This is to certify that the dissertation entitled ASSESSING PERSISTENCE, PRODUCTIVITY, ANIMAL PREFERENCE, FORAGE QUALITY AND BOTANICAL COMPOSITION OF ROTATIONALLY GRAZED PERENNIAL COOL SEASON GRASSES AND CLOVERES GROWN IN MONOCULTURE AND BINARY MIXTURES IN MICHIGAN Presented by Nasser S. Al-Ghumaiz has been accepted towards fulfillment of the requirements for the Ph.D degree in Crop and Soil Sciences KEN/K V150 Major lyrofessor t 1gnature ///.2aj/a (a Date MS U is an Affirmative Action/Equal Opportunity Institution LIBRARY Michigan State University PLACE IN RETURN BOX to remove this checkout from your record. To AVOID FINES return on or before date due. MAY BE RECALLED with earlier due date if requested. DATE DUE DATE DUE DATE DUE 2/05 p:/CIRC/DateDueiindd-p.1 ASSESSING PERSISTENCE, PRODUCTIVITY, ANIMAL PREFERENCE, FORAGE QUALITY AND BOTANICAL COMPOSITION OF ROTATIONALLY GRAZED PERENNIAL COOL SEASON GRASSES AND CLOVERS GROWN IN MONOCULTURE AND BINARY MIXTURES IN MICHIGAN By Nasser S. Al-Ghumaiz A DISSERTATION Submitted to Michigan State University In partial fulfillment of the requirements For the degree of DOCTOR OF PHILOSOPHY Department of Crop and Soil Sciences 2006 ABSTRACT ASSESSING PERSISTENCE, PRODUCTIVITY, ANIMAL PREFERENCE, FORAGE QUALITY AND BOTANICAL COMPOSITION OF ROTATIONALLY GRAZED PERENNIAL COOL SEASON GRASSES AND CLOVERS GROWN IN MONOCULTURE AND BINARY MIXTURES IN MICHIGAN By Nasser S. Al-Ghumaiz Most perennial cool season grasses and clovers introduced to Michigan have not been evaluated in binary mixtures. The objectives of this study, which was conducted over five growing seasons at three different latitudes in Michigan were: (i) to determine persistence and productivity of perennial grass and clover species grown in monoculture and binary mixtures under three different latitudes in Michigan; (ii) to determine botanical composition of grass-clover binary mixtures over time ; (iii) to determine animal preference and forage quality of these species under rotational grazing, and (iv) to evaluate the use of Near-Infrared Reflectance Spectroscopy (N IRS) to predict the species composition using three calibration equations. Grass-clover binary mixtures resulted in greater persistence, increased ground cover, greater animal preference and higher forage quality than grass or clover growing in monoculture. However, persistence of both perennial grass and clover was related to the site of the study. Kura clover provided the highest dry matter (DM) yield (tones acre") and exceptional persistence under grazing particularly at southern part of Michigan. NIRS had higher prediction accuracy with R2 ranging from 0.67 to 0.72 and SEP from 6.9 to 12.8 respectively using equations generated from hand separations of several grass and clover species. NIRS can be used to replace the hand separation method to determine botanical composition pasture species using a calibration equation developed from a large data set of hand-separated samples. DEDICATION To My Parents, My Wife And My Children iii ACKNOWLEDGMENTS First I want to thank ALLAH, my lord who enabled me to succeed in this work. Secondly, I sincerely express my gratitude to the people who helped in this work, my major advisor Dr. Richard Leep for giving me the opportunity to be his student at Michigan State University. I would like to thank him for encouraging me to express confidence, gain new skills and trusting me to get the job done. A special thanks to the other members of my guidance committee: Dr. Donald Penner for providing his expertise and advice to improve my research project, Dr. Herbert Bucholtz, Department of Animal Science, for his support, sharing knowledge and research ideas, that help to improve my research project and last but not least Dr. Shasha Kravchenko for her assistance in my program, particularly, her great inputs on statistical analyses. I am grateful to my colleague and fiiend Timothy Dietz for his valuable contribution in the field and lab works throughout my program until I accomplished this project. My thanks goes also to forage research crew namely, Deborah Warnock, James De Young, Daniel Hudson and the summer student employees including Joseph Brooks, Stephanie Little, Matthew Smith, Garrett Laurain-Marushia, Mildred Lyon, and Sherri Weisbeck, for their assistance in data collection and lab analyses. I acknowledge Christian Kapp for his technical support and effort managing the plots at Upper Peninsula Experiment Station. My appreciation is extended to all the staffs at Upper Peninsula Experiment Station, Lake City Experimental Station, Kellogg Biological Research Station at Hickory Comers and Crop and Soil Sciences Research and Teaching Station at East Lansing for their cooperation in providing facilities and support in my field research. I wish to think all graduate students, faculty and staff in Department of Crop and Soil iv Sciences at Michigan State University, as they were always supportive during my academic program. I am especially indebted to Calvin Bricker, Research Assistance, for his