатъ мекунад. • Гиёҳи тари онро кӯфта гузошта банданд, ҷароҳатҳоро ба ҳам оварда сиҳат мебахшад, вале агар хушкашро кӯфта гузошта банданд, захмҳоро хушк ва захмҳои хабисаро дафъ мекунад. Ҳамаи навъҳои печак ҳангоми хӯрдан ба асаб, сар ва хичак зарар дорад. Давои ин намуди зарари он набот хӯрдан аст. Инчунин ҳомила шудани занонро ҳам манъ мекунад, ҳайзро низ қатъ месозад. Миқдори як бор нӯшидан аз оби он дар як рӯз аз 25 то 100 грамм аст ба шарте, ки онро наҷӯшонида бо набот биёшоманд. Мизоҷи ПЕЧАКҲОИ МАЙДА қариб монанди печаки калон аст, яъне мураккаб-ул-қувват мебошад.

Хоситҳои шифоӣ

  • Хосиятҳои умумии ин: варамҳоро таҳлил медиҳад, моддаҳои ғафсро дар бадан равон (суюқ) мегардонад, инчунин бинобар часпанда будани таркибаш моддаҳои сафровиро бо исҳол аз бадан дафъ мекунад. Ин навъи печак назар ба ҳамаи қисмҳои дигараш солимтар ва форамтар аст. Агар онро бихӯранд, ҳамаи навъҳои сурфаро, ки бо хушкии дарун бошанд, дафъ мекунад ва инчунин кулинҷро, ки сабабаш моддаҳои гарм бошад, шифо мебахшад.
  • Агар инро кӯфта гузошта банданд, варамҳои пайвандҳои бадан ва ғайраро таҳлил медиҳад.

Миқдори як бор нӯшидан аз оби ин гиёҳ дар як рӯз: 150 грамм бо 75 грамм набот бояд биёшоманд. Ба ҷойи ин оби барги гули хайрӣ ва оби тугмачагулро бинӯшанд, раво мебошад.

Нигаред

Чиннигул (Мухаллас)

Эзоҳ

Сарчашма

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Муаллифон ва муҳаррирони Wikipedia
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wikipedia emerging languages

Печак: Brief Summary ( Tajique )

fornecido por wikipedia emerging languages

Печак, ашақа, лаблоб (лот. Convōlvulus arvēnsis) — рустаниест аз хонадони печакиҳо. Печак гиёҳи печандаи бисёрсола аст. Растании доруворӣ. Дар илми тиб истифода бурда мешавад.

licença
cc-by-sa-3.0
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Муаллифон ва муҳаррирони Wikipedia
original
visite a fonte
site do parceiro
wikipedia emerging languages

Полска повивка ( Macedônio )

fornecido por wikipedia emerging languages

Полска повивка (лат. Convolvulus arvensis) е вид на повивка која расте во Европа и Азија. Ова е повеќегодишно зелјесто растение кое расте од 0.5-2 m во висина. Листовите му се спирално подредени, линерани до стрелести, со должина од 2-5 cm, со дршки од 1-3 см. Цветовите му се во облик на труба, со пречник од 1-2,5 см, бели или светло розови, со пет малку потемно розеви радијални пруги.

 src=
Цвет со црвени грини
 src=
Convolvulus arvensis

Постојат два вариетета:

  • Convolvulus arvensis сорт. arvensis. Пошироки листови.
  • Convolvulus arvensis сорт. linearifolius. Потесни листови.

Иако дава убави цветови, повивката се смета за непожелно растение и коров заради нејзиниот забрзан раст и со тоа ги гуши сите останати растенија. Ова растение е донесено во Северна Америка, каде претставува инвазивен вид во некои подрачја. Таму расте во густи покривки и навлегува во полињата, со тоа намалувајќи го приносот; само во 1998 ова растение направило штета на американското земјоделство во износ од $377 милиони. [1]

Наводи

  1. Coombs, E. M., et al., уредн. (2004). Biological Control of Invasive Plants in the United States. Corvallis: Oregon State University Press, 151.

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Автори и уредници на Википедија
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wikipedia emerging languages

Полска повивка: Brief Summary ( Macedônio )

fornecido por wikipedia emerging languages

Полска повивка (лат. Convolvulus arvensis) е вид на повивка која расте во Европа и Азија. Ова е повеќегодишно зелјесто растение кое расте од 0.5-2 m во висина. Листовите му се спирално подредени, линерани до стрелести, со должина од 2-5 cm, со дршки од 1-3 см. Цветовите му се во облик на труба, со пречник од 1-2,5 см, бели или светло розови, со пет малку потемно розеви радијални пруги.

 src= Цвет со црвени грини  src= Convolvulus arvensis

Постојат два вариетета:

Convolvulus arvensis сорт. arvensis. Пошироки листови. Convolvulus arvensis сорт. linearifolius. Потесни листови.

Иако дава убави цветови, повивката се смета за непожелно растение и коров заради нејзиниот забрзан раст и со тоа ги гуши сите останати растенија. Ова растение е донесено во Северна Америка, каде претставува инвазивен вид во некои подрачја. Таму расте во густи покривки и навлегува во полињата, со тоа намалувајќи го приносот; само во 1998 ова растение направило штета на американското земјоделство во износ од $377 милиони.

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Шееронь карькс ( Moksha )

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 src=
Шееронь карькс, Convolvulus althaeoides. Flora Graeca 1806 к., рисавазе Фердинанд Бауэр
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Convolvulus arvensis

Шееронь карькс паксяньConvolvulus arvensis – ламакизонь тишень кондям касы, лувондови шееронь карьксоннетнедиConvolvulaceae. Касы сембе вастова, апак лувонтт Крайняй Северть. Рузкс тенза мярьрихть вьюнок, березка, берестень, тянучка. Тишесь кувака (васетькшевихть фкя метрань кувалмоса), ацаф модать лангса или ашкотф лия тишетненди. Лопанза кувака пильгоня лангсот, сянгярят. Видьмонза ёмлат равжет. Панчфонза оцюфт, акша или инезиаза-акша тюсса. Шееронь карькссь касы паксява соронь тишекс, перева, коське лугава, лоткова[1]..

Лятфтамат

  1. П.Голышенков "Лекарственные растения и их использование", Саранск ош, 1966 к., 83 л.
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Шееронь карькс: Brief Summary ( Moksha )

fornecido por wikipedia emerging languages
 src= Шееронь карькс, Convolvulus althaeoides. Flora Graeca 1806 к., рисавазе Фердинанд Бауэр  src= Convolvulus arvensis

Шееронь карькс паксянь – Convolvulus arvensis – ламакизонь тишень кондям касы, лувондови шееронь карьксоннетнеди – Convolvulaceae. Касы сембе вастова, апак лувонтт Крайняй Северть. Рузкс тенза мярьрихть вьюнок, березка, берестень, тянучка. Тишесь кувака (васетькшевихть фкя метрань кувалмоса), ацаф модать лангса или ашкотф лия тишетненди. Лопанза кувака пильгоня лангсот, сянгярят. Видьмонза ёмлат равжет. Панчфонза оцюфт, акша или инезиаза-акша тюсса. Шееронь карькссь касы паксява соронь тишекс, перева, коське лугава, лоткова..

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हिरन खुरी ( Hindi )

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हिरनखुरी
 src=
Convolvulus arvensis

हिरनखुरी (वैज्ञानिक नाम : कानओलबूलस आर्वेन्सिस / Convolvulus arvensis) खरपतवार की एक जाति है जो एशिया एवं यूरोप का मूलवाली है। यह पसरने या चढ़ने वाली शाकभक्षी (herbaceous) लता है जो 0.5-2 मीटर ऊंची होती है। यह गेहूँ इत्यादि में उगती है।

यह बेलदार पौधा जमीन पर फैलता है एवं नमीदार भूमि में नालियों आदि में फैलता है । इसका साग(घुटी हुई एक प्रकार की भारतीय भाजी) भी गामों (villages) में बनाकर बाजरे एवं धान की रोटी से खाया जाता है , यह बहुतायत में बरसात के मौसम में पनपती है ।

बाहरी कड़ियाँ

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हिरन खुरी: Brief Summary ( Hindi )

fornecido por wikipedia emerging languages
 src= हिरनखुरी  src= Convolvulus arvensis

हिरनखुरी (वैज्ञानिक नाम : कानओलबूलस आर्वेन्सिस / Convolvulus arvensis) खरपतवार की एक जाति है जो एशिया एवं यूरोप का मूलवाली है। यह पसरने या चढ़ने वाली शाकभक्षी (herbaceous) लता है जो 0.5-2 मीटर ऊंची होती है। यह गेहूँ इत्यादि में उगती है।

यह बेलदार पौधा जमीन पर फैलता है एवं नमीदार भूमि में नालियों आदि में फैलता है । इसका साग(घुटी हुई एक प्रकार की भारतीय भाजी) भी गामों (villages) में बनाकर बाजरे एवं धान की रोटी से खाया जाता है , यह बहुतायत में बरसात के मौसम में पनपती है ।

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Córzoól ( Eml )

fornecido por wikipedia emerging_languages

I córzoj (Sing. córzoól) i én d'èrbi dal gènòr Convolvulus(L., 1753), un gènór con doseént-sinquanta sòrti'd pianti chi fan pärta'd la famija dil Convolvulaceae. Con la paróla córzoól in gènór a s'inténda la sòrta Convolvulus arvensis ch'in Itâlija l'é difusa dapartùt, tant in t'la piana cme in t'il montagni.

Descrisión

Al córzoól l'é una piânta rampicanta c'la pol gnir longa anca pù'd du metòr. La fa di risòma bón d'arbuteèr tant c'me col ed la gramìgna e di fioór bianc chi polén tendór al rosiólén.

Al Convolvulus arvensis al fiorisà da Avrîl a Òtòbar e l'é considerè un'infestânta in t'il colturi ed fórmént e'd mélgón.

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Di córzój rampè su par dil gambi'd fórmént

Variétè

Convolvulus arvensis var. arvensis col foij lärghi e Convolvulus arvensis var. linearifolius col foij pù strichì.

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Córzoól: Brief Summary ( Eml )

fornecido por wikipedia emerging_languages

I córzoj (Sing. córzoól) i én d'èrbi dal gènòr Convolvulus(L., 1753), un gènór con doseént-sinquanta sòrti'd pianti chi fan pärta'd la famija dil Convolvulaceae. Con la paróla córzoól in gènór a s'inténda la sòrta Convolvulus arvensis ch'in Itâlija l'é difusa dapartùt, tant in t'la piana cme in t'il montagni.

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Convolvulus arvensis ( Inglês )

fornecido por wikipedia EN

Convolvulus arvensis, the field bindweed, is a species of bindweed that is rhizomatous and is in the morning glory family (Convolvulaceae),[1] native to Europe and Asia. It is a climbing or creeping herbaceous perennial plant with stems growing to 0.5–2 metres (1.6–6.6 ft) in length, usually found at ground level, with small, white and pink flowers.

Other common names, mostly obsolete, include lesser bindweed, European bindweed, withy wind (in basket willow crops), perennial morning glory, small-flowered morning glory, creeping jenny, and possession vine.

