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Lindernia crustacea
(Malaysian false pimpernel)

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Datasheet

Lindernia crustacea (Malaysian false pimpernel)

Summary

  • Last modified
  • 25 November 2019
  • Datasheet Type(s)
  • Invasive Species
  • Pest
  • Preferred Scientific Name
  • Lindernia crustacea
  • Preferred Common Name
  • Malaysian false pimpernel
  • Taxonomic Tree
  • Domain: Eukaryota
  •   Kingdom: Plantae
  •     Phylum: Spermatophyta
  •       Subphylum: Angiospermae
  •         Class: Dicotyledonae
  • Summary of Invasiveness
  • L. crustacea is an herb including in the Global Compendium of Weeds where it is listed as environmental and agricultural weed (

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Pictures

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PictureTitleCaptionCopyright
a, Flower; b, corolla, opened; c, pistil; d, capsule with calyx; e, seed.
TitleL. crustacea - line drawing
Captiona, Flower; b, corolla, opened; c, pistil; d, capsule with calyx; e, seed.
CopyrightSEAMEO-BIOTROP
a, Flower; b, corolla, opened; c, pistil; d, capsule with calyx; e, seed.
L. crustacea - line drawinga, Flower; b, corolla, opened; c, pistil; d, capsule with calyx; e, seed.SEAMEO-BIOTROP

Identity

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Preferred Scientific Name

  • Lindernia crustacea (L.) F. Muell.

Preferred Common Name

  • Malaysian false pimpernel

Other Scientific Names

  • Antirrhinum hexandrum Forssk.
  • Buchnera capillaris Desv. ex Ham.
  • Capraria crustacea L.
  • Gratiola aspera Roth
  • Gratiola lucida Willd.
  • Lindernia minuta Koord.
  • Morgania lucida Spreng.
  • Pyxidaria crustacea (L.) Kuntze
  • Tittmannia scabra (R. Br.) Spreng.
  • Torenia crustacea (L.) Hassk.
  • Torenia flaccida R. Br.
  • Torenia minuta Bl.
  • Torenia scabra R. Br.
  • Vandellia alba Benth.
  • Vandellia bodinieri H. Lév.
  • Vandellia crustacea (L.) Benth.
  • Vandellia minuta Miq.

International Common Names

  • English: brittle false pimpernel
  • Chinese: mu cao

Local Common Names

  • Bangladesh: chapraghash
  • Cook Islands: tutae torae
  • French Polynesia: haehaa; piriate
  • Indonesia: daun sirik ketok; jukut mata heuyeup
  • Indonesia/Java: brobos kebo
  • Japan: urikusa
  • Lesser Antilles: cresson bâtard

EPPO code

  • LIDCR (Lindernia crustacea)

Summary of Invasiveness

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L. crustacea is an herb including in the Global Compendium of Weeds where it is listed as environmental and agricultural weed (Randall, 2012). It has a wide distribution across tropical and subtropical regions of the world where it occurs in a wide range of wetland and some non-wetland habitats and is able to exploit anthropogenic habitats such as rice fields. Once established, this species has the potential to grow forming a mat up to 30 cm high. Currently, L. crustacea is listed as invasive in Hawaii, French Polynesia and Singapore (Wagner, 1999; Chong et al., 2009; Lansdown, 2011). 

Taxonomic Tree

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  • Domain: Eukaryota
  •     Kingdom: Plantae
  •         Phylum: Spermatophyta
  •             Subphylum: Angiospermae
  •                 Class: Dicotyledonae
  •                     Order: Scrophulariales
  •                         Family: Scrophulariaceae
  •                             Genus: Lindernia
  •                                 Species: Lindernia crustacea

Notes on Taxonomy and Nomenclature

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L. crustacea is one of about 85 accepted species in the genus Lindernia, which is among 16 plant genera now placed in the family Linderniaceae in the order Lamiales (The Plant List, 2013). In other classifications it used to be included within the family Scrophulariaceae sensu lato or more recently in Plantaginaceae sensu lato, but several authors have demonstrated that this taxon should be segregated from those families. The Linderniaceae is recognized in the APG III system. Members of the Linderniaceae are often small herbs with opposite leaves, square stems, and monosymmetric flowers with a sensitive stigma and the lower stamens usually very different from the upper.