technical assistance and consultation in computer software. I want to thank Rood Trust Fund who provided funding for this research. My sincere appreciation goes to Saudi Arabia Government who was behind all the financial support for entire my graduate studies at Michigan State University. To my colleagues in college of Agriculture in Qassem University in Saudi Arabia for offering all possible help throughout my academic program. I am especially gratefirl to my beloved father and mother for their years of patience, encouragement and prayers that I achieve my goal during my study abroad. Another heartfelt thanks to my wife, Nourah Al-Homaid, and my children, Saleh, Shahad and Abdulaziz, for their strong support and patience throughout my academic program. To all my relatives and friends who they were always thinking about me. TABLE OF CONTENTS Page LIST OF TABLES ............................................................................. v11 LIST OF FIGURES ............................................................................ xi GENERAL INTRODUCTION ................................................................. 1 Literature Cited .................................................................................. 5 CHAPTER 1 EVALUATION OF THE PERSISTENCE AND PRODUCTIVITY OF PERENNIAL COOL SEASON GRASSES AND CLOVERS GROWN IN MONOCULTURE AND BINARY MIXTURES IN MICHIGAN Abstract ........................................................................................... 6 Introduction And Background .................................................................. 7 Materials And Methods ........................................................................... 15 Results And Discussion. ......................................................................... 20 Conclusions ........................................................................................ 41 Literature Cited ................................................................................... 44 CHAPTER 2 ANIMAL GRAZING PREFERENCE AND FORAGE QUALITY OF PERENNIAL COOL SEASON GRASSES AND CLOVERS GROWN IN MONOCULTURE AND BINARY MIXTURES UNDER ROTATIONAL GRAZING Abstract .......................................................................................... 76 Introduction And Background ................................................................ 77 Materials And Methods ........................................................................ 83 Results And Discussion. .......................................................................... 87 Conclusions ....................................................................................... 94 Literature Cited ................................................................................. 95 CHAPTER 3 PREDICTING BOTANICAL COMPOSITION OF GRASS-CLOVER PASTURE MIXTURES USING NEAR-INFRARED REFLECTANCE SPECTROSCOPY Abstract .............................................................................................. 107 Introduction And Background ................................................................ 109 Materials And Method8112 Results And Discussion ........................................................................ 117 Conclusions ....................................................................................... 119 Literature Cited .................................................................................. 121 GENERAL SUMMARY ........................................................................ 125 APPENDICES ................................................................................... 127 vi LIST OF TABLES Page CHAPTER I Table 1. The mean values of winter injury rating of 16 grass cultivars established in monoculture at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) over a three-year period ....................................................................................... 51 Table 2. The mean values of winter injury rating of 67 grass-clover binary mixture treatments established at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) over a three- year period .................................................................................... 52 Table 3. The mean values of spring and fall ground cover rating of 16 grass cultivars established in monoculture at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (U PES) over a three-year period ............................................................................. 54 Table 4. The mean values of spring (S) and fall (F) ground cover rating of 67 binary mixtures treatments established at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) over a three-year period ............................................................................. 55 Table 5. The mean values of winter injury rating of eight clover cultivars established in monoculture at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) over a three-year period .......................................................................................... 