Pennisetum pedicellatum (deenanath grass)

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Caption

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Inflorescences

Pennisetum pedicellatum inflorescences, Mali.

©Chris Parker/Bristol, UK

Identity

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Preferred Scientific Name

Pennisetum pedicellatum Trin.

Preferred Common Name

deenanath grass

Other Scientific Names

Eriochaeta secundiflora Figari & De Notaris
Pennisetum amoenum A. Rich.
Pennisetum densiflorum (Figari & DeNot) T. Durand & Schinz
Pennisetum dillonii Steud.
Pennisetum implicatum Steud.
Pennisetum lanuginosum Hochst.

International Common Names

English: annual kyasuwa grass; dinanath grass; feather pennisetum; kayasuwa grass; kyasuma grass; kyasuwa grass; perennial dinanath

Local Common Names

Australia: dryland napier grass
Nigeria: Nigeria grass

EPPO code

PESPE (Pennisetum pedicellatum)

Summary of Invasiveness

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P. pedicellatum is an aggressive grass weed, commonly invading agricultural land in the tropics, where dense infestations can force the abandonment of whole farms. It spreads quickly and is difficult to control. It has been widely introduced in the previous several decades as a potential forage grass and has escaped from cultivation. There are risks of its further introduction, to e.g. tropical America where it would pose a serious threat to agriculture.

Taxonomic Tree

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Domain: Eukaryota
Kingdom: Plantae
Phylum: Spermatophyta
Subphylum: Angiospermae
Class: Monocotyledonae
Order: Cyperales
Family: Poaceae
Genus: Pennisetum
Species: Pennisetum pedicellatum

Notes on Taxonomy and Nomenclature

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The genus Pennisetum is derived from the Latin 'pinna' meaning feather, and 'seta' meaning stiff hair, alluding to the bristle-like involucre of many species of this genus. It is a large genus divided into five sections: Gymnothrix, Eu-Pennisetum, Pennicillaria, Heterostachya, and Brevivalvula. P. pedicellatum belongs to section Brevivalvula, tribe Paniceae. It is closely related to P. atrichum, P. glaucum, P. hordeoides, P. pedicellatum, P. polystachion, P. setosum (syn. P. polystachion) and P. subangustum, which together form a polyploid and agamic complex (Schmelzer, 1997). Two subspecies are accepted, subsp. pedicellatum and subsp. unispiculum.

Description

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P. pedicellatum is an annual tufted grass, rarely perennial in subsp. unispiculum. Grass culms are herbaceous; reaching a height of 30-150 cm; leaves hairy, 5-25 cm long and 4-15 mm wide, arranged in two rows. Inflorescence is a tight panicle, cylindrical, 5-15 cm long and 10-15 mm wide; inflorescence exerted from uppermost leaf-sheath; rachis angular, puberulous, and very rarely pubescent; branches ending in bristle-like appendages. Upper glume and lower lemma more or less 3-lobed, 2.5-6 mm long; upper lemma obtuse, thinly coriaceous, ciliolate at the apex, readily disarticulating from the rest of the spikelet. Spikelets 4-6 mm long solitary, falling entire at maturity with bristles. Spikelets in clusters of 1-5 within the involucre, at least one of the spikelets upon a pedicel 1-3 mm long; bristles densely woolly plumose, forming a fluffy ovate involucre 0.5-1 cm long. 2-flowered, lower floret of fertile spikelet male, upper bisexual or female, bisexual mixed in the same inflorescence, lower glume shorter than florets, completely surrounded by a ring of bristles. Bristles free to base, fine and thread-like. Involucre bristles hairy, rhachis glabrous, spikelets pedicelled within involucre (Hepper, 1972; Poilecot, 1995).