For L. crustacea two varieties have been described, with the var. crustacea occurring in predominantly dry habitats and the var. godefroyi occurring in wetlands (Lansdown, 2011; Stevens, 2012).

Description

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L. crustacea is a small, decumbent perennial, glabrous or thinly puberulent throughout, much-branched at the base, usually rooting at the lower nodes, 8-20 cm long. It flowers throughout the year. Stems slender, sharply quadrangular to narrowly 4-winged, the angles shortly hairy, green to purple. Opposite leaves, green to purple, ovate to oblong or lanceolate, apex obtuse or subobtuse, base broadly cuneate to rounded, margins entire or distantly serrate, often dull purple, 0.5-2.5 cm long, 0.5-1.5 cm wide, upper surface glabrous, lower surface minutely puberulent; petiole 1-6 mm long. Inflorescences axillary, solitary or the uppermost forming terminal cymes; pedicels 1-3 cm long. Calyx green or purplish, 5-angled cleft to about the middle, 4-6 mm long. Corolla pale blue or purplish, 5-8 mm long, upper lip 2-lobed, lower lip 3-lobed, middle one slightly larger than the outer ones, tube 4-7 mm long. Fruit a brown, papery, 2-celled, oblong-ovoid capsule, 3.5-5 mm long. Numerous seeds, pale brown, elliptic, obtuse at both ends, tuberculate, ca 0.5 mm long (Soerjani et al., 1987).

Seedling: hypocotyl 4-6 mm long, densely papillate. Cotyledons 2, petiole 2.5-4.5 mm long, sparsely minutely hairy; blade broadly ovate, 3.5-4.5 x 3.5-5.5 mm, obscurely pinnately nerved, base obtuse to attenuate, margin entire, sparsely minutely bristly, apex truncate to emarginate. Epicotyl 0.5-4.7 mm long, 4-angular, ribs appressed-hairy. First leaves 2; petiole 1.5-2.5 mm long, winged, appressed-hairy; blade ovate, 3.3-8.8 x 2.6-6.1 mm, glandular-dotted, pinnately nerved, base obtuse, margin crenate, bristly, apex rounded (Kostermans et al., 1987).

 

Plant Type

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Herbaceous
Perennial
Seed propagated

Distribution

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L. crustacea is native to tropical Asia, but is now distributed throughout the tropics (Usher, 1974; USDA-ARS, 2015). It can be found naturalized in tropical Africa, North America, South America, and the West Indies (Lansdown, 2011; Acevedo-Rodriguez and Strong, 2012; USDA-NRCS, 2015).

Distribution Table

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The distribution in this summary table is based on all the information available. When several references are cited, they may give conflicting information on the status. Further details may be available for individual references in the Distribution Table Details section which can be selected by going to Generate Report.

Last updated: 10 Jan 2020
Continent/Country/Region Distribution Last Reported Origin First Reported Invasive Reference Notes

Africa

CameroonPresentCABI (Undated); PROTA (2015)Original citation: Hepper, 1963
Côte d'IvoirePresentCABI (Undated)Original citation: Hepper, 1963
GhanaPresentCABI (Undated); PROTA (2015)Original citation: Hepper, 1963
MadagascarPresentIntroducedPROTA (2015)
NigeriaPresentCABI (Undated)Original citation: Hepper, 1963
Sierra LeonePresentCABI (Undated)Original citation: Hepper, 1963