58 Table 6. The mean values of spring and fall ground cover rating of eight clover cultivars established in monoculture at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) over a two-year period .............................................................................. 59 Table 7. The mean values of spring (S) and fall (F) percentage clover rating of festulolium-clover binary mixtures established at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (U PES) over a three -year period .................................................................... 60 Table 8. The mean values of spring (S) and fall (F) percentage clover rating of orchardgrass-clover binary mixtures established at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) over a three-year period ...................................................................... 61 vii Table 9. The mean values of spring (S) and fall (F) percentage clover of perennial ryegrass-clover mixtures in three locations ................................... Table 10. The mean values of spring (S) and fall (F) percentage clover rating of tall fescue-clover binary mixtures established at Kellogg Biological Research (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) over a three-year period ............................................................................ Table 11. Dry matter yield (tons acre") of 16 grass cultivars established in monoculture at Kellogg Biological Research (KBS) over a two-year period ........ Table 12. Dry matter yield (tons acre") of 16 grass cultivars established in monoculture at Lake City (LC) over a two-year period ................................. Table 13. Dry matter yield (tons acre'l) of 16 grass cultivars established in monoculture at Upper Peninsula Experiment Station (UPES) over a two-year period .......................................................................................... Table 14. Dry matter yield (tons acre") of 67 grass-clover binary mixtures treatments established at Kellogg Biological Research (KBS) over a two-year period ........................................................................................... Table 15. Dry matter yield (tons acre") of 67 grass- clover binary mixtures treatments established at Lake City (LC) over a two-year period ..................... Table 16. Dry matter yield (tons acre'l) of 67 grass- clover binary mixtures treatments established at Upper Peninsula Experiment Station (U PES) over a two-year period ............................................................................... Table 17. Dry matter yield (tons acre!) of eight clover cultivars established in monoculture at Kellogg Biological Research Station (KBS) over a two-year period .......................................................................................... Table 18. Dry matter yield production (tons acre") of eight clover cultivars established in monoculture at Lake City (LC) over a two-year period ............... Table 19. Dry matter yield (tons acre") of eight clover cultivars established in monoculture at Upper Peninsula Experiment Station (UPES) over a two-year period ......................................................................................... viii 62 64 65 66 67 68 70 72 74 74 75 CHAPTER II Table 1. Animal preference score of 16 grass cultivars established in monoculture treatments over eight grazing events .................................... Table 2. Animal preference score of eight clover cultivars established in monoculture over seven grazing events ................................................ Table 3. Animal preference score of 67 grass-clover binary mixtures over eight grazing events .................................................................................. Table 4. The mean values (%) of forage quality components (CP, ADF and NDF) for pasture species of grass, clover and binary mixtures over 2004-2005 growing seasons in three different locations .............................................. Table 5. Average forage quality parameters (CP, ADF and NDF) of 16 grass cultivars established in monoculture and binary mixtures in three locations. . .. Table 6. Average forage quality parameters (CP, ADF and NDF) of eight clover cultivars established in monoculture in three locations ................................ CHAPTER III Table 1. Calibration and validation statistics for NIRS determination of botanical composition of grass-clover mixture samples collected over 2003-2005 in KBS, LC and UPES using calibration equations developed from artificial mixed samples of 2004 Lake City data .................................................... Table 2. Calibration and validation statistics for NIRS determination of botanical composition of grass- clover mixture samples collected over 2003- 2005 in KBS, LC and UPES using calibration equations developed from hand- separation samples of 2004 Lake City data ............................................. Table 3. Calibration and validation statistics for NIRS determination of botanical composition of grass-clover mixture and weed samples collected over 2003-2005 in KBS, LC and UPES using calibration equations developed from the three years and three locations hand separation samples ix 101 102 103 105 105 106 123 123 123 APPENDICES Table 1A. Soil type, soil pH, cutting schedule over 2004 and 2005 growing seasons at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) and the grass and clover cultivars established in this study ........................................................................................... 