Perennial ryegrass
(Lolium perenne L.)
| Perennial ryegrass (Lolium perenne L.; also called
English ryegrass) is a temperate (cool-season) perennial grass that is native to Europe, temperate Asia, and North Africa (Jung et al., 1996; Balasko et al., 1995; Walton, 1983). It has been widely distributed to other parts of the world, including North and South America, Europe, New Zealand, and Australia. Both perennial and annual ryegrass (L. multiflorum; also called Italian ryegrass) are important grasses in forage-livestock systems. Mixtures of the two species sometimes are used to increase first season forage yields while establishing a perennial grass stand (Cullen, 1964). Perennial ryegrass is valued for high yield potential, fast establishment, reduced tillage renovation applications, and use on heavy and waterlogged soils. High palatability and digestibility make this species highly valued for use in dairy and sheep forage systems. As a result, it often is the preferred forage grass in temperate regions of the world. In the U.S., perennial ryegrass is used for forage predominately in the coastal northwest, irrigated intermountain valleys of the west, the midwest, and northeast . Description/Taxonomy Perennial ryegrass is a temperate (cool-season) bunchgrass that can behave as an annual, short-lived perennial, or perennial depending on environmental conditions (Stefferud, 1948; Hall, 1992). It resembles annual ryegrass (Lolium multiflorum Lam.), though the collar and blade of perennial ryegrass are more narrow and seeds are awnless . Vegetative Characteristics Leaves of perennial ryegrass are folded in the bud (in contrast to annual ryegrass (Lolium multiflorum L.) in which the leaves are rolled) (Francis, 1912; Nowosad et al., 1936; Stefferud, 1948). Leaf blades are 2 to 6 mm (.08-.24 inches) wide, 5 to 15 cm (2-15 inches) long, sharply taper-pointed, and keeled. Blades are bright green, prominently ridged on the adaxial (upper) surface, and smooth, glossy, and glabrous (hairless) on the abaxial (lower) surface. Leaf margins are slightly scabrous (rough to the touch, covered with minute serrations). Blades increase in size from the first to the seventh leaf on a tiller, although tillers rarely have more than three live leaves at one time (Balasko et al., 1995). Leaf sheaths usually are not keeled, compressed but sometimes almost cylindrical, glabrous, pale green, and reddish at the base (Francis, 1912). Sheaths may be closed or split. The collar is narrow, distinct, glabrous, and yellowish to whitish-green. Auricles are small, soft, and claw-like. The ligule is thin-membranous, from 0.5 to 2.5 mm (.02-.1 inches), obtuse (rounded at the apex), and may be toothed near the apex (Nowosad et al., 1936). The shallow root system is highly branched and produces adventitious roots from the basal nodes of tillers. Perennial ryegrass has no rhizomes or stolons. It will, however, produce a dense and closely knit sward or turf with high plant densities and proper management (Spedding and Diekmahns, 1972). Reproductive Characteristics Flowering stems (culms) are 30 to 100 cm (3 feet) in height depending on cultivar, moisture, and site conditions (Hitchcock, 1950). The stem base commonly is reddish. The spike-type inflorescence is up to 30 cm (12 inches) long, has 5 to 40 alternate, sessile (bractless), awnless spikelets (in contrast to annual ryegrass which is awned) that are positioned edgewise to the rachis (primary stem of the inflorescence). Spikelets contain 3 to 10 florets, with two glumes present in the terminal spikelet and with the inner glume missing in the other spikelets. Seeds of perennial ryegrass are awnless and range from 465,000 to 595,000 seeds per kg (1,025,000-1,311,000 per lbs) (Effenberger, 1993). This compares with a range of 395,000 to 445,000 (871,000-981,000 per lbs) for annual ryegrass and an average of 338,000 seeds per kg (745,000 per lbs) for intermediate ryegrass. Perennial ryegrass seed length is 5 to 8 mm (.2-.32 inches) and width at the midpoint is 1 to 1.5 mm (.04-.06 inches) (Spedding and Diekmahns, 1972). Breeding and Development There are many important perennial ryegrass cultivars and all are reproduced by seed. Many types of ryegrasses exist because of self-incompatibility and crosses with other Lolium and Festuca species (Riewe and Mondart, 1985). Persistence of perennial x annual hybrids generally is intermediate between annual and perennial cultivars. As a result, these crosses are called short-rotation ryegrasses. There are both diploid and tetraploid forage-type cultivars. Tetraploids have fewer but larger tillers with wider leaves, resulting in more open sods. Both the seed and seedlings of tetraploids are larger, but growth rate following emergence is greater for diploids. Tetraploids typically are less persistent than diploids (Balasko et al., 1995). Cultivars Including both forage and turf types, there are more than 100 perennial ryegrass cultivars listed in the "Grass Varieties of the US" document (Alderson and Sharp, 1995). There are more than 500 named cultivars are in the 1996 OECD list of cultivars (OECD, 1996). Information on cultivars also is available from the Oregon Ryegrass Growers Seed Commission and through the Germplasm Resources Information Network (GRIN; URL: http://www.ars-grin.gov/). Perennial ryegrass cultivars are grouped into three maturity categories; early, intermediate, and late. This is helpful, but groupings are somewhat arbitrary, since