Taxonomy

This plant first gained its scientific name in 1753, when it was described by Linnaeus in the Species Plantarum. In the centuries afterwards it gained many subspecies and varieties across its vast range, as well as synonyms as purportedly new species were described from places like China, Russia, Egypt or Morocco. New species and forms were even described from areas like Chile, Mexico and California when botanists encountered the plant there,[2][3] although it is not native to these areas.[2]

Convolvulus arvensis, Zaamin National Park, Uzbekistan

In the ninth volume of Augustin Pyramus de Candolle's Prodromus, published in 1845, Jacques Denys Choisy reduced a number of these synonyms to ten varieties of Convolvulus arvensis,[4] although he also recognised a number of species now also reduced to synonyms of C. arvensis.[2][3] Over time, most or all of these species and varieties were no longer recognised by the relevant authorities.[5]

In the 2009 Flora of Great Britain and Ireland, Peter Derek Sell described nine new forms he believed he had discovered in Cambridgeshire, especially along Fen Road in the village of Bassingbourn cum Kneesworth. The incredible bindweed biodiversity of Bassingbourn cum Kneesworth was not deemed credible by subsequent taxonomists, however, and the species is currently considered to be monotypic by most authorities.[2][3]

Description

Convolvulus arvensis is a perennial vine. It will climb to some one metre high. Underground the vine produces more or less woody rhizomes,[5] from which it re-sprouts in the spring, or when the above ground vines are removed.

The leaves are spirally arranged, linear to arrowhead-shaped, 2–5 cm (0.79–1.97 in) long and alternate, with a 1–3 cm (0.39–1.18 in) petiole. The flowers are trumpet-shaped, 1–2.5 cm (0.39–0.98 in) diameter, white or pale pink, with five slightly darker pink radial stripes. Flowering occurs in the mid-summer,[6] (in the UK, between June and September,[7]) when white to pale pink, funnel-shaped flowers develop. Flowers are approximately 0.75–1 in (1.9–2.5 cm) across and are subtended by small bracts. Fruit are light brown, rounded and 0.125 inches (3.2 mm) wide. Each fruit contains 2 or 4 seeds that are eaten by birds and can remain viable in the soil for decades. The stems climb by twisting around other plant stems in a counter-clockwise direction.[6]

Flower with red velvet mites
Convolvulus arvensis capsules and seeds
Convolvulus arvensis in pink

Similar species

Convolvulus arvensis can be confused with a number of similar weed species. Key traits are the small flowers often crowded together, and two sharp, backwards-pointed lobes at the base of the usually arrow-shaped leaf ending in a sharp apex.[8] Juvenile stems exude a milky sap when broken.[9]

In China, the most similar and only other vinaceous Convolvulus species is C. steppicola (most of the Convolvulus species are shrubs or herbaceous perennials),[10] however this species has a thick woody rootstock, almost no petioles, and only grows in northern Yunnan,[10][11] where C. arvensis is absent.[5]

Ecology

Plants are typically found inhabiting farmland,[5][7][12] waste places,[5][7][13] along roads,[5][12][13] in pastures,[12][13] grassy slopes,[5] and also along streams in North America.[12] It is able to colonise hot asphalt surface by covering it from the sides of roads, and worm its way between pavement stones.[7] It grows from 600 to 4,500 metres (2,000 to 14,800 ft) in altitude in China, and is absent from the warmer southern provinces.[5] It prefers dry areas with humus-poor, nutrient-rich and alkaline soils. It is a characteristic species in the phytosociological vegetation association Convolvulo-Agropyretum, belonging to the couch grass dry grasslands alliance (called Convolvulo-Agropyrion repentis in syntaxonomy).[13]

Like the other Convolvulus bindweeds of Eurasia, it is specifically pollinated by sweat bees in the genus Systropha. These are specialists (oligolectic) feeding upon the flowers of these plants, possessing unusual modifications of the scopa, such that almost the entire abdomen (including the dorsal surface) is used for carrying pollen, rather than the legs, as in most bees.[14] Species of Systropha in central Europe (such as S. curvicornis and S. planidens, both uncommon bees) are essentially entirely dependent upon C. arvensis. Although both species specialise on the same plant species, S. curvicornis is a habitat generalist while S. planidens is only found in steppe habitats,[15] although they are also found occurring together. The males of both species claim territories consisting of a patch of bindweed flowers, perching on the flowers in the afternoon after a regular patrol of their little patch for errant conspecific males, which, upon countenance, they proceed to attack the intruder by ramming him from the air with a specialised protuberance on their lower abdomen. Sometimes bumblebees, honey bees or other insects are air-bombed, but never rammed. The males retreat inside the flower after the perching session, as it closes in the late afternoon, spending the night inside the flower and escaping at dawn before or after it fully closes (the females stay in underground tunnel nests). The males only land on flowers (sometimes of other plants), eschewing other perches, and feed on the nectar. Females forage for nectar and pollen in the morning and early afternoon while flowers stay open. Most copulation occurs in bindweed flowers: when a virgin female wanders into their patch, and the larger males find them busy at one of their flowers during morning patrol, the males pounce upon them without ado and immediately establish contact with their mutual genitalia, getting the job done on average 90 seconds later.[16] These species are themselves specifically parasitised upon by the cuckoo bee Biastes brevicornis.[17]

As an invasive

Outside its native range, field bindweed does not appear to be a significant threat to natural habitats. It primarily requires disturbed ground (agricultural land),[18][19] and is easily shaded out by taller shrubs and trees. It may dominate the ground flora in some low quality, open grassland areas, however.[18] In North America it can become the or a co-dominant plant in specific habitats: the low vegetation found around vernal pools in Sacramento County, and around large pools in Tehama County, California; riparian corridors in Wyoming and Colorado; aspen stands and mountain-mahogany (Cercocarpus spp.) shrubland/grassland in Colorado; and disturbed riverbank areas in the Montreal area of Canada.[19] In some nature parks, it is commonly found in areas of disturbed soil, such as camp grounds or around horse corrals in California. Similarly, the report of its invasive character from Colorado is from former agricultural land being restored to a more natural state by The Nature Conservancy. Employees for the same organisation also reported that it was a significant weed on an irrigated plot of farmland in northern Idaho where native bunchgrass and forbs were cultivated, insofar that it caused "decreasing biodiversity" on the land.[19]

It is thought to have little effect on native fauna, although it may sometime be eaten by farm livestock. It may cause photosensitisation in susceptible animals. There is a report of its roots (rhizomes) being possibly poisonous to pigs.[18][19] and the alkaloids it contains may be poisonous to horses in sufficient amounts.[20] There are also reports of it being eaten by sheep and pigs to control it without reported problems.[19]

Chemistry

Bindweed contains several alkaloids which are toxic for mice, including pseudotropine, and lesser amounts of tropine, tropinone, and meso-cuscohygrine.[21]

Economic impacts

Although it produces attractive flowers, it is often unwelcome in gardens as a nuisance weed due to its rapid growth and choking of cultivated plants. It was most likely introduced into North America as a contaminant in crop seed as early as 1739, and became an invasive species. Its dense mats invade agricultural fields and reduce crop yields; it is estimated that crop losses due to this plant in the United States exceeded US$377 million in the year 1998 alone.[12] It is one of the most serious weeds of agricultural fields in many temperate regions of the US.[22]

Control and management

Bindweed is difficult to eliminate. Roots may extend as far as 9 feet (2.7 m) deep, according to one source,[9] or 30 feet (9.1 m), according to another.[23] New plants may sprout from seeds that are up to 20 years old.[24] New plants can also form from root runners[23] and root fragments.[9]

Methods for controlling bindweed include:

  • Physical removal: Bindweed can be controlled by pulling it out by hand or plowing it up every three weeks, for three[9] up to seven years.[23][19]
  • Mulching: Applying a thick barrier to block sun may control bindweed.[23]
  • Soil solarization for six to nine weeks in California was found to kill seedlings entirely, and control adult plants, but only for three weeks after treatment.[19]
  • Boiling water, placed on the plant, only practical for small areas.[25]
  • Biological control: Some insects and mites can eat, distort or stunt bindweed, but do not fully control it.[26]
  • Grazing: In Minnesota, sheep are able to consistently completely rid an infested pasture of the bindweed in two seasons, but only when the pasture is used to grow annual grains.[19]
  • In general, plant species which grow vigorously in the winter and early spring are best at smothering emerging shoots.[19]
  • It can be controlled by glyphosate.[19]
  • Other herbicides usually recommended for this species are 2,4-D, dicamba, picloram, quinclorac and paraquat.[19]

In culture

In one of the tales collected by Jacob and Wilhelm Grimm, Our Lady's Little Glass, this flower is used by Mary, mother of Jesus, to drink wine with when she helps free a wagoner's cart. The story goes on to say that "the little flower is still always called Our Lady's Little Glass".[27]

References

  1. ^ Parnell, J. and Curtis, T. 2012. Webb's An Irish Flora. Cork University Press. ISBN 978-185918-4783
  2. ^ a b c d Govaerts, Rafaël (2021). "Convolvulus arvensis L., Sp. Pl.: 153 (1753)". World Checklist of Selected Plant Families. Royal Botanic Gardens, Kew. Retrieved 9 July 2021.
  3. ^ a b c Wunderlin, R. P.; Hansen, B. F.; Franck, A. R.; Essig, F. B. (8 July 2021). "Convolvulus arvensis". Atlas of Florida Plants. Institute for Systematic Botany, University of South Florida, Tampa. Retrieved 9 July 2021.
  4. ^ Choisy, Jacques Denys (1845). Prodromus systematis naturalis regni vegetabilis (in Latin). Vol. 9. Paris: Fortin, Masson et sociorum. pp. 406, 407. doi:10.5962/bhl.title.286.
  5. ^ a b c d e f g h Fang, Ruizheng; Staples, George (1995). "Convolvulus arvensis Linnaeus, Sp. Pl. 1: 153. 1753". Flora of China. Vol. 16 (Gentianaceae through Boraginaceae). St. Louis: Missouri Botanical Garden Press.
  6. ^ a b Clapham, A.R., Tutin, T.G. and Warburg, E.F. 1968 Excursion Flora of the British Isles Second Edition Cambridge University Press.ISBN 0-521-04656-4
  7. ^ a b c d Reader's Digest Field Guide to the Wild Flowers of Britain. Reader's Digest. 1981. p. 250. ISBN 978-0-276-00217-5.
  8. ^ a b c d Muma, Walter. "Field Bindweed (Convolvulus arvensis)". Ontario Wildflowers. Walter Muma. Retrieved 10 July 2021.
  9. ^ a b c d e f "Bidding Farewell to the Dreaded Bindweed". Oregon State University Extension Service. September 2008. Archived from the original on 16 July 2019.
  10. ^ a b Fang, Ruizheng; Staples, George (1995). "Convolvulus Linnaeus, Sp. Pl. 1: 153. 1753". Flora of China. Vol. 16 (Gentianaceae through Boraginaceae). St. Louis: Missouri Botanical Garden Press.
  11. ^ Fang, Ruizheng; Staples, George (1995). "Convolvulus steppicola Handel-Mazzetti, Symb. Sin. 7: 810. 1936". Flora of China. Vol. 16 (Gentianaceae through Boraginaceae). St. Louis: Missouri Botanical Garden Press.
  12. ^ a b c d e Coombs, E. M., et al., Eds. (2004). Biological Control of Invasive Plants in the United States. Corvallis: Oregon State University Press, 151.
  13. ^ a b c d Oberdorfer, Erich (2001). Pflanzensoziologische Exkursionsflora für Deutschland und angrenzende Gebiete. Unter Mitarbeit von Angelika Schwabe und Theo Müller. 8., stark überarbeitete und ergänzte Auflage (in German). Stuttgart (Hohenheim): Eugen Ulmer. p. 772. ISBN 3-8001-3131-5.
  14. ^ Michener, C.D. (2000). The Bees of the World. Johns Hopkins University Press
  15. ^ Bogusch, Petr; Bláhová, Eliška; Horák, Jakub (21 October 2020). "Pollen specialists are more endangered than non-specialised bees even though they collect pollen on flowers of non-endangered plants". Arthropod-Plant Interactions. 14 (6): 759–769. doi:10.1007/s11829-020-09789-y. S2CID 226325867.
  16. ^ Fraberger, Raphaelo J.; Ayasse, Manfred (October 2007). "Mating Behavior, Male Territoriality and Chemical Communication in the European Spiral-Horned Bees, Systropha planidens and S. curvicornis (Hymenoptera: Halictidae)". Journal of the Kansas Entomological Society. 80 (4): 348–360. doi:10.2317/0022-8567(2007)80[348:MBMTAC]2.0.CO;2. JSTOR 25086401. S2CID 86029808. Retrieved 9 July 2021.
  17. ^ Müller, Andreas; Krebs, Albert; Amiet, Felix (1997). Bienen. Mitteleuropäische Gattungen, Lebensweise, Beobachtung (in German). Augsburg: Naturbuch-Verlag. ISBN 3-89440-241-5.
  18. ^ a b c "Impact Assessment - Bindweed (Convolvulus arvensis) in Victoria (Nox)". Victorian Resources Online. State of Victoria (Agriculture Victoria). 1996. Retrieved 8 July 2021.
  19. ^ a b c d e f g h i j k Zouhar, Kris (2004). "SPECIES: Convolvulus arvensis". Fire Effects Information System. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Retrieved 8 July 2021.
  20. ^ Todd, Fred G.; Stermitz, Frank R.; Schultheis, Partricia; Knight, Anthony P.; Traub-Dargatz, Josie (May 1995). "Tropane alkaloids and toxicity of Convolvulus arvensis". Phytochemistry. 39 (2): 301–303. doi:10.1016/0031-9422(94)00969-Z. PMID 7495531.
  21. ^ Vet Hum Toxicol. 1995 Oct;37(5):452-4. Toxicity of field bindweed (Convolvulus arvensis) to mice. Schultheiss PC1, Knight AP, Traub-Dargatz JL, Todd FG, Stermitz FR.
  22. ^ "The 10 Types of Weeds That Are Most Dangerous for Your Crops". www.gvcfarmsupply.com. 2018-10-31. Retrieved 6 June 2021.
  23. ^ a b c d Beddes, Taun (24 September 2014). "Tips on Controlling Bindweed". Utah State University Extension. Archived from the original on 16 July 2019.
  24. ^ USDA Forest Service. "Weed of the Week: Field Bindweed" (PDF). Archived from the original (PDF) on 16 July 2019.
  25. ^ "StackPath". www.gardeningknowhow.com. Retrieved 6 June 2021.
  26. ^ Cortat, Ghislaine (15 November 2018). "Convolvulus arvensis (bindweed)". Invasive Species Compendium. CAB International. Archived from the original on 16 July 2019.
  27. ^ "Our lady's little glass". Grimms' Fairy Tales. Retrieved 12 July 2021.