Plant Type

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Annual
Grass / sedge
Herbaceous
Seed propagated

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: 12 May 2022

Continent/Country/Region	Distribution	Origin	First Reported	Invasive	Reference	Notes
Africa
Benin	Present, Widespread	Native		Invasive	Heper (1972) Sinsin (1993) Poilecot (1995) Holou (2002)
Burkina Faso	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Cabo Verde	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Cameroon	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Côte d'Ivoire	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Eritrea	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Ethiopia	Present, Localized	Native		Invasive	Heper (1972) Holm et al. (1977) Poilecot (1995) EPPO (2022)
Gambia	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Ghana	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Guinea	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Kenya	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Mali	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Mauritania	Present	Native		Invasive	Heper (1972) Poilecot (1995)
Niger	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Nigeria	Present, Localized	Native		Invasive	Heper (1972) Holm et al. (1977) Poilecot (1995) EPPO (2022)
Senegal	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Sudan	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Tanzania	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Togo	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Zambia	Present, Widespread	Native		Invasive	Heper (1972) Poilecot (1995)
Asia
Bhutan	Present, Localized	Introduced			Noltie (2000) Seebens et al. (2017)
India	Present, Localized	Native		Invasive	Heper (1972) Poilecot (1995) EPPO (2022)
-Andaman and Nicobar Islands	Present	Introduced		Invasive	Gangwar and Jayan (1986)
-West Bengal	Present, Widespread	Introduced		Invasive	Mukherjee et al. (1982)
Indonesia	Present	Introduced			Holm et al. (1977)
Malaysia	Present, Localized	Introduced		Invasive	Holm et al. (1977) EPPO (2022)
Myanmar	Present				EPPO (2022)
Nepal	Present	Introduced	1997	Invasive	Siwakoti and Varma (1997)
Philippines	Present	Introduced			Holm et al. (1977)
Thailand	Present, Localized	Introduced		Invasive	Holm et al. (1977) EPPO (2022)
North America
United States	Present				CABI (Undated)	Present based on regional distribution.
-Florida	Present, Localized	Introduced		Invasive	CABI (Undated a)
Oceania
Australia	Present, Localized	Introduced		Invasive	Mott (1980) Groves (1991) Seebens et al. (2017) EPPO (2022)
-Northern Territory	Present	Introduced		Invasive	Doughton (1974) Mott (1980)
-Queensland	Present, Widespread	Introduced	1943	Invasive	Holm et al. (1977) Harrison (1983)
Fiji	Present, Localized	Introduced			Holm et al. (1977) EPPO (2022)
Norfolk Island	Present	Introduced		Invasive	Gangwar and Jayan (1986)
Solomon Islands	Present	Introduced		Invasive	Gangwar and Jayan (1986)
U.S. Minor Outlying Islands	Present	Introduced		Invasive	Gangwar and Jayan (1986)

History of Introduction and Spread

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These species are thought to be native to tropical Africa (Schmelzer and Renno, 1997), widespread in the sudanian and guinean zones from West to East Africa. It has been widely introduced as a drought-resistant fodder grass and has escaped from cultivation to become a serious invasive weed notably in Asia but also in Australia and the Pacific. Many of these introductions have been relatively recent. In Australia, P. pedicellatum was used in trials for the screening of potential pasture plants with early reports indicating its good yield and average quality (Anon., 1957), and from the 1960s to the 1980s a gradual spread occurred unwittingly aided by its establishment at a number of experiment sites. The species was reported as an addition to the flora of Nepal in 1997 (Siwakoti and Varma, 1997). This weed was introduced as a fodder crop to the Andaman islands, India (Gangwar and Jayan, 1986; Krishna and Kumar, 1996).

Risk of Introduction

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P. pedicellatum is regulated as a federal noxious weed in USA.

Habitat

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The species is widespread in sudanian and guinean savannahs of Africa though sparse in littoral areas, where it is a common agricultural weed, present on cultivated fields, also managed grasslands as well as extensively grazed savannahs. It is a weed in tropical uplands and croplands following disturbance or forest clearing, but is less common within forests and plantations, performing poorly under dense shade. Where introduced in India and Nepal it is also found on cultivated and pasture lands (Shukla et al., 1988; Siwakoti and Varma, 1997).