phenological development is a continuum and is affected by temperature and photoperiod (Cooper, 1957; Silsbury, 1965). Thus, without common criteria and standardized reporting procedures for maturity categories, there is substantial overlap. Recommendations Field trials for perennial ryegrass cultivar evaluation trials are conducted in various U.S. and international research and extension centers. These trials include yield and/or quality evaluation, based on local information needs. Consult your local Extension Service for specific recommendations for cultivars that have performed well in your area. Adaptation Area Perennial ryegrass is best adapted to cool, moist climates (Hannaway and McGuire, 1981; Hall, 1992; Balasko et al., 1995; Jung et al., 1996). It grows well in early spring and fall, but during the hot summer months it becomes dormant. Even with irrigation or abundant summer rainfall, perennial ryegrass production suffers due to high temperature stress when day temperatures exceed 30° C (86° F) and night temperatures exceed 25° C (77° F). It is more sensitive to temperature extremes and drought than annual ryegrass. Perennial ryegrass is less winter-hardy than orchardgrass (Dactylis glomerata L.) and tall fescue (Festuca arundinacea Schreb.) and less drought tolerant than smooth bromegrass (Bromus inermis Leyss). Studies in Wisconsin (Casler and Walgenbach; 1990; Novy et al., 1995), however, suggest that perennial ryegrass is able to survive severe climates, even where snow cover is unreliable. Optimum growth occurs between 20 and 25° C (68-77° F) (Spedding and Diekmahns, 1972). Perennial ryegrass grows best on fertile, well-drained soils but has a wide range of soil adaptability. It is tolerant of poorly-drained soils and frequently is used in these environments (Balasko et al., 1995). It tolerates both acid and alkaline soils, with a pH range of approximately 5.0 to 8.3 (Cropper, 1996; Miller and Reetz, 1995; Hall, 1992). Similar to tall fescue, perennial ryegrass is adapted to shade in the warmer portions of a cool, humid climate where winter kill is not a problem (Beard, 1973). In the U.S., primary adaptation and usage of perennial ryegrass for forage is in the Pacific Northwest, though there is considerable use in irrigated intermountain valleys, the midwest, and the northeast (Figure 1). Estimated perennial ryegrass forage production was provided by Balasko et al. (1995) at 50,000 ha each for the Pacific Northwest and northeastern areas. For the midwest, the estimate is 8,000 to 10,000 ha (20,000-25,000 acres) (S. Johnson, 1997, personal communication). Perennial ryegrass is less persistent than other perennial temperate grass species such as orchardgrass, tall fescue, timothy (Phleum pratense L.), smooth bromegrass, and Kentucky bluegrass (Poa pratensis L.) (Balasko et al., 1995; Hall, 1992). Despite these limitations, perennial ryegrass is the pasture grass of choice for areas with wet, mild-temperate climates like the Pacific northwest and northeast U.S., Great Britain, and New Zealand. Management Establishment In adapted areas, perennial ryegrass can be seeded in spring or late summer. In addition, it may be fall-seeded in areas with mild winters. Seeding depth should be between 0.5 and 1.25 cm (0.25-0.5 inches) (Hall, 1992; Balasko et al., 1995). Recommended seeding rates on a clean, well-prepared seedbed are 18 to 24 kg ha-¹ (15-20 lbs/a) in pure stands and 12 to 18 kg ha-¹ (10-15 lbs/a) in mixtures with legumes. When seeding with a no-till drill or surface seeding, seeding rates should be increased up to 45 kg ha-¹ (40 lbs/a) and the existing sod should be mowed or grazed short to reduce competition (Fransen and Chaney, 1996). Fertility and pH Requirements Perennial ryegrass requires high fertility levels for good production. Fertilization should be based on a soil test. Perennial ryegrass will grow on soils with pH of 5 to 8, but forage production is best at pH of 6 to 7 (Miller and Reetz, 1995). Consult your local Extension Service for specific fertilization and liming rates (Hart et al., 1996a; Hall, 1992). Perennial ryegrass is very responsive to N, with maximum yield attained between 600 and 1,200 kg N ha-¹ (535-1070 lbs N/a) per year (Whitehead, 1995; Morrison et al., 1980). Typically there is an almost linear increase in yield of between 20 and 30 kg (44-66 lbs) dry matter per kg N, until the rate of application is between 250 and 400 kg N ha-¹ (223-356 lbs N/acre) per year. At higher rates, the response per kg of additional fertilizer N declines until the maximum yield is attained. Applications of total yearly N should be split as evenly as possibly to reflect the continuing need for nitrogen throughout the growing season. The first application is provided at the beginning of the season and the others after each harvest except the last (Whitehead, 1995; Wedin, 1974). This pattern of application produces a greater annual yield and better quality forage than does a single, early spring application (Castle and Reid, 1968). T-Sum 200 In mild climates, the initial N application can be made when pasture plants start to grow in mid to late winter (Pirelli, 1996). Timing initial fertilization with the start of grass growth has been assisted by using a thermal time method called T-Sum 200 (Kowalenko et al., 1989). The first application of N is made when 200 heat units have accumulated. Heat units are the average of high and low temperature in degrees C (maximum temperature