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Convolvulus arvensis: Brief Summary ( Inglês )

fornecido por wikipedia EN

Convolvulus arvensis, the field bindweed, is a species of bindweed that is rhizomatous and is in the morning glory family (Convolvulaceae), native to Europe and Asia. It is a climbing or creeping herbaceous perennial plant with stems growing to 0.5–2 metres (1.6–6.6 ft) in length, usually found at ground level, with small, white and pink flowers.

Other common names, mostly obsolete, include lesser bindweed, European bindweed, withy wind (in basket willow crops), perennial morning glory, small-flowered morning glory, creeping jenny, and possession vine.

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Agra konvolvulo ( Esperanto )

fornecido por wikipedia EO

La agra konvolvulo (Convolvulus arvensis) estas planto el la familio de (Konvolvulacoj). Ĝi troviĝas sur herboriĉaj lokoj, kulturkampoj, laŭlonge de vojoj kaj en la dunoj. La tigoj volviĝas kontraŭ-horloĝdirekten ĉirkaŭ objektoj.

La floro estas rozkolora aŭ blanka kaj havas malhelajn striojn je la ekstera flanko. La floroj havas diametron de 1,5 ĝis 3 cm. Estas kvin sepaloj kun rondaj dentoj. La floroj bonodoras. Unu ĝis tri floroj floras sur longa tigo kun duonvoje du brakteoj. En Eŭropo la florado daŭras de junio ĝis la aŭtuno.

La konvolvulo havas senharan kapsulon.

La folioj estas ovalaj ĝis oblongaj kaj havas elstarajn baskojn ĉe la piedo.

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Convolvulus arvensis ( Espanhol; Castelhano )

fornecido por wikipedia ES

Convolvulus arvensis L. (correhuela o cahiruela) es una especie de planta trepadora del género Convolvulus, familia Convolvulaceae, nativa de Europa y Asia.

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Vista de la planta
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Hojas

Distribución

Aunque son nativas de Europa y la zona templada de Asia, se han naturalizado en otras zonas del mundo.

Ha sido introducida en Norteamérica, donde está considerada como especie invasora en algunas áreas.

Descripción

Es una planta perenne herbácea rastrera y trepadora que se desarrolla hasta una altura de 0,5 a 2 metros. Sus hojas se distribuyen en espiral, son lineares con forma terminal de punta de flecha, de unos 2 a 5 centímetros de largo, con un peciolo de 1 a 3 cm. Las flores con forma de trompeta, con un diámetro de 1 a 2,5 cm, de color rosa pálido o blanco, con cinco rayas radiales rosadas levemente más oscuras.

Variedades

  • Convolvulus arvensis var. arvensis. De hojas amplias.
  • Convolvulus arvensis var. linearifolius. De hojas estrechas alargadas.

Usos

Aunque produce flores atractivas, es a menudo una planta molesta en los jardines considerada como una mala hierba debido a su crecimiento y que pueden estrangular rápidamente a otras plantas cultivadas.

Ocupa muy fácilmente grandes superficies y se enreda a las plantas debilitándolas ya que les hace la competencia por la luz, el agua y los nutrientes. Cuando se ha desarrollado plenamente, la gran masa de tallos y de hojas puede dificultar o impedir la recolección mecánica. La correhuela es muy propensa a ser infectada por el hongo del oídio.

Control

Es difícil de eliminar por medios mecánicos de labranza porque aunque se eliminen las partes aéreas de los tallos tiene muchas y profundas raíces de las que la correhuela vuelve a rebrotar.

Los herbicidas que se pueden emplear son los de tipo sistémico que son absorbidos por las hojas y actúan sobre las raíces.

Taxonomía

Convolvulus arvensis fue descrito por Carlos Linneo y publicado en Species Plantarum 1: 153. 1753.[1]

Etimología

Convolvulus: nombre genérico que procede del latín convolvere, que significa "enredar".[2]

arvensis: epíteto que procede del latín arva, que significa "campo de labranza", es decir, que se trata de una especie que aparece en campos cultivados.

Sinonimia
  • Convolvulus ambigens House
  • Convolvulus incanus auct. non Vahl
  • Strophocaulos arvensis (L.) Small[3]
  • Convolvulus arvensis subsp. crispatus Franco
  • Convolvulus arvensis var. linearifolius Choisy
  • Convolvulus auriculatus Desr.
  • Convolvulus cherleri Agardh ex Roem. & Schult.
  • Convolvulus corsicus Roem. & Schult.
  • Convolvulus longipedicellatus Sa'ad[4][5]

Nombres populares

Altabaquillo, campanica, campanilla, campanilla de pobre, campanilla de pobres, campanilla pobre, campanillas, campanilla silvestre, campanuzas, campánula menor, carihuela, carregüela, carrehuela, carreuela, carrigüela, carrigüela fina, carrihuela, carrijuela, cerrihuela, cornihuela, cornijuela, corrayuela, corredora, corregüela, corregüela menor, correguela, correhuela, correhuela de los campos, correhuela menor, correjuela, correvuela, correyuela, corribuela, corrigüela, corrigüela borde, corrigüela fina, corrigüela muerta, corrigüela viva, corriguala, corrihuela, corriola, corriola blanca, corrivuela, corriyuela, corroyuela, corrugüelas, corruhuela, corruviela, corruyuela, curriol, currujuela, curruyuela, enredadera, enredadera de los campos, enredadera, escarigüela, escarrigüelo, escoriegüela, escorigüela, escorrigüela, garrotilla, garrotillo, gorrotilla, guniolas, hiedra de lagarto, hilandera, hilanderas, marañuela, maroma, panes, raízdecilla, torregüela, trababedarri de las piezas, yerba del muro, zaramalla.[4]

Galería de imágenes

Referencias

  1. «Convolvulus arvensis». Tropicos.org. Missouri Botanical Garden. Consultado el 8 de abril de 2014.
  2. En Flora de Canarias
  3. Listado de sinónimos de Convolvulus arvensis.[1].
  4. a b «Convolvulus arvensis». Real Jardín Botánico: Proyecto Anthos. Consultado el 27 de noviembre de 2009.
  5. Convolvulus arvensis en The Plant List
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Convolvulus arvensis: Brief Summary ( Espanhol; Castelhano )

fornecido por wikipedia ES

Convolvulus arvensis L. (correhuela o cahiruela) es una especie de planta trepadora del género Convolvulus, familia Convolvulaceae, nativa de Europa y Asia.

 src= Vista de la planta  src= Hojas
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Kassitapp ( Estônio )

fornecido por wikipedia ET
Disambig gray.svg See artikkel räägib liigist; perekonna kohta vaata artiklit Kassitapp (perekond)

Harilik kassitapp (Convolvulus arvensis) on kassitapuliste sugukonda kuuluv mitmeaastane rohttaim.

Levik ja kasvukoht

Kassitapp kasvab pärismaisena Euroopas ja Aasias. Eestis on ta tavaline.

Taim eelistab kuivemat savikat või liivast pinnast. Ta on levinud umbrohi aedades ja põldudel.

Kirjeldus

 src=
Õis
 src=
Kuprad koos seemnetega

Taim kasvab 0,5–1,5 meetri kõrguseks. Ta on väänduva roomava või roniva varrega taim.

Lehed kinnituvad varrele vaheldumisi. 2–6 cm pikkused lihtlehed on terveservalised.

Taime juured ulatuvad väga sügavale ja moodustavad harunenud võrgustiku. Juba esimese paari elukuuga suudab juurestik tungida kuni meetri sügavuseni, soodsatel tingimustel võib kasvada see kolme ja isegi viie meetri sügavusele.

Kassitapp õitseb juunist septembrini. Õis on lehterja kujuga, valge kuni õrnroosa, kuni 3,5 cm läbimõõduga. Taim on putuktolmleja.

Vili on umbes 6 mm pikkune kupar.

Taim paljuneb peamiselt maa-aluste võsundite abil, vähem seemnetega.

Vaata ka

Välislingid

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Kassitapp: Brief Summary ( Estônio )

fornecido por wikipedia ET

Harilik kassitapp (Convolvulus arvensis) on kassitapuliste sugukonda kuuluv mitmeaastane rohttaim.

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Ezkerte beltz ( Basco )

fornecido por wikipedia EU

Ezkerte beltza edo biurda (Convolvulus arvensis) Europa eta Asiako espezie igokari eta herrestaria da jatorriz. Askotan belar txartzat hartzen da, erraz eta erruz zabaldu egiten delako. Beste landareen gainera igo eta ito egiten ditu. Horretaz gain, errizoma luze batetik sustraiak nonahi botatzen dituenez eremu zabalak hartzen ditu aise eta oso zaila izaten da erauztea.

 src=
Lorea
 src=
Convolvulus arvensis

Deskripzioa

Ezkerte beltza landare belarkara eta bizikorra da, 0,5-2 m arteko luze. Hosto bakunak ditu, espiralean jarrita daudenak. Hauek peziolatuak dira, gezi-formakoak nahiz triangeluarrak, osoak edo ia osoak, 2-5 cm luze, 1-3 cm-ko txorten batekin.