131 Table 2A. Total monthly precipitation (mm) at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) during the growing season of 2004-2005 comparing with 30-year average. . . 132 Table 3A. Average daily maximum air temperatures (°C) at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) during the growing season of 2004-2005 comparing to 30-year average ........................................................................................ 133 Table 4A. Average daily minimum air temperatures (°C) and snow fall (cm) at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) from January through April of 2003-2006 comparing with 30-yr average ............................................................. 134 Table 5A. Average animal weight (kg), and the number of animals in each grazing event during 2004—2006 grazing season .......................................... 135 Table 6A. ANOVA for winter injury, spring and fall ground cover and spring and fall clover for binary mixture data fi'om years 2004-2006, locations (KBS, LC and UPES) and 67 binary mixtures(treatments) ..................................... 136 Table 7A. ANOVA for winter injury, spring and fall ground cover for grass monoculture data from years 2004-2006, locations (KBS, LC and UPES) and 16 grass varieties (Cultivars) .................................................................. 137 Table 8A. ANOVA for winter injury, spring, and fall ground cover for clover monoculture data from years 2004-2006, locations (KBS, LC and UPES) and eight clover varieties (Cultivars) ........................................................... 138 Table 9A. ANOVA for dry matter yield, animal preference and forage quality (CP, ADF and NDF) for binary mixtures data from years 2004-2005, locations (KBS, LC and UPES), cutting and 67 binary mixture (treatments) .................. 139 Table 10A. ANOVA for dry matter yield, animal preference and forage quality (CP, ADF and NDF) for grass monoculture data from years 2004-2005, locations (KBS, LC and UPES), cutting and 16 grass varieties (Cultivars) .................... 140 Table 11A. ANOVA for dry matter yield, animal preference and forage quality (CP, ADF and NDF) for clover monoculture data from years 2004-2005, locations (KBS, LC and UPES), cutting and eight clover varieties (Cultivars) ...... 141 LIST OF FIGURES Page CHAPTER I Figure 1. Comparing average winter injury (WI) at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experimental Station (U PBS) for grass-clover binary mixtures (BM), grasses, and clovers grown in monoculture .................................................................................. 50 CHAPTER II Figure 1. The differences in animal grazing preference for the binary mixture (BM), clover, and grass treatments during 2004 grazing season ...................... 100 Figure 2. The differences in animal grazing preference for the binary mixture (BM) clover, and grass treatments during 2005 grazing season ...................... 100 CHAPTER 111 Figure 1. Relationship of NIRS predicted percentage to hand-separated of grasses (a), clovers (b) and weeds (c) using a calibration equation of the hand separation of each component over three years at three experimental research stations. .......................................................................................................... 124 APPENDICES Figure 1A. Michigan map showing the three experimental locations representing three different latitudes in Michigan: Kellogg Biological Research Station at Hickory Comers (KBS) (1), Lake City Research Station (LC) (2), and Upper Peninsula Experiment Station at Chatham (UPES) (3) ................................. 128 Figure 2A. The map design of grass-clover binary mixtures and grass and clover monoculture treatments ...................................................................... 129 Figure 3A. The experimental area grazing arrangement ............................... 