plus the minimum temperature divided by 2) summed beginning with January 1. (The formula for converting Fahrenheit to centigrade is: degrees C = [(degrees F - 32) x 0.556]). Subsequent fertilizer applications are made following each grazing or mechanical harvest. Optimum Economic Rates Typically, economical levels of annual N fertilizer rates have been suggested to be in the range of 160 kg N ha-¹ yr-¹ (143 lbs N/a) (Balasko, 1995). However, economically optimum rates of fertilizer application (the rate at which the marginal increase in the value of the forage is equal to the marginal increase in the cost of fertilizer) can be estimated for individual sites by developing a response curve which averages results over several years. Although these are not precise estimates due to the variability of weather and livestock systems, they can serve as a useful guide. In the United Kingdom a minimum response of 5.7 kg DM per kg N was required for an economic return, whereas in the Netherlands 7.5 kg dry matter (DM) per kg N was necessary (Whitehead, 1995; Reid, 1970, Prins et al., 1980; van der Meer and van Uum-van Lohuyzen, 1986). A different approach, suggested by Morrison et al. (1980), determined the rate for producing a marginal response was 10 kg DM per kg N. In England and Wales, this optimum rate approach produced 90% of the maximum yield while using only 60% of the fertilizer. A few studies have determined optimum N fertilizer rates based on milk or meat production. This strategy calculates the optimum rate of nitrogen fertilizer based on the price received for the milk or meat and the cost of fertilizer N (Whitehead, 1995; Gordon, 1974; Holmes, 1968). For milk production, this approach shows an almost linear increase up to a fertilizer rate of 450 kg N ha-¹ yr-¹ (400 lbs N/a), with each kg N yielding about 15 kg (33 lbs) of milk (Whitehead, 1995). For beef production, targeting liveweight gain of 1,220 kg ha-¹ (1088 lbs/a) from fertilizer N rates of 300 kg N/ha (268 lbs N/a) per year suggests that 2 kg (4.4 lbs) liveweight gain per kg of fertilizer N is attainable by young animals (Whitehead, 1995; van Burg et al., 1981). Legume Nitrogen Fixation The amount of nitrogen fixed by legumes growing in combination with grasses depends on the legume species and the environment in which it is growing (Joost, 1996). When grown in the presence of available inorganic soil N, legume biological N2 fixation is decreased (Heichel, 1985; Miller and Heichel, 1995). Fixation is decreased by reducing the nitrogenase enzyme activity and by decreasing the formation of nodules (Eardly et al., 1985; Shuler and Hannaway, 1993). In grass-legume mixtures, inorganic N also increases the competition from the grass, which reduces N2 fixation per unit area. High levels of N2 fixation rates per unit area of white clover-grass can be maintained only under conditions of very low soil mineral N levels, which limit grass competitiveness (West and Mallarino, 1996). Thus, white clover (Trifolium repens L.) - perennial ryegrass communities dependent on symbiotic fixation as the N source are likely to be in chronic N deficiency and below their potential for pasture yield potential (Ball and Crush, 1985). The overall impact of applying fertilizer N to a well-managed grass and white clover sward is to reduce N2 fixation. Moderate rates of N (up to 80 kg ha-¹, 71 lbs/a) typically reduce N2 fixation about one half (Whitehead, 1995; Cowling, 1982; Crush et al., 1982). Higher rates (150-200 kg ha-¹ 133-178 lbs/a) are likely to eliminate N2 fixation entirely (Eardly et al., 1985). The size of the effect is influenced by factors such as the time of year of fertilizer application, the frequency of defoliation, soil moisture and other nutrients, and the form of fertilizer N. Frequent defoliation minimizes the effect by reducing the competition of the grass. In dry areas, irrigation can offset some of the effect, presumably by diluting the inorganic nitrogen in the vicinity of the nodules, encouraging rapid growth, and maintaining available energy supplies for fixation. Manure, urine, and less acid-forming types of N fertilizer minimize decreases in N2 fixation (Moloney and Murphy, 1963; Murphy et al., 1986). Thus, accommodating the sometimes competing objectives of high yields, high quality forage, optimizing N2 fixation by forage legumes, and maximizing the recycling of animal manures and municipal biosolids requires a balancing of fertility requirements and harvest/grazing management. Meeting but not exceeding soil, plant, and animal needs is a continual adjustment process. Developmental Physiology In addition to defoliation height and plant energy reserves, regrowth of perennial grasses is affected by its developmental physiology. The location and activity of meristems within the grass canopy is very important. A large pool of active meristems is necessary to capitalize on stored energy and current photosynthate to rapidly replace photosynthesizing leaf area. The ontogeny (seasonal development) of a perennial grass tiller can be divided into 4 growth periods; vegetative, elongation, reproductive, and seed ripening (Moore et al., 1991). During vegetative development, leaf growth and development occur. Stem internodes are differentiated but do not elongate. As long as the tiller remains vegetative, leaves continue to be produced. Reproductive growth (floral initiation) is triggered in vernalized tillers by exposure to lengthening days