Habitat List

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Category	Sub-Category	Habitat	Presence	Status
Terrestrial
Terrestrial	Managed	Cultivated / agricultural land	Present, no further details	Harmful (pest or invasive)
Terrestrial	Managed	Protected agriculture (e.g. glasshouse production)	Present, no further details	Harmful (pest or invasive)
Terrestrial	Managed	Managed forests, plantations and orchards	Present, no further details	Harmful (pest or invasive)
Terrestrial	Managed	Managed grasslands (grazing systems)	Present, no further details
Terrestrial	Natural / Semi-natural	Natural forests	Present, no further details	Harmful (pest or invasive)
Terrestrial	Natural / Semi-natural	Natural grasslands	Present, no further details
Terrestrial	Natural / Semi-natural	Wetlands	Present, no further details	Harmful (pest or invasive)
Terrestrial	Natural / Semi-natural	Cold lands / tundra	Present, no further details	Harmful (pest or invasive)
Terrestrial	Natural / Semi-natural	Deserts	Present, no further details	Harmful (pest or invasive)

Hosts/Species Affected

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P. pedicellatum is commonly found in many crops; it was found to be abundant in maize fields but scarce in cotton fields in Thailand (Yongboonkird, 1971) and is important in sorghum in Australia (Groves, 1991).

Host Plants and Other Plants Affected

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Plant name	Family	Context
Gossypium barbadense (Gallini cotton)	Malvaceae	Unknown
Gossypium hirsutum (Bourbon cotton)	Malvaceae	Unknown
Sorghum bicolor (sorghum)	Poaceae	Unknown
Zea mays (maize)	Poaceae	Unknown

Growth Stages

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Flowering stage, Fruiting stage, Vegetative growing stage

Biology and Ecology

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Genetics

Cytological studies of the perennial accession type Agros-4 of P. pedicellatum revealed it to be an octoploid (2n=72) with a base chromosome number of x=9. Detailed cytological analysis and the nature of chromosome pairing at microsporogenesis suggest a segmental allopolyploid origin of the taxon (Zadoo et al., 1997). However, the annual form of the weed in Australia was shown to have a chromosome number of 2n=36 (Harrison, 1983). Studies indicate that P. pedicellatum might hybridize with P. polystachion (Hepper, 1972).

Physiology and Phenology

Seedling growth varied considerably with temperature with the highest growth at a constant temperature of 32°C. P. pedicellatum responds well to nitrogen fertilization, with maximum yields (13 t DM/ha) obtained at 145 kg N/ha (Mukherjee et al., 1982). In Orissa, P. pedicellatum sown at the end of March gave fresh fodder yields of 55.7-81 t/ha and 82.1-128.5 t/ha when harvested 82 and 110 days after sowing, respectively (Mandal and Vamadevan, 1978). P. pedicellatum tiller number per plant increased with row spacing and highest yields were obtained with a 15 cm inter-row spacing (Ferris and Poudal, 1995). Cross-sowing of P. pedicellatum and Vigna unguiculata at 100% sowing rates of 12 and 40 kg seeds/ha, respectively, gave 53.30 t/ha fresh fodder and 11.50 t DM/ha (Prasad et al., 1990). The chemical composition of P. pedicellatum plants varied with the phenology (Banerjee and Mandal, 1974; Upadhyay et al., 1978; Jakhmola and Pathak; 1983).

Dry matter content of P. pedicellatum is 17-44% (Singh and Premchand Rahaman, 1972). Applied nitrogen increased below ground biomass, root length and root length density of P. pedicellatum (Vinod et al., 1996). Moreover, root growth was greatest at a 75-day cutting frequency, with the presence of mycorrhiza provoking a change in protein profiles and enzymes in the roots of P. pedicellatum (Ramesh et al., 2000). P. pedicellatum inoculated with Glomus mosseae, G. aggregatum and Gigaspora margarita, showed that G. margarita induced increased protein content, and acid phosphatase, alkaline phosphatase, superoxide dismutase and chitinase activities were highest at the beginning of infection, but declined as the infection advanced. G. margarita was an efficient fungus in enhancing enzyme activity and proteins in roots compared with Glomus mosseae and G. aggregatum.