Asia

BangladeshPresentNativeLansdown (2011); Moody (1989)
CambodiaPresentNativeUSDA-ARS (2015)
ChinaPresentCABI (Undated b)
-AnhuiPresentNativeFlora of China Editorial Committee (2015)
-FujianPresentNativeFlora of China Editorial Committee (2015)
-GuangdongPresentNativeFlora of China Editorial Committee (2015)
-GuangxiPresentNativeFlora of China Editorial Committee (2015)
-GuizhouPresentNativeFlora of China Editorial Committee (2015)
-HainanPresentNativeFlora of China Editorial Committee (2015)
-HenanPresentNativeFlora of China Editorial Committee (2015)
-HubeiPresentNativeFlora of China Editorial Committee (2015)
-HunanPresentNativeFlora of China Editorial Committee (2015)
-JiangsuPresentNativeFlora of China Editorial Committee (2015)
-JiangxiPresentNativeFlora of China Editorial Committee (2015)
-SichuanPresentNativeFlora of China Editorial Committee (2015)
-TibetPresentNativeFlora of China Editorial Committee (2015)
-YunnanPresentNativeFlora of China Editorial Committee (2015)
-ZhejiangPresentNativeFlora of China Editorial Committee (2015)
IndiaPresentMoody (1989); USDA-ARS (2015)
-Andaman and Nicobar IslandsPresentNativeLansdown (2011)
-Andhra PradeshPresentNativeLansdown (2011)
-AssamPresentNativeLansdown (2011)
-BiharPresentJha and Sinha (1989)
-DelhiPresentNativeLansdown (2011)
-GoaPresentNativeLansdown (2011)
-GujaratPresentNativeLansdown (2011)
-KarnatakaPresentNativeLansdown (2011)
-KeralaPresentNativeLansdown (2011)
-Madhya PradeshPresentNativeLansdown (2011)
-MaharashtraPresentNativeLansdown (2011)
-ManipurPresentNativeLansdown (2011)
-MizoramPresentNativeLansdown (2011)
-OdishaPresentNativeLansdown (2011)
-RajasthanPresentNativeLansdown (2011)
-Tamil NaduPresentNativeLansdown (2011)
-Uttar PradeshPresentCABI (Undated); Lansdown (2011)Original citation: Saxena et al. (1981)
-West BengalPresentNativeLansdown (2011)
IndonesiaPresentCABI (Undated b)
JapanPresentNativeUSDA-ARS (2015); CABI (Undated)
-HokkaidoPresentOhwi (1965)
-HonshuPresentOhwi (1965); Lansdown (2011)
-KyushuPresentOhwi (1965); Lansdown (2011)
-Ryukyu IslandsPresentOhwi (1965); USDA-ARS (2015)
-ShikokuPresentOhwi (1965); Lansdown (2011)
LaosPresentNativeUSDA-ARS (2015)
MalaysiaPresentBaki Hj Bakar (2004); USDA-ARS (2015)
NepalPresentMoody (1989); USDA-ARS (2015)
North KoreaPresentOhwi (1965); USDA-ARS (2015)
PhilippinesPresentMoody (1989); USDA-ARS (2015)
SingaporePresentInvasiveChong et al. (2009); Waterhouse (1993)Uncertain if introduced or native, but listed as invasive
South KoreaPresentOhwi (1965); USDA-ARS (2015)
Sri LankaPresentMoody (1989); USDA-ARS (2015)
TaiwanPresentOhwi (1965); Flora of China Editorial Committee (2015)
ThailandPresentYongboonkird et al. (1988); USDA-ARS (2015)
VietnamPresentUSDA-ARS (2015)