during spring. Tiller internodes begin to elongate and raise the growing point to a vulnerable height. Clipping or grazing below the growing point at the early-jointing stage will cause tiller death (because there is no regrowth meristem) and poor regrowth (because basal buds are not yet ready to re-initiate growth). Management Implications Defoliation management during vegetative growth should assure high quantities of high quality forage and rapid regrowth. This can be achieved by allowing swards to attain a height of 10 to 25 cm (4-10 inches) prior to grazing not shorter than 2.5 cm (1 inch) (6 cm [2.4 inches] for mechanical harvest). When plants enter the reproductive growth phase of internode elongation (early-jointing stage), defoliation management should avoid removal of the elevated growing points until after heading. This will assure rapid regrowth of basal buds forming new leaf producing tillers. Fertilization with N (50 kg ha-¹, 45 lbs a-) following each harvest cycle will assure rapid regrowth of leaves and roots. Persistence Cutting and grazing management affect stand persistence of many forage species, including perennial ryegrass. Repeated harvesting without allowing replenishment of storage carbohydrates will reduce stand persistence (Langer, 1990) and reduce regrowth rates (Fulkerson and Slack, 1994). (Refer to the Defoliation section for a more complete description of regrowth and persistence determinants.) The presence of the fungal endophyte (Acremonium lolii Latch, Christensen & Samuels) imparts insect resistance which improves persistence in some areas (Cunningham et al., 1993). Toxic metabolites produced by the plant and endophyte in their symbiotic relationship, however, cause animal health problems. (For a description of this problem, refer to the Fungal Endophyte portion of the Animal Health/Forage Antiquality Issues section.) Frosted Forage Perennial ryegrass is susceptible to temporary, and perhaps permanent damage if utilized in freezing weather or when frosted (Balasko et al., 1995). Livestock (and human) traffic should be prevented on frosted or frozen plants. Conservation, Wildlife, and Turf Uses Soil Conservation Perennial ryegrass, like other grasses, is well suited to many different soil conservation practices (CAST, 1986). Its extensive, shallow, fibrous root system makes it an effective species for reducing surface soil erosion. Perennial ryegrass is recommended as a fast starting component in mixtures, providing rapid cover and then allowing longer-lived or more winter hardy species to become established [i.e. bentgrass (Agrostis stolonifera L.), Canada bluegrass (Poa compressa L.), lovegrass (Erogrostis spp.), Kentucky bluegrass, and fine fescues (Festuca spp.)]. In its adaptation range, perennial ryegrass also is seeded alone to provide excellent soil erosion protection (Fransen and Chaney, 1996). Turf The "Green Industry," including home lawns and golf courses is estimated at over 20 billion dollars per year in the U.S. economy (Dubel, 1959). Use of perennial ryegrass for turf has increased in recent years with selection of more dense and persistent turf types. It is one of the most versatile of all turfgrass species. For turf, perennial ryegrass is used alone or in combination with other grasses. Significant disease problems and limited cold and heat tolerance, however, limit its persistence and zone of adaptation. For the southern region of the U.S., perennial ryegrass's intolerance to high temperature has become an advantage; it is used to overseed dormant bermudagrass (Cynodon dactylon L.) on Southern lawns and sports fields during the winter months. The perennial ryegrass thins and often dies during hot spring and summer weather, allowing the transition to bermudagrass turf thus maintaining an active surface suitable for golf and other sports (Beard, 1982). Recent improvements in turf cultivars include improved disease resistance, high temperature tolerance, and darker green color. European evaluation trials include tolerance to close mowing and traffic (S.W. Johnson, 1996, personal communication). One caution here for forage use, however, is that "turf-type" cultivars of perennial ryegrass often have a fungal endophyte added for increased pest resistance and persistence (Funk and Clarke, 1989). These endophyte-infected cultivars should be used with caution, if at all, for livestock feed due to the presence of toxins (primarily lolitrim b and ergovaline). (Refer to the Fungal Endophyte portion of the Animal Health/Forage Antiquality Issues section.) Diseases and Insect Pests Diseases In humid climates, perennial ryegrass is susceptible to ergot (Claviceps purpurea Tul.) which is toxic to livestock and to stripe smut (Ustilago striiformis (West.) Niessl.) which can cause grass to be unpalatable. Many cultivars are susceptible to leaf spots (Drechslera spp.), fusarium (Fusarium spp.), brown blight (Drechslera siccans), and other fungus diseases in hot, humid climates. Most varieties also are susceptible to snow molds (Typhus spp., Fusarium spp., and Sclerotinia spp.) and many are susceptible to mildews of various sorts including powdery mildew (Erysiphe graminis DC. Ex Merat.) (Braverman et al., 1986). In the northeastern and northwestern sections of the U.S., crown rust caused by Puccinia coronata Corda, Stem rust caused by P. graminis subsp. graminicola Z. Urban, bacterial wilt caused by Xanthomonas campestris pv. Graminis (Egli, Goto & Schmidt), and