Reproductive Biology

Embryogenesis has been studied (Shobha and Sindhe, 2000) and P. pedicellatum has apomictic reproductive behaviour (Chaix and Marchais, 1996). Seed yield in P. pedicellatum depends upon flowering period, flag-leaf area and number of panicles per plant (Muralimohanreddy and Chatterji, 1975), increasing linearly with nitrogen rates from 0.80 to 1.21 t/ha (Ramamurthy et al., 1998). Uniform ability for germination of P. pedicellatum seed is obtained at temperatures of 25-35°C (Afolayan and Olugbami, 1993). Hull-imposed dormancy was evident and removal of husks facilitated germination (Parihar et al., 1997). To facilitate P. pedicellatum seed germination, Maiti et al. (1981) proposed soaking for 24 h in 1% nitric acid or scarification with sandpaper. Seeds of P. pedicellatum showed 94% viability with maximum seedling emergence with seed sown on the soil surface and a progressive decrease in emergence at greater soil depths; with percentage germination of 45% and 19.2% at depths of 2 cm and 6 cm, respectively (Ezeigwe and Olunuga, 1974), and no germination below 7 cm. Germination was reduced under continuous light or darkness as compared to under alternating light and dark conditions (Afolayan and Olugbami, 1993). Storage length affects seed germination, with percentage germination of 8 week-old seed found to be 175% by Ramamurthy et al. (1998), or 12% germination at 10 weeks after harvest and 73-100% germination at 20-66 weeks, with maximum germination (95-100%) at 34-66 weeks after harvest (Paramathma and Surendran, 1990).

Environmental Requirements

P. pedicellatum is a tropical to sub-tropical species, tolerant to a range of rainfall regimes from semi-arid to humid. It is tolerant of salinity, though increased salinity affected growth (Varshney and Baijal, 1977). The species controlled water loss effectively and has a very strong recovery ability after watering even under severe drought conditions (Noitsakis et al., 1994).

Associations

On cultivated areas, the species is often associated with other weeds such as Andropogon pseudapricus, A. gayanus, A. fastigiatus, Aristida kerstingii, Loudetia togoensis and Pennisetum polystachion, and is considered as a characteristic species of young fallow (Poilecot, 1995). There are a number of recorded natural enemies, though their effects on the growth of P. pedicellatum are not known. Cynodon mosaic virus is associated with P. pedicellatum, first reported on Cynodon dactylon from India (Bhargava et al., 1971) and causing a systemic chlorotic mottling and is transmitted by mechanical inoculation and by aphids. It is also known to infect Zea mays and Sorghum bicolor. In Senegal, endomycorrhizal fungal (Glomus sp., Scutellospora verrucosa and S. gregaria) colonization by P. pedicellatum was poorly developed (Duponnois et al., 2001). Moreover, fungi such as Glomus intaradices, Sclerocystis rubiformis, Scutellospora gregaria, Scutellospora verrucosa were obtained in the rhizospheric soil of P. pedicellatum in Senegal (Ahmed et al., 1998). Also, Acaulospora sp., Glomus contrictum were obtained from the soil under P. pedicellatum using Lycopersicum esculentum and Lolium perenne as host plants. There are no reports on the mycorrhizal status of P. pedicellatum in semi arid soils, therefore the high spore density which can be obtained under this species may have come from other plants such as Acacia senegal, Combretum glutinosum, Piliostigma reticulatum, etc., which are known to harbour mycorrhiza (Cucousso, 1991). P. pedicellatum is usually associated with large nematode populations (Cadet and Floret, 1995), with Longidorus brevis described from Senegal (Swart et al., 1996) and Meloidogyne incognita in India (Vaishnav and Sethi, 1977). The contribution of termites to the breakdown of P. pedicellatum straw was estimated to be over 70% (Mando and Brussaard, 1999), indicating that it is an important resource for termites.