Uda betean loratzen da eta ematen dituen loreak turuta-formakoak dira, oso erregularrak, 1 eta 2,5 cm arteko diametrokoak, arrosa argiak edo zuriak, ilunagoak diren bost marra erradialekin. Fruitu marroi argiak ematen ditu, biribilduak, ilegabeak, bina hazi dituztenak. Hegaztiek jaten dituzte eta urtetan ernagarri iraun ahal dute lurrean.

Errizoma herrestaria; zurtoinak, berriz, birakariak, 2 m-ko garaiera har dezaketena.


Herrialde-azpiespezie.

  • Convolvulus arvensis var. arvensis. Hosto zabalak.
  • Convolvulus arvensis var. linearifolius. Hosto estuagoak.

Ekologia

Lore ederrak ematen baditu ere, sastraka kaltegarria izaten da sarritan lorategi eta baratzetan, azkar hazi eta beste landareei kiribiltzen zaielako hauei gaina hartu arte. Horrela, argia, ura eta nutrienteak lortzeko lehian, landatutako landareak eta bestelako landareria ahuldu eta galtzen ditu. Ipar Amerikan, esate baterako, 1739an jada sartua zen laborantzarako landareen haziekin nahasturik eta egun espezie inbaditzailetzat jotzen da.

Kontrola eta kudeaketa

Ezkerte beltza zaila izaten da erauztea, haziek 20 urte ere ernagarri iraun dezakete lurrean eta landare batek 500 hazi eman ditzake. Sustrai sakonek karbohidratoak eta proteinak metatzen dituzte eta horrek behin eta berriro ernatzea ahalbidetzen du pujak erauzi ondoren. Tapiz trinkoak eratzen ditu eta hauek laborantza-alorrak hartzen dituzte laborantzaren etekinak murriztuz. Esate baterako, 1998an Estatu Batuetan landare honek uztaroan eragin zituen galerak 377 miloi dolar baino gehiago balioztatu zituzten. Sortu ere arazo handiak sortzen ditu ibai-ertzak lehenengoratzen egiten diren saioetan, landare lastodunak eta ihidiak itotzen dituelako eta ondorioz, habitat bateko biodibertsitatea murrizten du.

Habitata

Bide bazterrak, soroak, larreak eta lur mugituak.

Toxikotasuna

Zertxobait toxiko da abereentzat.


Beste izen batzuk

Ziurda, txildurka, biurda, belarlatz, sapabelarra, kanpantxila-belar, kanpantxilar, pipila, lurruntza, lurruntze txiki,txurrutx, txurrusta-belar, lehuntz, pipalore, amabirgin atorra, birunga, hedetxo, kentidonia, odolbelar,

(RLQ=window.RLQ||[]).push(function(){mw.log.warn("Gadget "ErrefAurrebista" was not loaded. Please migrate it to use ResourceLoader. See u003Chttps://eu.wikipedia.org/wiki/Berezi:Gadgetaku003E.");});
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Ezkerte beltz: Brief Summary ( Basco )

fornecido por wikipedia EU

Ezkerte beltza edo biurda (Convolvulus arvensis) Europa eta Asiako espezie igokari eta herrestaria da jatorriz. Askotan belar txartzat hartzen da, erraz eta erruz zabaldu egiten delako. Beste landareen gainera igo eta ito egiten ditu. Horretaz gain, errizoma luze batetik sustraiak nonahi botatzen dituenez eremu zabalak hartzen ditu aise eta oso zaila izaten da erauztea.

 src= Lorea  src= Convolvulus arvensis
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Peltokierto ( Finlandês )

fornecido por wikipedia FI

Peltokierto (Convolvulus arvensis) on kiertokasvien heimoon kuuluva ruohokasvi, jota tavataan yleisesti Euraasiassa ja Pohjois-Amerikassa. Puutarhoissa ja viljelyksillä laji on erittäin hankalasti torjuttava rikkaruoho.

Ulkonäkö ja koko

Convolvulus arvensis5 ies.jpg
 src=
Convolvulus arvensis

Monivuotinen peltokierto kasvattaa 30–80 cm pitkän, köynneliään ja rennon varren. Kasvi on tavallisesti kalju. Lehdet sijaitsevat varressa kierteisesti ja ovat ruodillisia, pitkulaisia tai joskus kapeita, keihästyvisiä ja ehytlaitaisia. Valkoiset tai vaaleanpunaiset kukat ovat lehtihangoissa yksittäin tai kolmittain. Kukan teriöt ovat noin kaksi senttiä leveitä ja suppilomaisia. Kukkien pienet ja kapeat esilehdet ovat kukkaperän puolivälissä. Suomessa peltokierto kukkii heinä–elokuussa.[1]

Peltokierto kasvattaa hyvin laajan ja usean metrin syvyydelle ulottuvan juurakon. Se leviää helposti pienistäkin juurenkappaleista, mikä tekee siitä erittäin vaikeasti torjuttavan rikkaruohon.[2][3]

Levinneisyys

Peltokiertoa tavataan koko Euroopassa lukuun ottamatta Islantia ja mantereen pohjoisosia. Yhtenäinen levinnäisyysalue ulottuu Pohjois-Afrikasta läpi Euroopan Keski-Aasiaan ja Etelä-Siperiaan saakka. Ihmisen mukana laji on levinnyt laajalle Pohjois-Amerikkaan sekä mm. Australiaan ja Uuteen-Seelantiin.[2] Suomessa peltokierto on levinneisyytensä pohjoisrajoilla. Lajia tavataan satunnaisesti lähinnä asutuskeskuksissa Oulun korkeudelle saakka.[4] Suomessa peltokierto on tulokaslaji, joka on levinnyt maahan mm. satamien painolastimaiden tai Venäjältä tuodun viljan ja rehun mukana.[3][5]

Elinympäristö

Peltokierto on kulttuuriympäristön kasvi, jota tavataan pihoilla, puutarhoissa, kaupungeissa, tien- ja radanvarsilla, satamissa, joutomailla sekä vanhoilla kasarmi- ja linnoituspaikoilla.[1] Kasvi tukeutuu mielellään tiukalla kierteellä muihin kasveihin. Tuen puuttuessa se kasvaa maan pintaa myöten.[3]

Lähteet

  • Oulun kasvit. Piimäperältä Pilpasuolle. Toim. Kalleinen, Lassi & Ulvinen, Tauno & Vilpa, Erkki & Väre, Henry. Luonnontieteellinen keskusmuseo, Kasvimuseo, Norrlinia 11 / Oulun kaupunki, Oulun seudun ympäristövirasto, julkaisu 2/2005. Yliopistopaino, Helsinki 2005.
  • Retkeilykasvio. Toim. Hämet-Ahti, Leena & Suominen, Juha & Ulvinen, Tauno & Uotila, Pertti. Luonnontieteellinen keskusmuseo, Kasvimuseo, Helsinki 1998.

Viitteet

  1. a b Retkeilykasvio 1998, s. 345.
  2. a b Den virtuella floran: Åkervinda (ruots.) Viitattu 24.2.2010.
  3. a b c Peltokierto LuontoPortti. LuontoPortti. Viitattu 23.2.2010.
  4. Lampinen, R. & Lahti, T. 2009: Kasviatlas 2008. Helsingin Yliopisto, Luonnontieteellinen keskusmuseo, Kasvimuseo, Helsinki. Kasviatlas 2008: Peltokierron levinneisyys Suomessa Viitattu 24.2.2010.
  5. Oulun kasvit 2005, 446.

Aiheesta muualla

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Peltokierto: Brief Summary ( Finlandês )

fornecido por wikipedia FI

Peltokierto (Convolvulus arvensis) on kiertokasvien heimoon kuuluva ruohokasvi, jota tavataan yleisesti Euraasiassa ja Pohjois-Amerikassa. Puutarhoissa ja viljelyksillä laji on erittäin hankalasti torjuttava rikkaruoho.

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wikipedia FI

Liseron des champs ( Francês )

fornecido por wikipedia FR

Convolvulus arvensis

Le Liseron des champs (Convolvulus arvensis) est une plante herbacée vivace de la famille des Convolvulacées.

Historique et dénomination

L'espèce Convolvulus arvensis a été décrite par le naturaliste suédois Carl von Linné en 1753[4].

Le Liseron des champs est vulgairement dénommé Petit liset, Campanette, vrillée, clochette champêtre, robe de la Vierge[5].

Synonymie

Il existe pour cette espèce de très nombreux synonymes [6]:

  • Convolvulus ambigens House
  • Convolvulus arvensis f. purpurascens T.Tacik
  • Convolvulus arvensis f. rehmanii T.Tacik
  • Convolvulus arvensis subsp. crispatus Franco
  • Convolvulus arvensis var. angustatus Ledebour
  • Convolvulus arvensis var. crassifolius Choisy
  • Convolvulus arvensis var. hastulatus Meisn.
  • Convolvulus arvensis var. linearifolius Choisy
  • Convolvulus arvensis var. obtusifolius Choisy
  • Convolvulus arvensis var. parvifolius Choisy
  • Convolvulus arvensis var. prostratus Rouy
  • Convolvulus arvensis var. pumilus Choisy
  • Convolvulus arvensis var. sagittatus Ledebour
  • Convolvulus arvensis var. sagittifolius Fisch.
  • Convolvulus arvensis var. sagittifolius Turczaninow (nom. illeg.)
  • Convolvulus arvensis var. villosus Choisy
  • Convolvulus auriculatus Desr.
  • Convolvulus cherleri Agardh ex Roem. & Schult.
  • Convolvulus chinensis Ker Gawler
  • Convolvulus corsicus Roem. & Schult.
  • Convolvulus fischerianus Petrov
  • Convolvulus longipedicellatus Sa'ad
  • Convolvulus minor Bubani nom. illeg.
  • Convolvulus prostratus F.W.Schmidt (nom. illeg.)
  • Convolvulus sagittifolius (Fisch.) T.Liou & Ling (nom. illeg.)
  • Convolvulus sagittifolius Fisch. ex Choisy (nom. illeg.)
  • Convolvulus sagittifolius Salisbury (nom. illeg.)
  • Lizeron arvensis (L.) Rafinesque
  • Lizeron chinensis (Ker Gawl.) Rafinesque
  • Strophocaulos arvensis (L.) Small, 1933

Description

C'est une plante vivace rampante ou grimpante, atteignant 2 mètres au maximum. Les feuilles sont alternes, oblongues, pétiolées et sagittées. Les fleurs sont solitaires, éphémères (elles ne sont ouvertes souvent qu'une journée), blanches ou roses rayées de blanc, et faiblement parfumées. Les fruits sont des capsules arrondies. On trouve le liseron des champs en terrains cultivés ou vagues, dans les gazons tondus à ras et au bord des chemins et des routes[7].

C'est une adventice qui peut entrer en compétition pour la lumière avec les plantes qu'elle prend pour support. Elle se propage rapidement par voie aérienne via la dissémination de ses graines par les oiseaux.[réf. souhaitée]

Elle est cependant utilisée en jardinage écologique pour attirer les syrphes et limiter ainsi les populations de pucerons.[réf. souhaitée] Les liserons sont par leur racine un des moyens de maintenir les bonnes mycorhizes dans les parcelles potagères pendant l'hiver, le labour et le sol nu stérilisant le lieu.

Propriétés

En herboristerie, le Liseron des champs est utilisé pour ses propriétés laxatives et purgatives énergiques de sa racine récoltée pendant les mois de juillet et d'août. On prépare à cet effet un sirop purgatif[8]. Ses feuilles infusées ont les mêmes propriétés laxatives[9].