Drechslera (Helminthosporium) spp. can be problems with perennial ryegrass depending on weather conditions and cultivar susceptibility (Jung et al., 1996). Stem rust often is a problem in late spring and early summer, especially if forage is allowed to accumulate (S. Bittman, 1996, personal communication). Stem and crown rust occur in late summer and early fall. Although rust is not toxic to livestock, it can affect palatability. For horses especially, the spores from rusts and smuts can be a significant respiratory problem. High fertility and harvesting the accumulated forage reduce rust problems. For turf and grass seed production, chemical control measures are available (Pscheidt, 1996). Most, however, are not registered for forage use. Insects Grass grub (Costyletra spp.) is an important pest of ryegrass (Potter and Braman, 1991). Grub larvae eat ryegrass roots, rendering the plant more susceptible to drought (Jung et al., 1996). In New Zealand, the Argentine stem weevil is a major perennial ryegrass problem (Balasko et al., 1995). Perennial ryegrass is resistant to this weevil (and other pests) if the grass is infected by the fungal endophyte (Popay et al., 1990). Presence of the endophyte, however, is linked to the occurrence of a neurological disorder in livestock known as ryegrass staggers. (Refer to the Fungal Endophyte portion of the Animal health/Forage Antiquality Issues section.) For turf applications, the chinchbug and sod webworm are additional pest problems (Fisher et al., 1996). The European cranefly (Tipula paludosa) is of local importance in the Pacific Northwest (Fisher et al., 1996). Chemical control measures are available (Table 3), but seldom economical. Typically, pastures are reseeded with renovation techniques when stands are lost to the European cranefly. Seed Production Oregon is the world's major producer of cool-season forage and turf grass seed. Mild and moist winters with dry summers favoring seed development and harvest make the Oregon's Willamette Valley an ideal place to produce high quality seed. This small region produces almost two-thirds of the total U.S. seed production of cool-season grasses. Nearly all of the perennial ryegrass seed in the U.S. is grown in Oregon. In 1995, nearly 57000 ha of perennial ryegrass was harvested for seed in Oregon (Young, 1996). Average seed yield is 1300 to 1500 kg ha-¹ (1160-1338 lbs/a). Most seed produced in the USA is of turf-type cultivars. Over 55 percent of Oregon's production of perennial ryegrass was certified in 1995. Oregon produced 96 percent of all perennial ryegrass acres applied for certification through the Association of Official Seed Certifying Agencies in 1995 (AOSCA, 1995). The AOSCA summary reports total USA, Canada, Argentina, and New Zealand certified production. A vernalization period of low temperatures is necessary before photoperiodic (>13 h) floral initiation for most perennial ryegrass cultivars (Silsbury, 1965). An obligate vernalization requirement of at least 2 wk at 4°C (39.2°F) or lower was reported by Cooper (1960). In contrast, Mediterranean types do not require cold temperatures and initiate inflorescences at daylengths of 9 to 10 h (Balasko et al., 1995). Perennial ryegrass produces seed once per year in late spring in the northeastern and Pacific northwestern U.S. It is self-incompatible and will readily cross-pollinate (Balasko et al., 1995). References 1.Albrecht, K.A., and M.H. Hall. 1995. Hay and Silage Management. p. 155-162. In Robert F. Barnes, Darrell A. Miller, and C. J. Nelson. (eds.) Forages. Vol. 1. An Introduction to Grassland Agriculture. Iowa State Univ. Press. Ames, IA. 2.Alderson, J., and W.C. Sharp. 1995. Grass Varieties in the United States. USDA/SCS. Ag. Handbook No. 170. USDA, Washington, DC. Association of Official Seed Certifying Agencies (AOSCA). 1995. Acres applied for certification on 1995 by seed certifying agencies. Production Publication No. 49. 3.Balasko, J.A., G.W. Evers, and R.W. Duell. 1995. Bluegrasses, ryegrasses, and bentgrasses. p. 357-372. In R.F. Barnes, D.A. Miller, and C.J. Nelson. (eds.) Forages. Vol. 1. An Introduction to grassland Agriculture. 5th ed. Iowa State Univ. Press. Ames, IA. 4.Ball, D.M, C.S. Hoveland, and G.D. Lacefield. 1991. Southern Forages. Potash and Phosphate Institute. Williams Print. Co., Atlanta, GA. 5.Ball, P.R., and J.R. Crush. 1985. Prospects for increasing symbiotic nitrogen fixation in temperate grasslands. p. 56-62. In Proc. 15th Intl. Grassl. Congr., Kyoto, Japan. 6.Beard, J.B. 1982. p. 151-155. In Turfgrass management for golf courses. U.S. Golf Assoc. Far Hills, NJ. 7.Beard, J.B. 1973. Turfgrass: Science and Culture. Prentice-Hall, Inc., Englewood Cliffs, NJ. 8.Braverman, S.W., F.L. Lukezic, K.E. Zeiders, and J.B. Wilson. 1986. Diseases of forage grasses in humid temperate zones. Pennsylvania State Univ. Agric. Exp. Stn., Bull. 859. 9.Casler, M.D., and R.P. Walgenbach. 1990. Ground cover potential of forage grass cultivars mixed with alfalfa at divergent locations. Crop Sci. 30:825-831. 10.Castle, M.E., and D. Reid. 1968. The effects of single compared with split applications of fertilizer nitrogen on the yield and seasonal production of a pure grass sward. J. Agric. Sci. (Camb.) 70:383-389. 11.Cheeke, P.R. 1997. Natural Toxicants in Feeds, Forages, and Poisonous Plants. Interstate Pub., Danville, IL. 12.Clay, Keith. 1988. Fungal Endophytes of Grasses: a Defensive Mutualism Between Plants and Fungi. Ecology 69(1):10-16. 