Air Temperature

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Parameter	Lower limit	Upper limit
Absolute minimum temperature (ºC)	15
Mean annual temperature (ºC)	26	28
Mean maximum temperature of hottest month (ºC)		35
Mean minimum temperature of coldest month (ºC)	18

Rainfall

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Parameter	Lower limit	Upper limit	Description
Dry season duration	2	6	number of consecutive months with <40 mm rainfall
Mean annual rainfall	500	11000	mm; lower/upper limits

Soil Tolerances

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Soil drainage

free

Soil reaction

acid
neutral

Soil texture

heavy
light
medium

Special soil tolerances

infertile
saline
shallow

Notes on Natural Enemies

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P. pedicellatum is recorded as a larval food plant for the immature stages of the lepidopteran Borbo impar lavinia (Syn. Baoris impar) in Australia (Meyer, 1997; Michael, 2000). Commonly known as 'yellow swift', it feeds at night on various grasses and various subspecies are found from Indonesia to the Solomon islands. Larvae of the rice leaffolder or rice leaf roller, Cnaphalocrocis medinalis (Spilomelini: Pyraustinae: Pyralidae) (syn. Botys nurscialia) were observed feeding inside rolled leaves of P. pedicellatum growing along the edges of rice-fields in Madhya Pradesh, India, the first record of the rice pest infesting this grass in India (Patel, 1973). It is a pest throughout South-East Asia feeding on rice (Oryza sativa) and is known to migrate making control difficult. The species is found from China to Australia, as far south as Port Macquarie in New South Wales (Ian, 1990). Finally, in India, severe brown leaf spot disease of P. pedicellatum was caused by Pyricularia grisea (syn. Magnaporthe grisea) (Saikia et al., 1982; Bhaskar and Ahmad, 1994).

Means of Movement and Dispersal

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The factors associated with P. pedicellatum potential are prolific seedling, and windborne seed dispersal, a highly competitive and smothering growth habit, and poor values as dry standing feed. The collection of P. pedicellatum as a cut and carry fodder to livestock also contributes to the movement of the weed.

Pathway Vectors

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Vector	Notes	Long Distance	Local	References
Clothing, footwear and possessions		Yes
Land vehicles		Yes
Mail		Yes
Plants or parts of plants		Yes
Soil, sand and gravel		Yes

Plant Trade

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Plant parts liable to carry the pest in trade/transport	Pest stages	Borne internally	Borne externally	Visibility of pest or symptoms
Flowers/Inflorescences/Cones/Calyx	weeds/seeds
Fruits (inc. pods)	weeds/seeds
Growing medium accompanying plants	weeds/seeds
Leaves	weeds/leaves
Roots	weeds/roots
Stems (above ground)/Shoots/Trunks/Branches	weeds/leaves
True seeds (inc. grain)	weeds/seeds

Plant parts not known to carry the pest in trade/transport
Bark
Bulbs/Tubers/Corms/Rhizomes
Seedlings/Micropropagated plants
Wood

Impact Summary

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Category	Impact
Animal/plant collections	None
Animal/plant products	Positive
Biodiversity (generally)	Negative
Crop production	Negative
Environment (generally)	None
Fisheries / aquaculture	None
Forestry production	None
Human health	None
Livestock production	Positive
Native fauna	Positive
Native flora	Negative
Rare/protected species	None
Tourism	None
Trade/international relations	None
Transport/travel	None

Impact

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Holm et al. (1979) indicate that P. pedicellatum is a 'serious' weed (highest category) in Nigeria and Thailand, and a 'principal' weed in Australia. As an agricultural weed, P. pedicellatum reduces farmers' profit margins by reducing crop yields; but according to its fodder value, it contributes to meeting the fodder requirements for livestock in rural areas. The species may be serving as an alternative host of downy mildew (Sclerospora graminicola), but on the other hand, the resistance of such a species to this disease has been suggested as promising for breeding resistance in pearl millet (Pennisetum glaucum) (Singh and Navi, 2000).