Caractéristiques

Organes reproducteurs

Graine

Habitat et répartition

  • Habitat type : friches vivaces rudérales pionnières, mésoxérophiles, médioeuropéennes, psychrophiles
  • Aire de répartition : cosmopolite

Liste des variétés

Selon Tropicos (12 septembre 2020)[10] (Attention liste brute contenant possiblement des synonymes) :

  • variété Convolvulus arvensis var. angustatus Ledeb.
  • variété Convolvulus arvensis var. crassifolius Choisy
  • variété Convolvulus arvensis var. hastulatus Meisn.
  • variété Convolvulus arvensis var. linearifolius Choisy
  • variété Convolvulus arvensis var. sagittaefolius Turcz.
  • variété Convolvulus arvensis var. sagittatus Ledeb.
  • variété Convolvulus arvensis var. sagittifolius Turcz.
  • variété Convolvulus arvensis var. villosus Choisy

Notes et références

  1. IPNI. International Plant Names Index. Published on the Internet http://www.ipni.org, The Royal Botanic Gardens, Kew, Harvard University Herbaria & Libraries and Australian National Botanic Gardens., consulté le 12 septembre 2020
  2. a b c d e f g h i et j BioLib, consulté le 12 septembre 2020
  3. a et b The Plant List (2013). Version 1.1. Published on the Internet; http://www.theplantlist.org/, consulté le 12 septembre 2020
  4. Linnaeus, C. (1753) Species Plantarum, Tomus I: 153.
  5. A. Fleury de la Roche, Les plantes bienfaisantes, page 210 (article : liseron), éditions Gautier-Languereau, Paris, 1937
  6. USDA, ARS, National Genetic Resources Program. Convolvulus arvensis in the Germplasm Resources Information Network (GRIN), US Department of Agriculture Agricultural Research Service. Accessed on 09-Oct-10.
  7. Marjorie Blamey et Christopher Grey-Wilson, La flore d'Europe occidentale, Flammarion, 2003, 544 p. (ISBN 978-2-08-200995-9)
  8. A. Fleury de la Roche, Les plantes bienfaisantes, page 211 (article : liseron), éditions Gautier-Languereau, Paris, 1937
  9. A. Fleury de la Roche indique la dose de 12 à 15 g de feuilles de liseron contuses infusées pendant une demi-heure dans 500 g d'eau ou de lait frais pour la préparation de cette potion laxative. Il en indique également l'usage sous forme de poudre de feuilles administrée avec du miel.
  10. Tropicos.org. Missouri Botanical Garden., consulté le 12 septembre 2020

Références biologiques

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wikipedia FR

Liseron des champs: Brief Summary ( Francês )

fornecido por wikipedia FR

Convolvulus arvensis

Le Liseron des champs (Convolvulus arvensis) est une plante herbacée vivace de la famille des Convolvulacées.

licença
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Auteurs et éditeurs de Wikipedia
original
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Convolvulus arvensis ( Irlandês )

fornecido por wikipedia GA

Is speiceas de phlanda dreaptha nó reatha é Convolvulus arvensis (an ainleog ), den ghéineas Convolvulus, a bhaineann leis an bhfine Convolvulaceas,[1] agus ar speicis dhúchasacha iad san Eoraip agus san Áise. Is plandaí luibheach ilbhliantúil é, a fhásann go 0.5-2 m ar airde.

Tá dhá chineál ann:

  • Convolvulus arvensis var. arvensis. Duilleoga níos leithne
  • Convolvulus arvensis var. linearifolius. Duilleoga níos cúinge

Tagairtí

  1. Parnell, J. and Curtis, T. 2012. Webb's An Irish Flora. Cork University Press. ISBN 978-185918-4783
 src=
Is síol é an t-alt seo. Cuir leis, chun cuidiú leis an Vicipéid.
Má tá alt níos forbartha le fáil i dteanga eile, is féidir leat aistriúchán Gaeilge a dhéanamh.


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Convolvulus arvensis: Brief Summary ( Irlandês )

fornecido por wikipedia GA

Is speiceas de phlanda dreaptha nó reatha é Convolvulus arvensis (an ainleog ), den ghéineas Convolvulus, a bhaineann leis an bhfine Convolvulaceas, agus ar speicis dhúchasacha iad san Eoraip agus san Áise. Is plandaí luibheach ilbhliantúil é, a fhásann go 0.5-2 m ar airde.

Tá dhá chineál ann:

Convolvulus arvensis var. arvensis. Duilleoga níos leithne Convolvulus arvensis var. linearifolius. Duilleoga níos cúinge
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Poljski slak ( Croato )

fornecido por wikipedia hr Croatian

Poljski slak (lat.Convolvulus arvensis) je biljka iz porodice Convolvulaceae. Raste diljem Europe kao vrlo čest korov. Biljka je otrovna a korištena je u narodnoj medicini.

Sastav

Listovi sadrže do 143 mg% askorbinske kiseline i do 7,9 mg% karotina. Svi dijelovi, a naročito korijen sadrže glikozid konvolvulin.Sjemenke sadrže alkaloide.[1]

Dodatna literatura

že alkaloideŠreter,A.I. Lekarstvenaja flora sovetskogo dalnego vostoka,Moskva 1975.

Uporaba u narodnoj medicini

Koristi se kao holagog; Diuretik; Laksativ; Purgativ; kod ugriza insekata; za ženske probleme.U ruskoj,arapskoj,indijskoj i tibetanskoj narodnoj medicini koristi se za liječenje tuberkuloze,bronhitisa,sifilisa,ateroskleroze.Prašak korijena za nesanicu,mast od korijena kao lokalni anestetik.[2]

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Poljski slak: Brief Summary ( Croato )

fornecido por wikipedia hr Croatian

Poljski slak (lat.Convolvulus arvensis) je biljka iz porodice Convolvulaceae. Raste diljem Europe kao vrlo čest korov. Biljka je otrovna a korištena je u narodnoj medicini.

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Rólna wijawka ( Sorábio superior )

fornecido por wikipedia HSB

Rólna wijawka[1][3] (Convolvulus arvensis) je rostlina ze swójby wijawkowych rostlinow (Convolvulaceae). Dalšej serbskej ludowej mjenje stej sedłač[1][4][3] a sobołk[1][5].

Wopis

 src=
Běłe kćenje z čerwjenymi blečkami
 src=
Kapslowy płód a symjenja.

Rólna wijawka je trajne zelo, kotrež docpěje wysokosć wot 20 hač do 80 cm.

Stołpiki su ćeńke a deleka ležace, lězuce abo nalěwo wijace.

Łopjena

Łopjena su wutrobojte hač šipojte a 3 hač 6 raz tak dołhe kaž šěroke. Wone docpěja dołhosć wot 3 hač do 4 cm.

Kćenja

Kćěje wot junija hač do septembra. Kćenja su likojte, běłe abo róžojte a docpěja dołhosć wot 1,5 hač do 2,5 cm. Wone sedźa na dołhich stołpikach w łopjenowych rozporach.

Stejnišćo

Rosće na rolach, winicach, w zahrodach, na smjećowych městnach, pućnych kromach a pustych płoninach. Ma radšo małohumozne pódy.

Rozšěrjenje

Rostlina je w Europje rozšěrjena.

Wužiwanje

Nóžki

  1. 1,0 1,1 1,2 1,3 1,4 Pawoł Völkel: Prawopisny słownik hornjoserbskeje rěče. Hornjoserbsko-němski słownik. Ludowe nakładnistwo Domowina, Budyšin 2005, ISBN 3-7420-1920-1, str. 540.
  2. W internetowym słowniku: Winde
  3. 3,0 3,1 3,2 W internetowym słowniku: Ackerwinde
  4. Pawoł Völkel: Prawopisny słownik hornjoserbskeje rěče. Hornjoserbsko-němski słownik. Ludowe nakładnistwo Domowina, Budyšin 2005, ISBN 3-7420-1920-1, str. 451.
  5. Pawoł Völkel: Prawopisny słownik hornjoserbskeje rěče. Hornjoserbsko-němski słownik. Ludowe nakładnistwo Domowina, Budyšin 2005, ISBN 3-7420-1920-1, str. 468.

Žórła

  • Schauer - Caspari: Pflanzenführer für unterwegs, ISBN 978-3-8354-0354-3, 2. nakład, 2008, strona 220 (němsce)
  • Spohn, Aichele, Golte-Bechtle, Spohn: Was blüht denn da? Kosmos Naturführer (2008), ISBN 978-3-440-11379-0, strona 54 (němsce)
  • Brankačk, Jurij: Wobrazowy słownik hornjoserbskich rostlinskich mjenow na CD ROM. Rěčny centrum WITAJ, wudaće za serbske šule. Budyšin 2005.
  • Kubát, K. (Hlavní editor): Klíč ke květeně České republiky. Academia, Praha (2002)
  • Lajnert, Jan: Rostlinske mjena. Serbske. Němske. Łaćanske. Rjadowane po přirodnym systemje. Volk und Wissen Volkseigener Verlag Berlin (1954)
  • Rězak, Filip: Němsko-serbski wšowědny słownik hornjołužiskeje rěče. Donnerhak, Budyšin (1920)

Eksterne wotkazy

Commons
Hlej wotpowědne dataje we Wikimedia Commons:
Rólna wijawka
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Rólna wijawka: Brief Summary ( Sorábio superior )

fornecido por wikipedia HSB

Rólna wijawka (Convolvulus arvensis) je rostlina ze swójby wijawkowych rostlinow (Convolvulaceae). Dalšej serbskej ludowej mjenje stej sedłač a sobołk.

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Convolvulus arvensis ( Italiano )

fornecido por wikipedia IT

Il convolvolo o vilucchio (Convolvulus arvensis Linnaeus, 1753 ) è una Convolvulacea originaria dell'Europa e dell'Asia, molto comune in tutta Italia, dalla pianura alla media montagna.

La forma biologica è G rhiz - Geofite rizomatose, cioè piante con un rizoma sotterraneo che ogni anno emette radici e fusti.

È una nota infestante del mais.

Descrizione

È una pianta erbacea perenne, rampicante o strisciante, che raggiunge a maturità una lunghezza di 0,5–2 m. Possiede un rizoma biancastro e fusti erbacei generalmente avvolti verso sinistra. Ha foglie spiralate, da lineari a cuoriformi, lunghe 2–5 cm, larghe 2–3 cm e con picciolo di 1–3 cm. I fiori, portati all'ascella delle foglie mediane, hanno calice e corolla entrambi campanulati: il calice, erbaceo, di 4–5 mm, la corolla da 1 a 2,5 cm di diametro, di colore bianco o rosa pallido, con cinque strisce radiali di un rosa leggermente più scuro. Il fiore ha antere violacee e stimma bianco con due lobi divergenti. Fiorisce da aprile a ottobre. Il frutto è una capsula sferica glabra.

 src=
Fiore infestato da acari
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Convolvulus arvensis, capsule e semi.

Varietà

È presente in due varietà:

  • Convolvulus arvensis var. arvensis, a foglie larghe;
  • Convolvulus arvensis var. linearifolius, a foglie lineari.

Altre notizie

Nonostante produca fiori attraenti e pur costituendo un ottimo foraggio per conigli[1], è spesso considerato una sgradita pianta infestante nei giardini e negli orti a causa della sua rapida crescita e del conseguente soffocamento delle piante coltivate.

In una delle leggende raccolte dai Fratelli Grimm, La tazzetta della Madonna, e attestata anche in paesi come la Toscana[2], questo fiore venne usato dalla Madonna per bere vino quando aiutò a liberare il carretto di un carrettiere. La leggenda narra che "il piccolo fiore viene ancora chiamato Tazzetta della Madonna".