13.Coker, E.G., J.E. Hall, C.H. Carlton-Smith, and R.D. Davis. 1987. Field investigations into the manurial value of liquid undigested sewage sludge when applied to grassland. J. Agric. Sci. (Camb.). 109:479-494. 14.Cooper, J.P. 1957. Developmental analysis of populations in the cereals and herbage grasses. II. Response to low-temperature vernalization. J. Agric. Sci. 49:361-383. 15.Council for Agricultural Science and Technology. 1986. Forages: Resources for the Future. Rep. No. 108. Ames, IA. 16.Cowling, D.W. 1982. Biological nitrogen fixation and grassland production in the United Kingdom. Philosophical Trans. of the Royal Soc., London, B 296:397-404. 17.Cropper, J. 1997. Forage Species Suitability Based on Soil pH. Table 4. In Nutritional Range and Pasture Handbook. Natural Resource Conservation Service, Washington, DC (in press). 18.Crush, J.R., G.P. Cosgrove, and R.W. Brougham. 1982. The effect of nitrogen fertiliser on clover nitrogen fixation in an intensively grazed Manawatu pasture. N.Z. J. of Exp. Agric. 10:395-399. 19.Cullen, N.A. 1964. Species Competition in Establishing Swards: Suppression Effects of Ryegrass on Establishment and Production of Associated Grasses and Clovers. N.Z. J. of Agric. Res. 7:678-693. 20.Cunningham, L., and G. Hanson. 1993. Farmer Profitability with Intensive Rotational Stocking: Better Grazing Management for Pastures. Natural Resource Conservation Service Spec. Pub. 21.Cunningham, P.J., and W.J. Hartley. 1959. Ryegrass staggers. N.Z. Vet. J. 7:1-7. 22.Cunningham, P.J., J.Z. Foot, and K.F.M. Reed. 1993. Perennial ryegrass (Lolium perenne) endophyte (Acremonium lolii) relationships: the Australian experience. In R. Joost and S. Quisenberry (eds.) Agric., Ecosys. and Env. 44:157-168. 23.Decker, A.M., and T.H. Taylor. 1985. Establishment of New Seedings and Renovation of Old Sods. p. 288-303. In M.E. Heath, R.F. Barnes, and D.S. Metcalfe (eds.) Forages: The Science of Grassland Agriculture. 4th ed. Iowa State Univ. Press. Ames, IA. 24.Duble, R.L. 1989. Southern Turfgrasses: Their Management and Use. TexScape, Inc., College Station, TX. 25.Eardly, B.D., D.B. Hannaway, and P.J. Bottomley. 1985. Nitrogen nutrition and yield of seedling alfalfa as affected by ammonium nitrate fertilization. Agron. J. 77:57-62. 26.Edmond, D.B. 1966. The influence of animal treading on pasture growth. p. 453-458. In A.G.G. Hill (ed.) Proc. 10th Int. Grassl. Congr., Helsinki, Finland. 7-16 July, Finn. Grassl. Assoc., Helsinki, Finland. Effenberger, J. 1993. Rules for Testing Seeds. J. Seed Tech. 16(3). 27.Fisher, G., J. DeAngelis, C. Baird, R. Stoltz, L. Sandvol, A. Antonelli, E. Beers, and D. Mayer. 1996. Pacific Northwest Insect Control Handbook. Oregon State Univ. Ext. Service, Corvallis, OR. 28.Francis (Baker), M.E. 1912. The Book of Grasses. Doubleday, Page & Co., Garden City, NY. 29.Fransen, S.C. 1993. Viewing Perennial Grasses for Pasture and Silage - a Perspective from the Field. p. 24-37. In: Proc. of the 1993 Northwest and Lower Columbia Dairy Shortcourses. Washington State Univ. Spec. Pub. 30.Fransen, S.C. 1994. Forage yield and quality of ryegrass with intensive harvesting. Agron. Abstr. p. 194. 31.Fransen, S., and M. Chaney. 1997. Pasture and hayland renovation for western Washington and Oregon. Tech. Bull. Washington State Univ. Pullman, WA. (in press) 32.Fulkerson, W.J. 1994. Effect of redefoliation on the regrowth and water soluble carbohydrate content of Lolium perenne. Aust. J. Agri. Res. 45:1809-1815. 33.Fulkerson, W.J., and K. Slack. 1994. Leaf number as a criterion for determining defoliation time for Lolium perenne. 1. Effect of water soluble carbohydrates and senescence. Grass and Forage Sci. 49:373-37. 34.Fulkerson, W.J., and K. Slack. 1995. Leaf number as a criterion for determining defoliation time for Lolium perenne. 2. Effect on defoliation frequency and height. Grass and Forage Sci. 50:16-20. 35.Fulkerson, W.J., K. Slack, and K.F. Lowe. 1994. Variation in the response of Lolium genotypes to defoliation. Aust. J. Agric. Res. 45:1309-1317. 36.Funk, C.R., and B.B. Clarke. 1989. Turfgrass breeding with special reference to turf-type perennial ryegrass, tall fescue, and endophytes. P. 3-10. In: Proc. of the 6th Int'l. Turfgrass Res. Conf. July 31-August 5, Tokyo, Japan. 37.Gallagher, R.T., A.G. Campbell, A.D. Hawkes, P.T. Holland, D.A. McGaveston, and E.A. Pansier. 1982. Ryegrass staggers: The presence of lolitrem neurotoxins in perennial ryegrass seed. N.Z. Vet. J. 30:183-184. 38.Gallagher, R.T., E.P. White, and P.H. Mortimer. 1981. Ryegrass staggers: Isolation of potent neurotoxins lolitrem A and lolitrem B from staggers-producing pastures. N.Z. Vet. J. 29:189-190. 39.Gordon, F.J. 1974. The use of fertilisers on grassland for milk production. Proc. of the Fert. Soc. London. 142:14-27. 40.Hall, M.H. 1992. Ryegrass. Pennsylvania State Univ. Coop. Ext. Service Agron. Facts 19. 41.Hannaway, D.B., L.P. Bush, and E. Leggett. 1980. Plant Nutrition and Hypomagnesemia. Univ. of Kentucky Agric. Exp. Stn. Bull. 716. 42.Hannaway, D.B., and W.S. McGuire. 1981. Growing perennial ryegrass for forage. FS 262. Oregon State Univ. Ext. Service. Corvallis, OR. 43.Hansen, D.E., R.D. McCoy, O.R. Hedstrom, S.P. Snyder, and P.J. Ballerstedt. 1994. Photosensitization associated with exposure to Pithomyces chartarum in lambs. J. Amer. Vet. Med. Assoc. 204:1668-1671. 44.Hart, J., L. Cannon, and G. Pirelli. 