Environmental Impact

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P. pedicellatum has positive benefits in controlling soil erosion and improving the physical and chemical properties of the soil (Kumar and Jena, 1996).

Impact: Biodiversity

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In some habitats where the species is undesirable, P. pedicellatum can replace natural plants and then reduce species richness.

Social Impact

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P. pedicellatum can be so aggressive when invading agricultural land in the tropics that dense infestations have been known to force the abandonment of whole farms with the subsequent negative social impact.

Risk and Impact Factors

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Invasiveness

Invasive in its native range
Proved invasive outside its native range
Highly adaptable to different environments
Tolerates, or benefits from, cultivation, browsing pressure, mutilation, fire etc
Has high reproductive potential

Impact outcomes

Negatively impacts agriculture
Reduced native biodiversity

Impact mechanisms

Competition - monopolizing resources

Likelihood of entry/control

Highly likely to be transported internationally accidentally
Highly likely to be transported internationally deliberately
Difficult to identify/detect as a commodity contaminant
Difficult/costly to control

Uses

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P. pedicellatum is widely used as green fodder for cattle (Skerman and Riveros, 1990; Sinsin, 1993; Cisse et al., 2002; Holou, 2002); however, P. pedicellatum was found to be inferior to sorghum fodder primarily because of lower voluntary intake (Awadhesh et al., 2000). The supplementation of late-harvested forage with cottonseed meal increased intake and digestibility, attributed to greater stimulation of rumen flora as a result of increased availability of energy and nitrogen-providing nutrients (Nianogo et al., 1997). Protein content is 20.50% (Mishra et al., 1996), and cutting at 60-65 days results in a high crude protein (9.06%), high crude fat (2.55%) and low crude fibre (28.95%) contents (Khan et al., 1995). Mean daily dry matter intakes of P. pedicellatum reached 2.175 kg/100 kg bodyweight according to the animal; nitrogen balance is 1.3 g per day, and daily nitrogen excretion in urine is 4.86 g (Jakhmola and Pathak, 1983). The chemical composition of P. pedicellatum plants varied with the phenology (Banerjee and Mandal, 1974; Upadhyay et al., 1978; Jakhmola and Pathak; 1983). Balances of N, Ca and P were all negative. Nutritive value was calculated in terms of total digestible nutrients to be 52.77% for dry matter and 7.95% on fresh weight basis; and corresponding values for digestible crude protein were 3.03 and 0.46% (Banerjee and Mandal, 1974). These data demonstrate the important nutritive value of the species.

In the Sahel, P. pedicellatum is also used as mulch in the rehabilitation of encrusted soil. The biological activity, mainly from termites, in mulched plots was the most important factor in the efficacy of mulching. In the plains of Chhattisgarh, India, the species is used for fuel (Misra, 1958). A mixture of chopped P. pedicellatum straw and clay is also used in the building of houses and straw is used to make mats and for roof thatch; a juice from leaves has medicinal purposes (Poilecot, 1995). P. pedicellatum has also been sown to control soil erosion and to improve the physical and chemical properties of the soil (Kumar and Jena, 1996).

Uses List

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Animal feed, fodder, forage

Fodder/animal feed

Similarities to Other Species/Conditions

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At the subspecies level, P. pedicellatum subsp. pedicellatum is characterised by an involucre surrounding 2-5 spikelets, among which one at least is carried by a pedicel 1.5-3.5 (-5) mm long, whereas P. pedicellatum subsp. unispiculum's involucre surrounds only one spikelet which is carried by one pedicel 0.5-1 (-1.5) mm long. This subspecies is mainly found on coastal and saline sites (Poilecot, 1995). Flowering time of the first subspecies is August-October (December), whereas the second subspecies flowers during October-November. P. pedicellatum may be confused with P. polystachyon and P. purpureum, but is separable by having spikelets pedicelled or in groups of two to five (Holm et al., 1977).

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.