130 xi GENERAL INTRODUCTION Forage crops, by definition, are crops grown primary for feeding livestock. Forage crops can be harvested by machines or grazed by animals. Grazed forage is defined as forage, which is consumed directly by the grazing animals (Pasturage) (V allentine, 2001). Pasture refers to the fenced area of domesticated forages on which animals are grazed. In Michigan more than 1.5 million hectares of farmland is dedicated to forage crops used for hay, silage, green chop, and over 500 thousand hectares are pastureland (2002 Census of Agriculture). The goal of pasture management is to maximize forage quality and yield, while ensuring stand persistence. Stand persistence depends in part on management practices such as controlling weeds, maintaining proper soil fertility, and using an appropriate harvest or grazing schedule, but it also depends on the innate compatibility and winter hardiness of the forage species or cultivars used in pastures. Severe winter conditions can cause damage to perennial forage crops in northern latitudes (Bélanger et al., 2002). Introducing a new species requires knowledge of the species tolerance to local or regional environmental conditions. Pasture managers in northern temperate climates could improve their production and lengthen stand life by selecting high yielding winter hardy cultivars for pasture production. Since most pastures are planted with both legume and perennial grass, it is important that species selection is based on their performance in binary mixtures. However, there is limited commercial information available on pasture species performance in binary mixtures because seed companies mainly test their species in a monoculture. Plant performance in pastures cannot be understood without reference to animals. Under gazing, animals tend to prefer the most palatable plants first, which consequently causes overgazing of the most palatable species (V allentine, 2001 ). Consumption of the more palatable species can also have an impact on the mixture composition. Hence, animal preference is a factor that may influence the relationship between legume and gasses in the pasture system. Forage nutritive evaluation provides the final assessment of pasture in terms of nutritional values, which ultimately can be vital in a pasture forage evaluation program. The botanical composition need to be determined to estimate the percentage of actual legume and gass content in a pasture. Several methods have been used for estimating botanical composition of gass and legume mixtures. The most common method involves manually separating the mixtures into gass, legume, and weed components. However, this strategy is not practical since it is laborious, time-consuming, costly, and prone to operator error, especially when a large numbers of samples are being processed. Near-Infrared Reflectance Spectroscopy (N IRS) can lead to more efficient determination of various components of forage quality. NIRS might be used successfully for analyzing forage components as a rapid and inexpensive technique to replace the hand separation approach. Historically, the first application of NIRS was reported in literature in 1939 (Gordy and Martin, 1939). The potential of NIRS for solving analytical problems was developed by Kay (1954). In 1968, Ben-Gera and Norris applied NIRS to analysis of ag'icultural products. NIRS was first shown by Norris et al. (1976) to be a rapid method to determine the chemical composition of forages. This research was conducted to assess the persistence of gass and clover species and cultivars gown in monoculture and binary mixtures at three different latitudes in Michigan. Animal gazing preferences and forage quality were used in assessing the nutritive values and palatability of species and cultivars in this study. In addition, this study evaluated the use of NIRS for providing rapid and accurate results for predicting the botanical composition of gass and clover species. This dissertation is divided into three studies. The objective of the first study, Chapter 1, was to assess the persistence and productivity of gass and clover cultivars gown in monoculture and binary mixtures established in three latitude locations in Michigan. Several variables were used for this evaluatation including: total forage yield, winter hardness, estimation of the gass and clover botanical composition, determining clover and gass gound cover and the percent clover in gass-clover mixtures over time. The objective of the second study, Chapter 2, was to determine animal preferences and forage nutritive evaluation of perennial gass and clover species and cultivars established in monocultures and binary mixtures. The gazing trial was conducted in a single location. However, the nutritive evaluation was completed on all perennial gasses and clovers from three locations. The objective of the third study, Chapter 3, was to determine whether NIRS can be applied as an alternative technique to the hand separation method for estimating gass- clover botanical composition. In this study, three calibration equations were created. The first equation was developed from pure samples obtained from a single location and year, which were mixed artificially to different proportions; the second equation was developed from hand separated samples collected from a single location and year and the third equation created from hand separated samples from three locations over three years with an additional constituent, weeds. All the three equations were developed to predict gass-clovers botanical composition collected from samples from three locations during 2003-2005 seasons. Calibration and validation equations were reported along with coefficients of determination (R2) and standard errors of prediction (SEP). LITERATURE CITED Belanger, G, P. Rochette, Y. Castonguay, A Bootsma, D. Mongain, and D.A.J. Ryan. 2002. Climate. change and winter survival of perennial forage crops in eastern Canada. Agr. J. 94: 1120-1130. Ben-Gera, 1., and K.H. Norris.l968. Direct spectrophotometric determination of fat and moisture in meat products. J .Food Sci. 33: 64-67. Gordy, W., and PC. Martin 1939. The infrared absorption of HLC in solution J. Chem. Phys. 7:99-102. Kaye,W.l954. Near infrared spectroscopy. 