1996a. Fertilizer guide for western Oregon and western Washington pastures. FG 63. Oregon State Univ. Ext. Service, Corvallis, OR. 45.Hart, J., M. Gangwer, M. Graham, and E. Marx. 1996b. Dairy manure as a fertilizer source. EM 8586. Oregon State Ext. Service. Corvallis, OR. 46.Hart, J., E.S. Marx, and M. Gangwer. 1996c. Manure Application Rates for Forage Production. EM 8585. Oregon State Univ. Ext. Service, Corvallis, OR. 47.Heichel, G.H., and K.I. Henjum. 1991. Dinitrogen fixtation, nitrogen transfer, and productivity of forage legume-grass communities. Crop Sci. 31:202-208. 48.Hitchcock, A.S. 1950. Manual of the Grasses of the United States. U.S. Department of Agriculture Misc. Pub. No. 200. U.S. Gov. Print. Office, Washington, DC. 49.Hodgson, J. 1990. Grazing Management; Science into Practice. Longman Scientific & Technical. Essex, England. 50.Holmes, W. 1968. The use of nitrogen in the management of pasture for cattle. Herbage Abstr. 38:265-277. 51.Joost, R.E. 1996. Nutrient cycling in forage systems. p. 1-11. In R.E. Joost, and C.A. Roberts (eds.) Nutrient Cycling in Forage Systems. Potash & Phosphate Institute. Norcross, GA. 52.Joost, R.E., and C.A. Roberts. (eds.) 1996. Nitrogen Cycling in Forage ystems. Proc. of a Symposium. Columbia, MO. Pub. by Potash and Phosphate Inst. and Found. for Agron. Res., Manhattan, KS. 53.Jung, G.A., R.E. Kocker, C.F. Gross, C.C. Berg, and O.L. Bennett. 1976. Nonstructural carbohydrates in the spring herbage of temperate grasses. Crop Sci. 16:353-359. 54.Jung, G.A., A.J.P. van Wijk, W.F. Hunt, and C.E. Watson. 1996. Ryegrasses. p. 605-641. In L.E. Moser, et al. (eds.) Cool-Season Forage Grasses. ASA Monograph 34. ASA, Madison, WI. 55.Kowalenko, C.G., S. Freyman, D.L. Bates, and N.E. Holbek. 1989. An evaluation of the T-sum method for efficient timing of spring nitrogen application on forage production in South Coastal British Columbia. Can. J. Plant Sci. 69:1179-1192. 56.Kvasnicka, B., and L.J. Krysl. 1994. Grass Tetany in Beef Cattle. CL 627. Cow-Calf Management Guide & Cattle Producer's Library. 2nd ed. Univ. of Idaho Coop. Ext. System, Moscow, ID. 57.Langer, R.H.M. 1990. Pastures: Their ecology and management. Oxford Univ. Press. Auckland, New Zealand. 58.Miller, D.A., and G.H. Heichel. 1995. Nutrient metabolism and nitrogen fixation. p. 45-53. In R.F. Barnes, D.A. Miller, and C.J. Nelson. (eds.) Forages. Vol. 1. An Introduction to Grassland Agriculture. 5th ed. Iowa State Univ. Press. Ames, IA. 59.Miller, D.A., and H.F. Reetz, Jr. 1995. Forage Fertilization. p. 71-87. In R.F. Barnes, D.A. Miller, and C.J. Nelson. (eds.) Forages. Vol. 1. An Introduction to Grassland Agriculture. 5th ed. Iowa State Univ. Press. Ames, IA. 60.Moloney, D., and W.E. Murphy. 1963. The effect of different levels of nitrogen on a grass clover sward under grazing conditions. I. Animal output. Irish J. of Agric. Res. 2:1-12. 61.Morris, C.A., N.R. Towers, C. Wesselink, and M. Wheeler. 1994. Selection for or Against Facial Eczema Susceptibility in Sheep, Proc. N.Z. Soc. Animal Production 54:263-266. 62.Morrison, J., M.V. Jackson, and P.E. Sparrow. 1980. The response of perennial ryegrass to fertilizer nitrogen in relation to climate and soil. Tech. Rep. 27. Grassland Res. Inst. Hurley, England. 63.Mortimer, P.H. 1983. Ryegrass staggers: clinical, pathological and aetiological aspects. Proc. New Zealand Grassland Assoc. 44:230-233. 64.Mortimer, P.H., and D.C. Dalton. 1981. Facial Eczema: Causes, Effects, and Treatment, N.Z. Ministry of Agriculture and Fisheries, Aglink Pub. #FPP493. 65.Mortimer, P.H., L.R. Fletcher, M.E. Di Menna, I.C. Harvey, G.S. Smith, G.M. Barker, R.T. Gallagher, and E.P. White. 1982. Recent advances in ryegrass staggers. Proc. Ruakura Farmers Conf. 34:71-74. 66.Munday, R., A.M. Thompson, E.A. Fowke, C. Wesselink, R.M. McDonald, and A.J. Ford. 1993. A Slow Release Device for Facial Eczema Control in Sheep, N.Z. Vet. J. 41:220 (abstr). 67.Murphy, P.M., S. Turner, and M. Murphy. 1986. Effect of spring applied urea and calcium ammonium nitrate on white clover (Trifolium repens) performance in a grazed ryegrass-clover pasture. Irish J. of Agric. Res. 25:251-259. 68.National Research Council. 1996. Nutrient Requirements of Domestic Animals Series. Nutrient Requirements of Beef Cattle, 7th Rev. Ed. National Academy Press, Washington, DC. 69.Novy, E.M., M.D. Casler, and R.R. Hill Jr. 1995. Selection for persistence of tetrapolid ryegrasses and festulolium in a mixture with perennial legumes. Crop Sci. 35:1046-1051. 70.Nowosad, F.S., D.E. Newton Swales, and W.G. Dore. 1936. The identification of certain native and naturalized hay and pasture species by their vegetative characters. Pasture Studies IX. McGill Univ. Tech. Bull. No. 16. 71.OECD. 1996. List of cultivars Eligible for Certification. Organization for Economic Co-operation and Development. Paris, France. Pirelli, Gene. 1996. Timing of nitrogen fertilizer for western Oregon pastures. Oregon State Univ. Ext. Service Pub. 72.Popay, A.J., R.A. Prestige, D.D. Rowan, and J.J. Dymock. 1990. The role of Acremonium lolii mycotoxins in insect resistance of perennial ryegrass (Lolium perenne). p. 44-48. In S.S. Quisenberry and R.E. Joost (eds.) Proc. Int. Symp. Acremonium-Grass Interactions. Baton Rouge: Louisiana Agric. Exp. Stn. 73.Potter, D.A., and S.K. Braman. 1991. Ecology and management of turfgrass insects. p. 383-406. In T.E. Mittler et al. (ed.) Annual review of entomology. Annu. Rev. Inc., Palo Alto, CA. 74.Prins, W.J. and P.J.M. Snijders. 