North America

BelizePresentIntroducedBalick et al. (2000)
CubaPresentIntroducedAcevedo-Rodríguez and Strong (2012)
DominicaPresentIntroducedBroome et al. (2007)
Dominican RepublicPresentIntroducedAcevedo-Rodríguez and Strong (2012)
GrenadaPresentIntroducedBroome et al. (2007)
GuadeloupePresentIntroducedBroome et al. (2007)
HaitiPresentIntroducedAcevedo-Rodríguez and Strong (2012)
JamaicaPresentIntroducedAcevedo-Rodríguez and Strong (2012)
MartiniquePresentIntroducedBroome et al. (2007)
MexicoPresentIntroducedLewis (2000)
MontserratPresentIntroducedBroome et al. (2007)
Puerto RicoPresentIntroducedAcevedo-Rodríguez and Strong (2012)Weed
Saint LuciaPresentIntroducedGraveson (2012)Weed
Saint Vincent and the GrenadinesPresentIntroducedBroome et al. (2007)
Trinidad and TobagoPresentIntroducedInvasiveHolm et al. (1979)
United StatesPresentCABI (Undated a)Present based on regional distribution.
-AlabamaPresentIntroducedUSDA-NRCS (2015)
-ArkansasPresentIntroducedUSDA-ARS (2015)
-FloridaPresentIntroducedUSDA-ARS (2015)
-GeorgiaPresentIntroducedUSDA-ARS (2015)
-HawaiiPresentIntroducedInvasiveWagner et al. (1999)
-LouisianaPresentIntroducedUSDA-NRCS (2015)
-MississippiPresentIntroducedUSDA-NRCS (2015)
-North CarolinaPresentIntroducedUSDA-NRCS (2015)
-South CarolinaPresentIntroducedUSDA-NRCS (2015)
-TexasPresentIntroducedUSDA-NRCS (2015)

Oceania

American SamoaPresentWhistler (1980)Uncertain if native or alien
AustraliaPresentCABI (Undated a)Present based on regional distribution.
-QueenslandPresentNativeUSDA-ARS (2015)
Christmas IslandPresentNativeUSDA-ARS (2015)
Cook IslandsPresentCABI (Undated)Original citation: Whistler (1992)
Federated States of MicronesiaPresentLorence and Flynn (2010)Uncertain if native or alien
FijiPresentSmith (1991)Origin uncertain
French PolynesiaPresentCABI (Undated); Florence et al. (2013)Original citation: Whistler (1992)
Marshall IslandsPresentPIER (2015)
Northern Mariana IslandsPresentNativeRaulerson (2006)
PalauPresentNativePIER (2015)
Papua New GuineaPresentNativePIER (2015)
SamoaPresentNativePIER (2015)
Solomon IslandsPresentNativeHancock and Henderson (1988)
TongaPresentCABI (Undated)Introduced on Kao and Vava Islands; Original citation: Whistler (1992)

South America

BoliviaPresentIntroducedLewis (2000)
BrazilPresentCABI (Undated a)Present based on regional distribution.
-AcrePresentIntroducedSouza (2015)
-AlagoasPresentIntroducedSouza (2015)
-AmazonasPresentIntroducedSouza (2015)
-CearaPresentIntroducedSouza (2015)
-GoiasPresentIntroducedSouza (2015)
-MaranhaoPresentIntroducedSouza (2015)
-Mato GrossoPresentIntroducedSouza (2015)
-Mato Grosso do SulPresentIntroducedSouza (2015)
-ParaPresentIntroducedSouza (2015)
-ParaibaPresentIntroducedSouza (2015)
-PernambucoPresentIntroducedSouza (2015)
-RondoniaPresentIntroducedSouza (2015)
-RoraimaPresentIntroducedSouza (2015)
-Sao PauloPresentIntroducedSouza (2015)
-SergipePresentIntroducedSouza (2015)
-TocantinsPresentIntroducedSouza (2015)
ColombiaPresentIntroducedIdárraga-Piedrahita et al. (2011)
EcuadorPresentIntroducedJørgensen and León-Yánez (1999)
French GuianaPresentIntroducedFunk et al. (2007)
GuyanaPresentIntroducedFunk et al. (2007)
PeruPresentIntroducedLewis (2000)
SurinamePresentFunk et al. (2007)
VenezuelaPresentIntroducedFunk et al. (2007)

History of Introduction and Spread

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Because L. crustacea behaves as a weed, it was probably introduced accidentally into new habitats. In the West Indies, this species appears in herbarium collections made in 1894 in Guadeloupe, 1912 in Jamaica, 1939 in Martinique and Grenada and in 1950 in St Lucia (US National Herbarium). In Puerto Rico, this species represents a recent introduction. It was first reported by Liogier (1965) as common in waste grounds. The current status in this island is not well known but it seems to be very common in open, moist habitats. 