È pianta visitata dalle api per il suo nettare.[3]

Note

  1. ^ vilùcchio, in Treccani.it – Vocabolario Treccani on line, Istituto dell'Enciclopedia Italiana.
  2. ^ C. Lapucci, La Bibbia dei poveri. Storia popolare del mondo, Firenze, Sarnus, 2013, p. 38 (versione da Siena)
  3. ^ (FR) Convolvulus arvensis & Apis mellifera, su Florabeilles, 25 novembre 2012. URL consultato il 4 luglio 2019.

Bibliografia

 title=
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Convolvulus arvensis: Brief Summary ( Italiano )

fornecido por wikipedia IT

Il convolvolo o vilucchio (Convolvulus arvensis Linnaeus, 1753 ) è una Convolvulacea originaria dell'Europa e dell'Asia, molto comune in tutta Italia, dalla pianura alla media montagna.

La forma biologica è G rhiz - Geofite rizomatose, cioè piante con un rizoma sotterraneo che ogni anno emette radici e fusti.

È una nota infestante del mais.

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Autori e redattori di Wikipedia
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wikipedia IT

Dirvinis vijoklis ( Lituano )

fornecido por wikipedia LT

Dirvinis vijoklis (lot. Convolvulus arvensis) – vijoklinių (Convolvulaceae) šeimos augalas, paplitęs Eurazijoje.

Augalas žolinis, vijoklinis, daugiametis. Stiebas šešiabriaunis, užaugantis iki 170 cm, vyniojasi ant kitų augalų, stulpų arba driekiasi pažeme. Lapai lancetiški arba linijiškai pailgi, su strėlišku, ietišku arba širdišku pagrindu, 2–5 cm ilgio. Žiedai piltuviškai varpiški, kvapnūs, balti arba rausvi, 1,9–2,5 cm skersmens. Vaisius rudas, apvalus, 0,3 cm skersmens, su 2 sėklomis. Šaknys baltos, virvelinės.

Dirvinis vijoklis – sunkiai išnaikinama piktžolė. Auga laukuose, daržuose, dykvietėse, soduose, ant pylimų. Nors avys, galvijai augalą ėda, didesni jo kiekiai kenksmingi (ypač arkliams)[1]. Šiaurės Amerikoje – invazinė rūšis.

Šaltiniai

  1. Vijoklis. Tarybų Lietuvos enciklopedija, T. 4 (Simno-Žvorūnė). – Vilnius: Vyriausioji enciklopedijų redakcija, 1988. 515 psl.
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Dirvinis vijoklis: Brief Summary ( Lituano )

fornecido por wikipedia LT

Dirvinis vijoklis (lot. Convolvulus arvensis) – vijoklinių (Convolvulaceae) šeimos augalas, paplitęs Eurazijoje.

Augalas žolinis, vijoklinis, daugiametis. Stiebas šešiabriaunis, užaugantis iki 170 cm, vyniojasi ant kitų augalų, stulpų arba driekiasi pažeme. Lapai lancetiški arba linijiškai pailgi, su strėlišku, ietišku arba širdišku pagrindu, 2–5 cm ilgio. Žiedai piltuviškai varpiški, kvapnūs, balti arba rausvi, 1,9–2,5 cm skersmens. Vaisius rudas, apvalus, 0,3 cm skersmens, su 2 sėklomis. Šaknys baltos, virvelinės.

Dirvinis vijoklis – sunkiai išnaikinama piktžolė. Auga laukuose, daržuose, dykvietėse, soduose, ant pylimų. Nors avys, galvijai augalą ėda, didesni jo kiekiai kenksmingi (ypač arkliams). Šiaurės Amerikoje – invazinė rūšis.

 src=

Požymiai

 src=

Margi žiedai

 src=

Augimvietė

 src=

Vaisiai ir sėklos.

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Akkerwinde ( Neerlandês; Flamengo )

fornecido por wikipedia NL

De akkerwinde (Convolvulus arvensis) is een plant uit de windefamilie (Convolvulaceae). Hij komt voor op grazige plekken, bouwland, langs wegen en in de duinen. De stengels winden zich tegen de wijzers van de klok in om dingen heen.

De bloem is geheel roze of wit, of met meer of minder duidelijke roze of witte strepen, en heeft aan de buitenkant soms donkerder strepen. De bloemen hebben een doorsnede van 1,5 tot 3 cm. Er zijn vijf kelkbladen met ronde tanden. De bloemen hebben een aangename geur. Eén tot drie bloemen bloeien aan een lange steel met halverwege twee schutblaadjes. De bloeitijd is van juni tot de herfst.

De akkerwinde heeft een onbehaarde doosvrucht.

De bladeren zijn eirond tot langwerpig en hebben uitstaande slippen aan de voet.

Externe links

Wikibooks Wikibooks heeft meer over dit onderwerp: Ecologisch tuinieren - Akkerwinde.
Wikimedia Commons Mediabestanden die bij dit onderwerp horen, zijn te vinden op de pagina Convolvulus arvensis op Wikimedia Commons.
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Akkerwinde: Brief Summary ( Neerlandês; Flamengo )

fornecido por wikipedia NL

De akkerwinde (Convolvulus arvensis) is een plant uit de windefamilie (Convolvulaceae). Hij komt voor op grazige plekken, bouwland, langs wegen en in de duinen. De stengels winden zich tegen de wijzers van de klok in om dingen heen.

De bloem is geheel roze of wit, of met meer of minder duidelijke roze of witte strepen, en heeft aan de buitenkant soms donkerder strepen. De bloemen hebben een doorsnede van 1,5 tot 3 cm. Er zijn vijf kelkbladen met ronde tanden. De bloemen hebben een aangename geur. Eén tot drie bloemen bloeien aan een lange steel met halverwege twee schutblaadjes. De bloeitijd is van juni tot de herfst.

De akkerwinde heeft een onbehaarde doosvrucht.

De bladeren zijn eirond tot langwerpig en hebben uitstaande slippen aan de voet.

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Powój polny ( Polonês )

fornecido por wikipedia POL

Powój polny (Convolvulus arvensis L.) – gatunek byliny należący do rodziny powojowatych.

Zasięg występowania

Występuje na półkuli północnej, głównie w strefie klimatu umiarkowanego, ale czasami także ciepłego. Jest pospolity w prawie całej Europie, występuje w Afryce Północnej, na obszarach Azji o klimacie umiarkowanym, a częściowo również ciepłym (Nepal, Pakistan). Rozprzestrzenia się gdzieniegdzie także poza tymi obszarami występowania[3]. W Polsce jest pospolity na niżu i pogórzu[4]. Status gatunku we florze Polski: gatunek rodzimy[5].

Morfologia

Pokrój
Wytwarza długie, cienkie i elastyczne pędy. Jest rośliną płożącą się po ziemi, jeśli jednak napotka na jakieś podpory zaczyna się po nich wspinać. Naziemna część owija się wokół innych roślin czy przedmiotów zawsze w lewo[6].
Korzenie
Tworzy silnie rozwinięty system korzeniowy. Korzenie główne wrastają w głąb ziemi na 2-4 m. Odrastające od nich poziomo, na dużej głębokości korzenie boczne w odległości 1-2 m od korzenia głównego ponownie pionowo wrastają w ziemię. Na korzeniach bocznych jesienią wyrastają pączki przybyszowe, a z nich roślina tworzy nowe odrosty[7].
Łodyga
Pełzająca lub wijąca się, długości 20-100 (wyjątkowo 200) cm[4]. Pod ziemią roślina posiada nitkowate i rozgałęzione kłącze o długości do 2 m[7].
Liście
Pojedyncze, na długich ogonkach, jajowate o strzałkowatej lub oszczepowatej nasadzie . Ulistnienie skrętoległe[7].
Kwiaty
Wyrastają na długich szypułkach z kątów liści. Mają lejkowatą koronę, w białoróżowe smugi, albo są całkiem białe lub całkiem różowe. Kielich o suchobłoniastym, brunatnym brzegu. W pewnej odległości od kwiatu występują dwa małe podkwiatki[7][8].
Owoc
Jajowata, zaostrzona dwukomorowa torebka zawierająca maksymalnie do 4 ciemnobrunatnych, kropkowanych nasion[7].
Gatunki podobne

Kielisznik zaroślowy (Calystegia sepium)

Biologia i ekologia

Rozwój
Hemikryptofit, czasami geofit. Kwitnie od maja do września[4]. Kwiaty otwierają się tylko przy słońcu i przekwitają po jednym dniu. Podczas kwitnienia wydzielają zapach migdałów. Zapylane są przez motyle, słupek i pręciki dojrzewają równocześnie. Roślina miododajna. Rozmnaża się przez nasiona oraz przez kłącze[8]. Jedna roślina wytwarza około 500 nasion[9]. Nasiona dojrzewają w glebie, kiełkują jednak dość słabo. Bez szkody znoszą przebywanie w układzie pokarmowym ptaków, które mogą je w ten sposób przenosić na duże odległości. Zachowują zdolność kiełkowania nawet przez 20 lat. Jednak w uprawach rolnych roślina rozmnaża się głównie wegetatywnie[6].
Siedlisko
Rośnie na polach, przydrożach, terenach ruderalnych, nasypach. Występuje zarówno na glebach gliniastych, jak i na piaskach[7]. W klasyfikacji zbiorowisk roślinnych gatunek charakterystyczny dla klasy Agropyretea, Ass. Convolvulo-Agropyretum[10].
Roślina trująca
Ziele i korzeń zawierają flawonoidy, kwas kawowy, żywice, garbniki i związki kumarynowe. Najsilniej trujące są nasiona[11].
Korelacje międzygatunkowe
Pasożytują na nim niektóre gatunki grzybów: Erysiphe convolvuli wywołujący mączniaka prawdziwego, Thecaphora seminis-convolvuli, Septoria convolvuli, Stagonospora calystegiae, Ramularia convolvuli, Fusicladium convolvularum, Thecaphora seminis-convolvuli. Żerują na nim wciornastki i niektóre gatunki chrząszczy[12].
 src=
Pęd
 src=
Kwiaty i liście
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Nasiona
 src=
Pąk i kwiat
 src=
Kwiaty

Znaczenie

W uprawach rolnych jest uporczywym chwastem. Dla uprawianych roślin stanowi duże zagrożenie. Może całkowicie zagłuszyć rośliny, a obciążając łodygi zbóż powoduje ich wyleganie[6][8]. Nie zuboża natomiast gleby w składniki pokarmowe, gdyż pozyskuje je z głębszych warstw gleby[7]. Występuje głównie w uprawach kukurydzy, zbóż, a sporadycznie także buraków[9].

Jest trudny do wytępienia. Nawet z bardzo małego fragmentu kłącza może wyrosnąć nowa roślina[8]. W uprawach rozmnaża się głównie przez kawałki kłącza, które są rozprzestrzeniane podczas mechanicznej uprawy gleby. Orka i inne zabiegi uprawowe tylko pobudzają go do tworzenia nowych rozłogów i wzrostu, nie niszczą go, gdyż rozłogi korzeniowe znajdują się głęboko, poza zasięgiem pługa. Mimo regularnego niszczenia odrostów roślina utrzymuje się przy życiu przez dwa lata, nim wyczerpie zgromadzone w korzeniach substancje zapasowe. W tym czasie może wytworzyć dziesiątki nowych odrostów. Jest trudny również do zwalczenia chemicznego, jest bowiem dość odporny na zawarte w herbicydach środki chemiczne. Najskuteczniejsze do chemicznego zwalczania są środki zawierające dikamb, fluroksypyr, florasulam lub tritosulfuron[6].