1987. Negative effects of animal manures on grassland due to surface spreading and injection. p. 129-135. In H.G. van der Meer, R.J. Unwin, T.A. Van Dijk, and G.C. Ennik (eds.) Animal Manure on Grassland and Forage Crops: Fertilizer or Waste? Martinus Nijhoff, Dordrecht. 75.Prins, W.H., P.F.J. van Burg, and H. Wieling. 1980. The seasonal response of grassland to nitrogen at different intensities of nitrogen fertilization, with special reference to methods of response measurements. p. 35-49. In W.H. Prins and G.H. Arnold (eds.) The Role of Nitrogen in Intensive Grassland Production. PUDOC, Wageningen, The Netherlands. 76.Pscheidt, J.W. 1996. Pacific Northwest Plant Disease Control Handbook. Oregon State Univ. Ext. Service. Corvallis, OR. (Also available as "An On-line Guide" [http://www.orst.edu/dept/botany/epp/guide/index.html]) 77.Pysher, D., and S. Fales. 1992. Production and quality of selected cool-season grasses under intensive rotational grazing by dairy cattle. p. 32-36. In W. Faw (ed.) Proc. Amer. Forage and Grassl. Conf., Grand Rapids, MI. Redding, V.V., and D.L. Grunes. (eds.) 1979. Grass tetany, ASA Spec. Publ. 35. ASA, Madison, WI. 78.Reid, D. 1970. The effects of a wide range of nitrogen application rates on the yields from perennial ryegrass swards with and without white clover. J. Agric. Sci. (Camb.) 74:227-240. 79.Ries, R.E., and T.J. Svejcar. 1991. The grass seedling: When is it established? J. Range Manage. 44(6):574-576. 80.Riewe, M.E., and C.L. Mondart. 1985. The Ryegrasses. p. 241-246. In M.E. Heath, R.F. Barnes, and D.S. Metcalfe (eds.) Forages: The Science of Grassland Agriculture. 4th ed. Iowa State Univ. Press. Ames, Iowa. 81.Shuler, P.E., and D.B. Hannaway. 1993. The effect of preplant nitrogen and soil temperature on yield and nitrogen accumulation of alfalfa. J. Plant Nutr. 16:373-392. 82.Siegel, M.R. 1993. Acremonium endophytes: our current state of knowledge and future directions for research. In R. Joost and S. Quisenberry (eds.) Agriculture, Ecosystems and Environment. 44:301-321. 83.Silsbury, J.H. 1965. Interrelations in the growth and development of Lolium.. I. Some effects of vernalization on growth and development. Aust. J. Agric. Res. 16:903-913. 84.Smith, J.H., and J.R. Peterson. 1982. Recycling of nitrogen through land application of agricultural, food processing and municipal wastes. p. 791-831. In F.J. Stevenson (ed.) Nitrogen in Agricultural Soils. ASA, Madison, WI. 85.Spedding, C.R.W., and E.D. Diekmahns (eds.) 1972. Grasses and Legumes in British Agriculture. Bull. 49. Commonwealth Bureau of Pastures and Field Crops. Farnham Royal, Bucks, England: Commonwealth Agriculture Bureaux. 86.Stefferud, A. (ed.) 1948. Grass: The Yearbook of Agriculture. USDA, U.S. Gov. Printing Office, Washington, DC. 892 p. 87.Sullivan, D.M., C.G. Cogger, A.I. Bary, S.C. Fransen, and R.G. Stevens. 1994. Predicting Plant-available Nitrogen from Dewatered Biosolids Applications. Agron. Abstr. p. 398. 88.Van Burg, P.F.J., W.H. Prins, D.J. den Boer, and W.J. Sluiman. 1981. Nitrogen and intensification of livestock farming in EEC countries. Proc. of the Fert. Soc., London. 199:1-78. 89.Van der Meer, H.G. and M.G. van Uum-van Lohuyzen. 1986. The relationship between inputs and outputs of nitrogen in intensive grassland systems. p. 1-18. In H.G. van der Meer, J.C. Ryden, and G.C. Ennik (eds.) Nitrogen Fluxes in Intensive Grassland Systems. Martinus Nijhoff, Dordrecht. 90.Vetter, H., G. Steffens, and R. Schropel. 1987. The influence of different processing methods for slurry upon its fertiliser value on grassland. p. 73-86. In H.G. van der Meer, R.J. Unwin, T.A. Van Dijk, and G.C. Ennik (eds.) Animal Manure on Grassland and Forage Crops: Fertilizer or Waste? Martinus Nijhoff, Dordrecht. 91.Walton, P.D. 1983. Production and management of cultivated forages. Reston Pub. Co., Inc. Reston, VA. 92.Wedin, W.F. 1974. Fertilization of cool-season grasses. p. 95-118. In D.A. Mays (ed.) Forage Fertilization. American Society of Agronomy, Madison, WI. 93.West, C.P., and A.P. Mallarino. 1996. Nitrogen transfer from legumes to grasses. p. 167-175. In R.E. Joost, and C.A. Roberts (eds.) Nutrient Cycling in Forage Systems. Potash & Phosphate Institute. Norcross, GA. 94.Whitehead, D.C. 1995. Grassland nitrogen. CAB International, Wallingford, U.K. 95.Wilkinson, S.R., and J.A. Stuedemann. 1979. Tetany hazard of grass as affected by fertilization with nitrogen, potassium and poultry litter and methods of grass tetany prevention. p. 93-121. In V.V. Redding and D.L. Grunes (eds.). Grass Tetany. ASA Spec. Publ. 35. ASA, Madison, WI. 96.Young, W.C. III. 1996. Extension estimates for Oregon forage and turf grass seed crop acreage, 1995. News/Notes 10(1):8-11. Crop & Soil Science Dept., Oregon State Univ. Corvallis, OR. Extracted from Fransen, Steven C. 1993. Viewing Perennial Grasses for Pasture and Silage -- a Perspective from the Field. p. 24-37. In Proc. of the 1993 Northwest and Lower Columbia Dairy Shortcourses. Washington State Univ. Document Citation Evers, G.W., D.B. Hannaway, S. Griffith, S. Minier, P. Hoagland, M. Runyon, M.H. Hall, I. Jacob, S.W. Johnson, E. Liss, S. Fransen, S.L. Fales, W. Lane, D.M. Ball, M. Chau, J. Matylonek, M. Chaney, J. Cropper, A. Liston, and W.C. Young III. 1996. Perennial Ryegrass (Lolium perenne L.) International Forage Fact Sheet. Intl. Forage Species Fact Sheet Series of the Forage Information System. URL: http://www.forages.css.orst.edu/Topics/Species/Grasses/ Perennial_ryegrass/International_Fact_Sheet.html. |