Risk of Introduction

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The risk of introduction of L. crustacea is high. This species is a common weed in both agricultural and disturbed sites and has a wide geographical distribution. Additionally, it has a great dispersion capability and can spread by seeds and vegetatively by nodes on the stems (Lansdown, 2011; Randall, 2012; PROTA, 2015; USDA-ARS, 2015). 

Habitat

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In Polynesia, L. crustacea extends as far east as the Marquesas (Whistler, 1992). It is common in wet sites, cultivated fields and gardens, along roadsides, often on compact hard soils, and may form a dense turf on bare ground if not disturbed. L. crustacea grows up to 3000 m in altitude, but mostly to 1500 m (Kostermans et al., 1989). In Polynesia, it is found in wet places, such as stream beds and taro fields, from the lowlands to the montane forest (Whistler, 1992).

Lansdown (2011) says that it “can occur in dry roadsides, lawns, rice fields, riversides, swamps, sandy river banks, low-lying pastures and drying-out tanks, sometimes near the sea-shore”.

Habitat List

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CategorySub-CategoryHabitatPresenceStatus
Terrestrial
Terrestrial – ManagedCultivated / agricultural land Present, no further details Harmful (pest or invasive)
Cultivated / agricultural land Present, no further details Natural
Rail / roadsides Present, no further details Harmful (pest or invasive)
Rail / roadsides Present, no further details Natural
Terrestrial ‑ Natural / Semi-naturalNatural grasslands Present, no further details Harmful (pest or invasive)
Natural grasslands Present, no further details Natural
Riverbanks Present, no further details Harmful (pest or invasive)
Riverbanks Present, no further details Natural

Host Plants and Other Plants Affected

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Plant nameFamilyContext
Colocasia esculenta (taro)AraceaeOther
Oryza sativa (rice)PoaceaeMain

Biology and Ecology

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Genetics

The chromosome number reported for L. crustacea is 2n = 32, 42.

Physiology and Phenology

L. crustacea is a small annual or perennial weed, reproducing by seed. Information on germination biology is lacking, and it is not certain whether this species can germinate under water. It is not a strictly aquatic plant but is recorded from all types of rice cultivation and must have some ability to tolerate flooded conditions.

In a seed bank study conducted, L. crustacea seed germinated over a three month period when incubated in 1 cm of soil, at 74-92% humidity and soil surface temperatures of 25-29.4°C (Kellman, 1974).

In China, L. crustacea has been recorded flowering and fruiting all year round (Flora of China Editorial Committee, 2015). In India, it produces flowers and fruits from August to November (India Biodiversity Portal, 2016).

Environmental Requirements

L. crustacea grows mainly in moist to wet habitats in disturbed areas; particularly rice fields, grassland, irrigated crops, riverbanks, creeks, swamp edges, damp grassland, lawns, disturbed forests, plantations, and along roadsides and trails. It grows at altitudes ranging from sea level to 1300 m in China, 250-1800 m in Nepal, 150-1220 m in Hawaii, 0-300 m in Fiji, and from 0-2500 m in Papua New Guinea (Smith, 1991; Wagner et al., 1999; Flora of China Editorial Committee, 2015; PIER, 2015; PROTA, 2015).

Climate

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ClimateStatusDescriptionRemark
Af - Tropical rainforest climate Preferred > 60mm precipitation per month
Am - Tropical monsoon climate Preferred Tropical monsoon climate ( < 60mm precipitation driest month but > (100 - [total annual precipitation(mm}/25]))
As - Tropical savanna climate with dry summer Preferred < 60mm precipitation driest month (in summer) and < (100 - [total annual precipitation{mm}/25])
Aw - Tropical wet and dry savanna climate Preferred < 60mm precipitation driest month (in winter) and < (100 - [total annual precipitation{mm}/25])

Soil Tolerances

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Soil reaction

  • acid
  • neutral

Soil texture

  • light
  • medium

Means of Movement and Dispersal

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L. crustacea spreads by seed and vegetatively by nodes on the stems. Seeds are approximately 0.5 mm long and can be dispersed by multiple factors such as wind, water, animals and as a contaminant in machinery, soils, and crops (Wagner et al., 1999; Flora of China Editorial Committee, 2015).