Filatelistyka

Poczta Polska wyemitowała 5 września 1967 r. znaczek pocztowy przedstawiający powój polny o nominale 60 gr, w serii Kwiaty polne. Autorem projektu znaczka był Tadeusz Michaluk. Znaczek pozostawał w obiegu do 31 grudnia 1994 r.. Powój polny pojawił się też na pierwszym znaczku tej serii o nominale 20 gr, w bukiecie kwiatów polnych[13].

Przypisy

  1. Stevens P.F.: Angiosperm Phylogeny Website (ang.). 2001–. [dostęp 2010-09-22].
  2. The Plant List. [dostęp 2015-08-23].
  3. Germplasm Resources Information Network (GRIN). [dostęp 2015-08-23].
  4. a b c Lucjan Rutkowski: Klucz do oznaczania roślin naczyniowych Polski Niżowej. Warszawa: Wydawnictwo Naukowe PWN, 1998, s. 373. ISBN 83-01-12218-8.
  5. Barbara Sudnik-Wójcikowska: Rośliny synantropijne. Warszawa: Multico, 2011. ISBN 978-83-7073-514-2. OCLC 948856513.
  6. a b c d Powój polny – opis, szkodliwość i skuteczne zwalczanie. [dostęp 2015-08-13].
  7. a b c d e f g František Činčura, Viera Feráková, Jozef Májovský, Ladislav Šomšák, Ján Záborský: Pospolite rośliny środkowej Europy. Jindřich Krejča, Magdaléna Záborská (ilustracje). Warszawa: Państwowe Wydawnictwo Rolnicze i Leśne, 1990. ISBN 83-09-01473-2.
  8. a b c d Olga Seidl, Józef Rostafiński: Przewodnik do oznaczania roślin. Warszawa: PWRiL, 1973.
  9. a b Horst Klaaßen, Joachim Freitag: Profesjonalny atlas chwastów. Limbergerhof, 2004.
  10. Władysław Matuszkiewicz: Przewodnik do oznaczania zbiorowisk roślinnych Polski. Warszawa: Wyd. Naukowe PWN, 2006. ISBN 83-01-14439-4.
  11. Jakub Mowszowicz: Przewodnik do oznaczania roślin trujących i szkodliwych. Warszawa: PWRiL, 1982. ISBN 83-200-2415-3.
  12. Malcolm Storey: Convolvulus arvensis L. (Field Bindweed). W: BioInfo (UK) [on-line]. [dostęp 2018-02-28].
  13. Marek Jedziniak: Kwiaty polne (pol.). www.kzp.pl. [dostęp 2018-05-31].
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Powój polny: Brief Summary ( Polonês )

fornecido por wikipedia POL

Powój polny (Convolvulus arvensis L.) – gatunek byliny należący do rodziny powojowatych.

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Convolvulus arvensis ( Português )

fornecido por wikipedia PT

Convolvulus arvensis é uma espécie de planta com flor pertencente à família Convolvulaceae.

A autoridade científica da espécie é L., tendo sido publicada em Species Plantarum 1: 153. 1753.[1]

Portugal

Trata-se de uma espécie presente no território português, nomeadamente em Portugal Continental, no Arquipélago dos Açores e no Arquipélago da Madeira.

Em termos de naturalidade é nativa de Portugal Continental e Arquipélago da Madeira e introduzida no arquipélago dos Açores.

Protecção

Não se encontra protegida por legislação portuguesa ou da Comunidade Europeia.

Referências

  1. Tropicos.org. Missouri Botanical Garden. 5 de Outubro de 2014 http://www.tropicos.org/Name/8500005>

Bibliografia

 title=
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Convolvulus arvensis: Brief Summary ( Português )

fornecido por wikipedia PT

Convolvulus arvensis é uma espécie de planta com flor pertencente à família Convolvulaceae.

A autoridade científica da espécie é L., tendo sido publicada em Species Plantarum 1: 153. 1753.

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Volbură ( Romeno; moldávio; moldavo )

fornecido por wikipedia RO

Volbura, sau rochița-rândunicii, (Convolvulus arvensis) este o specie de plante, nativă Europei și Asiei. Este o plantă perenă, erbacee, cățărătoare sau târâtoare, care poate crește până la 2 m. Frunzele sunt dispuse în spirală, de formă variată, lungi de 2–5 cm, cu un pețiol de 1–3 cm. Florile au formă de trompetă, cu diametrul de 1-2,5 cm, albe sau roz pal, cu cinci dungi radiale mai închise la culoare.

 src=
Floare cu acarieni roşii
 src=
Convolvulus arvensis

Există două varietăți:

  • Convolvulus arvensis var. arvensis - frunze late.
  • Convolvulus arvensis var. linearifolius - frunze înguste

Deși produce flori atractive, deseori este considerată a fi o buruiană din cauza creșterii rapide și sufocării plantelor cultivate. A fost introdusă în America de Nord, unde, pe alocuri, este o specie invazivă. Covoarele formate invadează culturile și scad recolta; se estimează că pierderile cauzate de această plantă în SUA depășesc 377 milioane de dolari doar în 1998e.[1]

Note

  1. ^ Coombs, E. M., et al., Eds. (2004). Biological Control of Invasive Plants in the United States. Corvallis: Oregon State University Press, 151.

Referințe

Bibliografie

  • Florentin Crăciun, Mircea Alexan, Carmen Alexan - Ghidul plantelor medicinale uzuale, Editura științifică, București 1992, pag. 88

Legături externe


v d m
Plante medicinale (Listă) Specii
AbiuAbrus precatoriusAglicăAcacia catechuAcacia senegalAcokanthera abyssinicaAconitum feroxAconitum napellusAfinAgrișAlbăstreaAloe veraAmăralaAnasonAnemone ranunculoidesAngelicăAnghinareArborele de cacaoArmurariuArnicaArnicăBambusBrad argintiuBrustureBrândușă de toamnăBusuiocCapereCartofCătină albăCerențelChimenChimionCicoareCimbrișor de câmpCiuboțica cuculuiCiulinCiumăfaieCoacăz roșuCoada-caluluiCoada șoriceluluiCoada raculuiCoriandruCrețișoarăCrețușcăCrușinCurcumaCânepă indianăCălinCătină de garduriDafinDracilăDumbravnicEfedraFecioricăFeniculFloarea patimilorGălbeneleGențianăGhimbirGhimpeGhințură (galbenă) • HameiHasmațuchiIarbă mareIederăIenupărInIpcărigeaIsopIzmă bunăJneapănLavandulaLemn dulceLiliacLimba cerbuluiLimba mieluluiLumânăricăMandragorăMăceșMaghiranMăselarițăMătrăgunăMerișorMurMușchi de piatrăMușețelMuștar albMuștar negruNalbă mareObligeanăOsul iepureluiPanseluțăPapayaPăpădiePătlaginăPătlăgeaua roșiePătrunjelPiper de baltăPirPlămânăricăPăducelPelinPodbalPopilnicPorumbarRăchitanRăcovinăRoibaRoinițăRostopascăRozmarinRoșcovRușcuță de primăvarăSalvieSăpunărițăScai vânătSchindufSchinelSoc (negru)SpilcuțăSunătoareSulfinăȘovârfTagetesTalpa gâștiiTătăneasăTeiTraista-ciobanuluiȚintaurăTrei-frați-pătațiTroscotTurița mareUngurașUrzicăUrzică moartă albăValerianăVentrilicăViolaViță de vieVolburăVâsc europeanZămoșiță
Floare de gălbenele

Wikipedia book Carte · Categorie Categorie · Portal Portal · WikiProject WikiProiect
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Volbură: Brief Summary ( Romeno; moldávio; moldavo )

fornecido por wikipedia RO

Volbura, sau rochița-rândunicii, (Convolvulus arvensis) este o specie de plante, nativă Europei și Asiei. Este o plantă perenă, erbacee, cățărătoare sau târâtoare, care poate crește până la 2 m. Frunzele sunt dispuse în spirală, de formă variată, lungi de 2–5 cm, cu un pețiol de 1–3 cm. Florile au formă de trompetă, cu diametrul de 1-2,5 cm, albe sau roz pal, cu cinci dungi radiale mai închise la culoare.

 src= Floare cu acarieni roşii  src= Convolvulus arvensis

Există două varietăți:

Convolvulus arvensis var. arvensis - frunze late. Convolvulus arvensis var. linearifolius - frunze înguste

Deși produce flori atractive, deseori este considerată a fi o buruiană din cauza creșterii rapide și sufocării plantelor cultivate. A fost introdusă în America de Nord, unde, pe alocuri, este o specie invazivă. Covoarele formate invadează culturile și scad recolta; se estimează că pierderile cauzate de această plantă în SUA depășesc 377 milioane de dolari doar în 1998e.

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Åkervinda ( Sueco )

fornecido por wikipedia SV

Åkervinda (Convolvulus arvensis) är en art inom familjen vindeväxter.

Utbredning

Arten förekommer i tempererade områden i Europa och Asien. I Sverige finns åkervindan upp till mellersta Norrland, men är i Norge och Finland begränsad till de sydliga landskapen.

Habitat

Ruderatmark, vägkanter, järnvägsbankar.

Beskrivning

 src=
Blomma med kvalster av släktet Trombidium.
 src=
Convolvulus arvensis

Åkervinda är en mångformig flerårig ört med mer eller mindre förvedade jordstammar.

Stjälkarna är krypande eller klättrande, upp till 150 cm långa, kala eller något håriga. I de klättrande formerna har stjälken blivit styv genom vridning. Tvärsnittet kan vara cirkulärt eller elliptiskt. (Se bild avsnitt Externa länkar.

Bladen är skaftade, avlånga till äggrunda 1,5…5 × 1…4 cm, kala eller håriga, bladbasen är pillik till hjärtlik.

Blommorna kommer i juli – augusti med 1…3 st placerade tillsammans i bladvecken. Kronan är vriden i knoppläget, vit eller rosa, brett trattlik 1,5…2,6 cm lång, brämet är grunt femflikigt. Ståndarna är fem till antalet, två långa, två korta och den femte av medellängd. Den praktiska vinsten olika längd på ståndarna är kanske att ståndarknapparna kan få mer plats än om de satt i jämnhöjd, och således lättare beröras av pollinatörerna.

Frukten är en 2-rummig kapsel, med 4 frön eller färre. Fröet har en tät, grå, hornartad, vid fuktning slemmig frövita där en grönfärgad grodd (embryo, växtanlag) ligger inbäddad. Nederst i fröanlaget är fröets rothål. Där innanför ligger groddens rot (rotanlaget eller "lillroten") och längre in i fröet de stora, veckade eller hopskrynklade hjärtbladen.

Arten har uppdelats i många underarter och varieteter. Vanligen erkänns inte dessa i moderna floror. Det finns även odlade former med blommor i många olika färgställningar.

Åkervindan hör till de svåra ogräsen och kan vara svår att få bort från oönskade platser. En orsak är att varje individ kan ge upp till 500 frön, och varje frö kan överleva i jorden upp till 20 år, innan det gror.[1]

Artepitetet arvensis (Lat.) betyder "tillhör åkern", men där är den invasiv.