Cultural Control

P. pedicellatum is a serious weed but can be controlled by timely cultivation (Doughton, 1974). Management by grazing at critical times may reduce seed production, but observations indicate that affects are limited.

Mechanical Control

Hand pulling can be effective on young seedling but it is impractical on large plants. Mechanical cutting is used and has an effect on the growth of the species, recorded for the maximization of production of the species as a fodder, with Prasad (1996) noting increased green forage yields higher with 2 cuts (36.2 t) than with 3 (31.1 t) or 4 cuts (29.9 t); and respective seed yields were 0.85, 0.33 and 0.14 t.

Chemical Control

P. pedicellatum has been sucessfully controlled in Australia with glyphosate (McGowan, 1970), and the success of low application rates in no-till situations confirms the significant reduction of the species by judicious timing of spraying. Pre-emergence, spraying soil with trifluralin and nitralin, and bromacil and picloram, prevented germination of P. pedicellatum seed for 5 weeks (Suwunnamek, 1974) and Doughton (1974) found atrazine to be an effective pre-emergent herbicide. When seedlings were 5-10 cm high, diuron, ametryne and linuron were very effective, and when plants were 20-25 cm high, diuron, prometryne, linuron and glyphosate were effective (Suwunnamek, 1974).

Biological Control

No known efforts have been made towards biological control of P. pedicellatum.

References

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Afolayan AJ; Olugbami SS, 1993. Seed germination and emergence of Setaria pallidefusca and Pennisetum pedicellatum (Cyperales: Poaceae) in Nigeria. Revista de Biología Tropical, 41(1):23-26; 10 ref.

Ahmed TD; Papa ISM; Ducousso M, 1998. Arbuscular mycorrhization fungi in the semi-arid areas of Senegal. Eur. J. Soil Biol., 35(2):65-75.

Anon., 1957. Katherine Research Station Progress Report 1946-1958. CSIRO Division of Land Research and Regional Survey. Divisional Report 57/1. Australia: CSIRO.

Awadhesh I; Verma ML; Kishore A, 2000. Comparative feeding value of Dinanath grass and sorghum fodder for crossbred heifers. Indian Journal of Animal Nutrition, 17(4):311-314.

Banerjee GC; Mandal L, 1974. Nutritive value of Pennisetum pedicellatum grass for adult sheep. Indian Veterinary Journal, 51, 9-10: 620-625.

Bhargava KS; Joshi RD; Rishi N, 1971. Indian Phytopathology, 24:119.

Bhaskar RB; Ahmad ST, 1994. Pennisetum pedicellatum a new host of Pyricularia grisea. Indian Phytopathology, 47(3):275

Cadet P; Floret C, 1995. An initial study of fallow periods on the nematode community in the Soudanese Sahelian zone of Senegal. Acta Oecologica, 16(1):7-8.

Chaix G; Marchais L, 1996. Diversity of penicillariam millets (Pennisetum glaucum and Pennisetum purpureum) as for the compatibility between their gynoecia and pollens from some other Poaceae. Euphytica, 88:97-106.

Choubey S; Prasad NK; Bhagat RK, 1997. Suitable grass-legume combination for higher forage production. Journal of Research, Birsa Agricultural University, 9(1):81-83.

Cisse M; Ly I; Nianogo AJ; Sane I; Sawadogo JG; N'Diaye M; Awad C; Fall Y, 2002. Grazing behavior and milk yield of Senegalese Sahel goat. Small Ruminant Research, 43(1):85-95.

Cucousso M, 1991. Importance des symbioses racinaires pour l'utilisation des acacias d'Afrique de l'ouest. Dakar, Sénégal and Nogent-sur-Marne, France: Cirad-Forêt/ISRA, 205p.

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Distribution References

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GISD/IASPMR: Invasive Alien Species Pathway Management Resource and DAISIE European Invasive Alien Species Gateway	https://doi.org/10.5061/dryad.m93f6	Data source for updated system data added to species habitat list.

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Pennisetum pedicellatum (deenanath grass)

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