Pathway Causes

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CauseNotesLong DistanceLocalReferences
DisturbanceWeed Yes Yes Holm et al., 1979

Pathway Vectors

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VectorNotesLong DistanceLocalReferences
Debris and waste associated with human activitiesAgricultural weed Yes Yes Holm et al., 1979
Soil, sand and gravelSeeds and stem fragments Yes Yes Holm et al., 1979
WaterSeeds Yes Yes Holm et al., 1979
WindSeeds Yes Yes Holm et al., 1979

Impact Summary

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CategoryImpact
Economic/livelihood Positive and negative
Environment (generally) Positive and negative

Economic Impact

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L. crustacea is described by Kostermans et al. (1987) as a weed of all kinds of rice field, but of minor importance. In the Philippines, it is a common weed in open fields, rice paddies and cultivated ground (Pancho and Obien, 1995). In Bangladesh, it occurs in transplanted aman rice fields at higher altitudes, along roadsides and on levees of crop fields (Mamun, 1989). It occurs as a weed in transplanted rice in India, Indonesia and Vietnam, in upland rice in India, the Philippines and Vietnam, and in wet-seeded rice (sprouted seeds sown on puddled soil) in India and Malaysia. It has also been reported as a weed of lowland rice in Bangladesh and a weed of rice in Nepal and Sri Lanka (Moody, 1989).

It is a weed in tobacco and vegetables as well as rice (Waterhouse, 1993). It is also described as a serious weed in Trinidad, and a widespread and important weed in Malaysia and Singapore (Holm et al., 1979, Waterhouse 1993; Bakar, 2004; Chong et al., 2009).

Risk and Impact Factors

Top of page Invasiveness
  • Proved invasive outside its native range
  • Has a broad native range
  • Abundant in its native range
  • Highly adaptable to different environments
  • Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
  • Pioneering in disturbed areas
  • Highly mobile locally
  • Benefits from human association (i.e. it is a human commensal)
  • Fast growing
Impact outcomes
  • Ecosystem change/ habitat alteration
  • Modification of successional patterns
  • Negatively impacts agriculture
  • Reduced native biodiversity
  • Threat to/ loss of native species
Impact mechanisms
  • Competition - monopolizing resources
  • Competition - smothering
  • Rapid growth
Likelihood of entry/control
  • Highly likely to be transported internationally accidentally
  • Difficult to identify/detect as a commodity contaminant
  • Difficult to identify/detect in the field

Uses

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In Asia, L. crustacea is used as a medicinal herb. Petard (1972), cited in Whistler (1992), reported that it was used for umbilical infections, boils, uterine haemorrhage, leucorrhea, jaundice and colic. In Malaysia, a decoction of the leaves is used as medicine after childbirth. In the Moluccas, it is applied to boils and itches and herpes-like sores. In Indo-China, the plant is considered to have emetic and cathartic properties, and has given good results in treating bilious disorders, dysentery, amenorrhoea, and hepatitis. It is one of the commonest plants in Chinese pharmacies in Indonesia and Malaysia. In Brunei, the powdered herb mixed with rice water is drunk to relieve diarrhoea, vomiting and cholera (Flora of China Editorial Committee, 2015; PROTA, 2015).

The leaves are used in Tahiti to treat earache (Usher, 1974). Currently, the most popular Tahitian use is in purgative remedies for infants; it is also used for leucorrhea. In the Cook Islands, a solution of the crushed leaves is given to babies suffering from an ill-defined group of ailments known as IRA and sometimes for infection of the navel (Whistler, 1992).