Synonymer

  • Convolvulus ambigens House
  • Convolvulus arvensis f. purpurascens T.Tacik
  • Convolvulus arvensis f. rehmanii T.Tacik
  • Convolvulus arvensis subsp. crispatus Franco
  • Convolvulus arvensis var. angustatus Ledebour
  • Convolvulus arvensis var. crassifolius Choisy
  • Convolvulus arvensis var. hastulatus Meisn.
  • Convolvulus arvensis var. linearifolius Choisy
  • Convolvulus arvensis var. obtusifolius Choisy
  • Convolvulus arvensis var. parvifolius Choisy
  • Convolvulus arvensis var. prostratus Rouy
  • Convolvulus arvensis var. pumilus Choisy
  • Convolvulus arvensis var. sagittatus Ledebour
  • Convolvulus arvensis var. sagittifolius Fisch.
  • Convolvulus arvensis var. sagittifolius Turczaninow nom. illeg.
  • Convolvulus arvensis var. villosus Choisy
  • Convolvulus auriculatus Desr.
  • Convolvulus cherleri Agardh ex Roem. & Schult.
  • Convolvulus chinensis Ker Gawler
  • Convolvulus corsicus Roem. & Schult.
  • Convolvulus fischerianus Petrov
  • Convolvulus longipedicellatus Sa'ad
  • Convolvulus minor Bubani nom. illeg.
  • Convolvulus prostratus F.W.Schmidt nom. illeg.
  • Convolvulus sagittifolius (Fisch.) T.Liou & Ling nom. illeg.
  • Convolvulus sagittifolius Fisch. ex Choisy nom. illeg.
  • Convolvulus sagittifolius Salisbury nom. illeg.
  • Lizeron arvensis (L.) Rafinesque
  • Lizeron chinensis (Ker Gawl.) Rafinesque
  • Strophocaulos arvensis (L.) Small, 1933

Bygdemål

Namn Trakt Ref. Kommentar Bräudkallå Gotland [2] Kärringtarmar [3]

Källor

  1. ^ Convolvulus arvensis, åkervinda, på engelskspråkiga Wikipedia
  2. ^ Braudkallå: Johan Ernst Rietz: Svenskt dialektlexikon, sida 57, [1] Gleerups, Lund 1862–1867, faksimilutgåva Malmö 1962
  3. ^ Kärringtarmar: Johan Ernst Rietz: Svenskt dialektlexikon, sida 310, [2] Gleerups, Lund 1862–1867, faksimilutgåva Malmö 1962

Se även

Externa länkar

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Åkervinda: Brief Summary ( Sueco )

fornecido por wikipedia SV

Åkervinda (Convolvulus arvensis) är en art inom familjen vindeväxter.

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Берізка польова ( Ucraniano )

fornecido por wikipedia UK
 src=
Ботанічна ілюстрація з книги О. В. Томе «Flora von Deutschland, Österreich und der Schweiz», 1885
 src=
Convolvulus arvensis
 src=
Квітка берізки польової з оксамитовими кліщами (Trombidium sp.)

Опис

Стебла довжиною 1-1,5 м, численні, тонкі, в'юнкі, спірально скручені, обплітають сусідні рослини. Корінь стрижневий, розгалужений, йде в ґрунт на глибину до 2 м. Листки чергові, яйцеподібно-еліптичні або довгасті, розташовані на черешках. Квітки білі або рожеві, лійкоподібні, до 2-х см, з поздовжніми темними смужками, зі слабким приємним ароматом, розташовані в пазухах листя. Цвіте в квітні — жовтні. Квітки відкриваються залежно від часу доби і змін погоди. Плід — гладка коробочка яйцеподібної форми з дрібним насінням.

Рослина поширена від Білого моря до Середньої Азії. Росте вздовж доріг, на полях і в городах як бур'ян. Господарського значення не має.

Квітки рослини принаджують диких бджіл, жуків та метеликів, в тому числі бражника берізкового (Agrius convolvuli).

Використання

Берізка польова є лікарською сировиною — використовуються стебла і коріння, рідше квітки та насіння. Авіценна рекомендував її для лікування астми, захворювань легенів, печінки та селезінки. В експериментальних дослідженнях на тваринах доведено гіпотензивну, спазмолітичну, протизапальну, кровоспинну, місцево анестезуючу та подразнюючу слизові оболонки дію. Відвар трави приймають як проносний, діуретичний та ранозагоювальний засіб, а також для лікування гіпертонічної хвороби, бронхіальної астми і бронхітів (відвар квітів), безсоння (порошок кореня всередину) і як потогінний засіб (водний настій насіння).

В складі сіна рослина придатна для годування худоби.

Див. також

Література

Посилання

Примітки

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Берізка польова: Brief Summary ( Ucraniano )

fornecido por wikipedia UK
 src= Ботанічна ілюстрація з книги О. В. Томе «Flora von Deutschland, Österreich und der Schweiz», 1885  src= Convolvulus arvensis  src= Квітка берізки польової з оксамитовими кліщами (Trombidium sp.)
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Convolvulus arvensis ( Vietnamita )

fornecido por wikipedia VI

Convolvulus arvensis là một loài thực vật có hoa trong họ Bìm bìm. Loài này được L. mô tả khoa học đầu tiên năm 1753.[1]

Hình ảnh

Chú thích

  1. ^ The Plant List (2010). Convolvulus arvensis. Truy cập ngày 20 tháng 6 năm 2013.

Liên kết ngoài


Bài viết về chủ đề Họ Bìm bìm này vẫn còn sơ khai. Bạn có thể giúp Wikipedia bằng cách mở rộng nội dung để bài được hoàn chỉnh hơn.
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Convolvulus arvensis: Brief Summary ( Vietnamita )

fornecido por wikipedia VI

Convolvulus arvensis là một loài thực vật có hoa trong họ Bìm bìm. Loài này được L. mô tả khoa học đầu tiên năm 1753.

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Вьюнок полевой ( Russo )

fornecido por wikipedia русскую Википедию
 src=
Convolvulus arvensis

На окультуренных территориях является обычным сорняком.

Ботаническое описание

Голый, тонкий, вьющийся стебель в сечении гранёный, достигает в длину, иногда, более 1 м.
Листья снизу голые, узкие, копьевидные, у черешка имеют две острые лопасти, размещаются на стебле по спирали.

Цветки правильные воронковидные диаметром около 2 см, обоеполые, обычно с белым или розовым венчиком, разделённым на сегменты пятью радиальными полосами более тёмного цвета.

Формула цветка: ∗ K ( 5 ) C ( 5 ) A 5 G ( 2 _ ) {displaystyle ast K_{(5)};C_{(5)};A_{5};G_{({underline {2}})}} ast K_{(5)} ; C_{(5)} ; A_5 ; G_{(underline2)} [3]

Распространение

Широко распространён по европейской части России, на Кавказе, в Западной и Восточной Сибири, на Дальнем Востоке и в Средней Азии.

Применение

Применяется в народной медицине. Содержит психотропные алкалоиды, а в листьях присутствуют сердечные гликозиды.

В составе сена растение пригодно для кормления скота.

Цветки растения содержат нектар и пыльцу, которые привлекают диких пчёл, жуков и бабочек, например бабочку Бражник вьюнковый (Agrius convolvuli).

Вьюнок в культурах народов мира

Примечания

  1. Об условности указания класса двудольных в качестве вышестоящего таксона для описываемой в данной статье группы растений см. раздел «Системы APG» статьи «Двудольные».
  2. Flora Europaea
  3. Барабанов Е. И. Ботаника: учебник для студ. высш. учеб. заведений. — М.: Издат. центр «Академия», 2006. — С. 333. — 448 с. — ISBN 5-7695-2656-4.
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Вьюнок полевой: Brief Summary ( Russo )

fornecido por wikipedia русскую Википедию
 src= Convolvulus arvensis

На окультуренных территориях является обычным сорняком.

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田旋花 ( Chinês )

fornecido por wikipedia 中文维基百科

田旋花学名Convolvulus arvensis)是旋花科旋花属的一个物种,分布在欧洲亚洲

形态

Convolvulus arvensis.jpg
 src=
田旋花果实与种子标本

这是一种攀爬草本多年生植物,长达0.5-2米。叶子呈成螺旋形分布,形状为线状至箭形,2-5厘米长,叶柄长度为1-3厘米。呈喇叭形,直径为1-2.5厘米,白色或浅桃红色,有5条放射状深桃红色条纹。

分类

田旋花有两个变种

  • 田旋花(Convolvulus arvensis var. arvensis),叶子较宽。
  • 線葉田旋花(Convolvulus arvensis var. linearifolius),叶子较细。

入侵物种

尽管田旋花的花朵吸引人,但是却不受花圃欢迎。因为其生长得很快,侵占了其他栽培的植物。田旋花引入到北美洲后,在某些地方成为入侵物种。其浓密的植被侵占了农田,使农作物减产。1998年该物种使美国农作物损失达3.77亿美元。[2]

参考文献

  1. ^ Convolvulus arvensis L.. In: The Plant List (2013). Version 1.1. Published on the Internet; http://www.theplantlist.org/ [2018-11-20].
  2. ^ Coombs, E. M., et al., Eds. (2004). Biological Control of Invasive Plants in the United States. Corvallis: Oregon State University Press, 151.
 title=
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田旋花: Brief Summary ( Chinês )

fornecido por wikipedia 中文维基百科

田旋花(学名:Convolvulus arvensis)是旋花科旋花属的一个物种,分布在欧洲亚洲

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セイヨウヒルガオ ( Japonês )

fornecido por wikipedia 日本語
セイヨウヒルガオ Convolvulus arvensis.jpg 分類 : 植物界 Plantae : 被子植物門 Magnoliophyta : 双子葉植物綱 Magnoliopsida : ナス目 Solanales : ヒルガオ科 Convolvulaceae : セイヨウヒルガオ属 Convolvulus : セイヨウヒルガオ C. arvensis 学名 Convolvulus arvensis
L. 英名 field bindweed
 src=
Convolvulus arvensis

セイヨウヒルガオ (Convolvulus arvensis) は、ヨーロッパに生息するヒルガオ科つる植物。園芸植物としては、コンボルブルス・アルベンシスという学名で呼ばれることもある。

分布[編集]

ヨーロッパを原産地とする[1]

南北アメリカ、オセアニア、アジア、アフリカに移入分布する[2]

特徴[編集]

多年草。0.5-2mくらいに成長する。葉はらせん状につき、糸状もしくは矢じり形で、長さは2-5cm。葉柄は1-3cm。花はトランペット状で、直径1-2.5cm、色は白またはパールピンクで、5つの少し濃いピンクの放射状の帯がある。

以下の二つの亜種がある。

  • C. a. var. arvensis(葉が広い)
  • C. a. var. linearifolius(葉が狭い)

外来種問題[編集]

日本では観賞植物として導入されて、1940年代以降、全国に定着した[1]

きれいな花を咲かせるが、成長が早く、栽培している植物を覆ってしまうため、庭ではしばしば雑草として迷惑がられる。また、農作物にも悪影響を与える[2]

外来生物法により要注意外来生物に指定されている[1]

参考文献[編集]

  1. ^ a b c 多紀保彦(監修) 財団法人自然環境研究センター(編著) 『決定版 日本の外来生物』 平凡社ISBN 978-4-582-54241-7。
  2. ^ a b セイヨウヒルガオ 国立環境研究所 侵入生物DB

 

外部リンク[編集]


執筆の途中です この項目は、植物に関連した書きかけの項目です。この項目を加筆・訂正などしてくださる協力者を求めていますプロジェクト:植物Portal:植物)。
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ウィキペディアの著者と編集者
original
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wikipedia 日本語

セイヨウヒルガオ: Brief Summary ( Japonês )

fornecido por wikipedia 日本語
 src= Convolvulus arvensis

セイヨウヒルガオ (Convolvulus arvensis) は、ヨーロッパに生息するヒルガオ科つる植物。園芸植物としては、コンボルブルス・アルベンシスという学名で呼ばれることもある。

licença
cc-by-sa-3.0
direitos autorais
ウィキペディアの著者と編集者
original
visite a fonte
site do parceiro
wikipedia 日本語