 

Uses List

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Medicinal, pharmaceutical

  • Traditional/folklore

Similarities to Other Species/Conditions

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L. crustacea may be distinguished from other Lindernia species by its four fertile stamens (two in L. ciliata, L. anagallis and L. antipoda) and its purple corolla tube, with purple limb, lower lip with a yellow spot at base, and calyx divided only to the middle (corolla tube white, lower lip white with a purple margin, and calyx divided almost to the base in L. procumbens).

Prevention and Control

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Due to the variable regulations around (de)registration of pesticides, your national list of registered pesticides or relevant authority should be consulted to determine which products are legally allowed for use in your country when considering chemical control. Pesticides should always be used in a lawful manner, consistent with the product's label.

Foliar treatment with 2,4-D may be applied; paraquat was found to be ineffective for control of L. crustacea (Kostermans et al., 1987). Post emergence application of ioxynil+2,4-D controlled a range of broadleaved weeds, including L. crustacea, in sugar cane (Cooke et al. 1969).

While Lindernia species are normally controlled by sulfonylurea herbicides, resistance to this group of herbicides has now been observed in Japan, in L. micrantha, L. dubia, L. pyxidara and L. sessiliflora (Itoh and Guangxi Wang, 1997).

References

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Acevedo-Rodríguez P; Strong MT, 2012. Catalogue of the Seed Plants of the West Indies. Smithsonian Contributions to Botany, 98:1192 pp. Washington DC, USA: Smithsonian Institution. http://botany.si.edu/Antilles/WestIndies/catalog.htm

Anon, 1986. Mechanised rice projects at Rambai, Mulaut and Kandol. Interim Report for Mulaut, Volume 2, Appendices. Negara Brunei Darussalam: Agricultural Development Corporation.

Anon., 1964. Weeds found on Cultivated Land in Western Taiwan. Plant Industry Series No. 25. Taipei, Taiwan: Plant Industry Division.

Anon., 1992. Important crops of the world and their weeds, 2nd ed. Leverkusen, Germany: Bayer.

Azmi M, 1996. Weed succession and control in Malaysian direct seeded rice. Lee MS, 1996. An introduction to direct-seeded rice in Taiwan. In: Weed Control under Direct Seeded Rice, Proceedings of an International Symposium, Omagari, Japan, 1995, 2-26.

Bakar NH, 2004. Invasive weed species in Malaysian agro-ecosystems: species, impacts and management. Malaysian Journal of Science, 23:1-42.

Balick MJ; Nee M; Atha DE, 2000. Checklist of the vascular plants of Belize. Memoirs of the New York Botanical Garden, 85:1-246.

Broome R; Sabir K; Carrington S, 2007. Plants of the Eastern Caribbean. Online database. Barbados: University of the West Indies. http://ecflora.cavehill.uwi.edu/index.html

Bu WL; Lou HX; Liang QN; Cai XJ, 1994. Brief report on the screening of herbicides in thin sowing rice nurseries. Plant Protection, 20(1):47

Chiang YJ; Leu LS, 1987. Effect of application timing and residual period of Londax on main paddy weeds in Taiwan. Proceedings, 11th Asian Pacific Weed Science Society Conference Taipei, Taiwan; Asian Pacific Weed Science Society, No. 1:223-231

Chong KY; Tan HTW; Corlett RT, 2009. A checklist of the total vascular plant flora of Singapore: native, naturalised and cultivated species. Singapore: Raffles Museum of Biodiversity Research, National University of Singapore, 273 pp. http://lkcnhm.nus.edu.sg/nus/pdf/PUBLICATION/LKCNH%20Museum%20Books/LKCNHM%20Books/flora_of_singapore_tc.pdf

Cooke K; Parker CG; Williams DJ, 1969. Post-emergence weed control experiments in sugar cane with formulations of asulam and ioxynil/ 2,4-D. In: Proceedings, West Indies Sugar Cane Conference. 112-17.

Fassett NC, 1966. A Manual of Aquatic Plants. Madison, Wisconsin, USA: University of Wisconsin Press.

Flora of China Editorial Committee, 2015. Flora of China. St. Louis, Missouri and Cambridge, Massachusetts, USA: Missouri Botanical Garden and Harvard University Herbaria. http://www.efloras.org/flora_page.aspx?flora_id=2

Florence J; Chevillotte H; Ollier C; Meyer J-Y, 2013. Base de données botaniques Nadeaud de l'Herbier de la Polynésie Française (PAP) (Botanical database of the Nadeaud Herbarium of French Polynesia). http://www.herbier-tahiti.pf

Fujikawa K; Kyo S, 1973. Efficacy of chlomethoxynil in rice. Proceedings of the 4th Asian-Pacific Weed Science Society Conference, Rotorua, 1973, 130-133.

Fukushima Y; Ihkuma M; Tanaka K, 1995. Weed emergence and optimum time for application of herbicides in early-season paddy-rice culture in northern Kyushu. Weed Research Japan, 40:1-7.

Funk V; Hollowell T; Berry P; Kelloff C; Alexander SN, 2007. Checklist of the plants of the Guiana Shield (Venezuela: Amazonas, Bolivar, Delta Amacuro; Guyana, Surinam, French Guiana). Contributions from the United States National Herbarium, 584 pp.

Graveson R, 2012. The Plants of Saint Lucia (in the Lesser Antilles of the Caribbean). The Plants of Saint Lucia (in the Lesser Antilles of the Caribbean). http://www.saintlucianplants.com

Hancock IR; Henderson CP, 1988. Flora of the Solomon Islands. Research Bulletin No. 7. Honiara, Solomon Islands: Dodo Creek Research Station.

Holm LG; Pancho JV; Herberger JP; Plucknett DL, 1979. A Geographical Atlas of World Weeds. New York, USA: Wiley.

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Hsieh FK; Hwang JS, 1986. Some ecological aspects of the green peach aphid transmitting papaya ringspot virus in Taiwan. Plant Protection Bulletin, Taiwan, 28(3):273-287

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Distribution References

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Lansdown RV, 2011. Lindernia crustacea. In: The IUCN Red List of Threatened Species. Version 2014, http://www.iucnredlist.org/details/168747/0

Lewis D Q, 2000. A revision of the New World species of Lindernia (Scrophulariaceae). Castanea. 65 (2), 93-122.

Lorence DH, Flynn T, 2010. Checklist of the plants of Kosrae. Unpublished checklist., Lawai, Hawaii, National Tropical Botanical Garden. 26.

Moody K, 1989. Weeds reported in rice in South and Southeast Asia. Manila, Philippines: International Rice Research Institute. 442 pp.

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Smith AC, 1991. Flora Vitiensis nova: A new flora of Fiji., 5 Lawai, Kauai, Hawai`i, National Tropical Botanical Garden. 626 pp.

Souza VC, 2015. Linderniaceae in the list of species of the Flora of Brazil. (Linderniaceae in Lista de Espécies da Flora do Brasil)., http://floradobrasil.jbrj.gov.br/jabot/floradobrasil/FB21093

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Waterhouse D F, 1993. The major arthropod pests and weeds of agriculture in Southeast Asia. Canberra, Australia: ACIAR. v + 141 pp.

Whistler WA, 1980. The vegetation of eastern Samoa. In: Allertonia, 2 45-90.

Yongboonkird U, Notaya A, Paisooksantiwatana Y, Lekham J, Vongsaroj J, 1988. The survey of weeds in upland rice. In: Annual Report 1985, Bangkok, Thailand: Botany and Weed Science Division, Ministry of Agriculture and Cooperatives. 62-67.

Links to Websites

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GISD/IASPMR: Invasive Alien Species Pathway Management Resource and DAISIE European Invasive Alien Species Gatewayhttps://doi.org/10.5061/dryad.m93f6Data source for updated system data added to species habitat list.

Contributors

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03/06/15 Updated by:

Julissa Rojas-Sandoval, Department of Botany-Smithsonian NMNH, Washington DC, USA

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