1. Spectral identification and analytical application. Spectrochim . Acta 6:257-287. Norris, K.H., R.F.Bames, J .E. Moore, and 1.8. Shenk. 1976. Predicting forage quality by infrared reflectance spectroscopy .J. Anim. Sci. 43: 889- 897. USDA, National Agiculture Statistics Service. 2002 Census of Ag'iculture-State data. Vallentine, J .F. 2001. Grazing management, 2“d ed. Harcourt Science and Technology company. San Diego, CA. Chapter 1 EVALUATION OF THE PERSISTENCE AND PRODUCTIVITY OF PERENNIAL COOL SEASON GRASSES AND CLOVERS GROWN IN MONOCULTURE AND BINARY MIXTURES IN MICHIGAN ABSTRACT Persistence of gass-legume binary mixture components is important for pasture management, yet one species is often lost from the stand within a few gowing seasons. Forage and livestock producers seek species and cultivars, which provide the geatest persistence and dry matter (DM) yield over the longest time. The objective of this study was to evaluate the persistence and DM yield of several gass and clover cultivars established in monoculture and binary mixtures across three locations representing different latitudes in Michigan. The evaluation criteria were based upon winter injury, percent gound cover, percentage clover in the gass-clover binary mixtures and total DM yield. Binary mixtures resulted in increased DM yield and resistance to winter injury compared to monoculture treatments. Even non-winter hardy gass species had higher persistence when associated with clovers compared with gass monoculture. Sigrificant differences in performance among gass cultivars were observed with tall fescue shown sigrificantly higher persistence and yield stability at all locations. Variations between latitude locations were observed. Among clover monoculture species, kura clover (Endura) had the geatest persistence and DM yield at the southern latitude in both monoculture and binary mixtures. This study demonstrated the importance of proper species and cultivars selection based upon location for persistence and dry matter production. INTRODUCTION AND BACKGROUND Several temperate forage gasses are commonly gown in binary mixtures with alfalfa (Medicago sativa L.), for hay or silage production (Casler, 1988). Most forage gasses gown in Michigan pastures can be classified as cool season plants (C3 plant), which have an optimum gowth temperature of 18°-24 °C (Rohweder and Albrecht, 1995). During the mid to late summer, both heat and rainfall deficits often exceed the optimal gowth range for cool season gasses, causing them to go into a drought-induced dormancy. During this period, there is often a shortage of soil moisture available for the shallow rooted cool season gasses (Penn State University Agonomy Guide, 2005-2006). Thus, many producers include legumes such as clovers in their pasture mixtures since the deeper taproots of clovers are able to utilize the soil moisture and minerals in the sub soil. Clovers species are often preferred for pasture over alfalfa as they are more tolerant to frequent gazing than alfalfa. Forage gass-legume binary mixtures are important components of dairy and livestock diets, which offer many advantages over pure stands (Vough, et.al., 1995). Grasses provide a sod that can be helpful for increasing water infiltration and reducing runoff and soil erosion (Wadleight, et al., 1974; Wischmeier and Smith, 1978). Binary mixtures are more competitive with weeds than pure stands (Drolsom and Smith, 1976). Moreover, gasses benefit from fixing the atmosphere nitrogen (N) provided by legumes, which reduces the need for supplemental nitrogen fertilization (Vough, et al., 1995). Grass-legume binary mixtures may yield geater dry matter (DM) than legume monoculture (Chamblee and Collins, 1988). In contrast, alfalfa-gass binary mixtures did not yield more forage than an alfalfa monoculture at high seeding rates (Wilsie, 1949). In addition, legume-gass binary mixtures had higher in vitro DM digestibility (IVDMD), crude protein (CP) and better seasonal yield distribution than monoculture treatments. Binary mixed stands can reduce the risk of bloat, which is a very common problem with ruminants associated with gazing exclusively legume pastures (Casler and Walgenbach, 1990). In this study, we evaluated the persistence and DM yield of cool season gasses and clover species and cultivars under Michigan gowing conditions. Cool season grasses Perennial ryegass (Lolium perenne L.) is one of the most common cool season gasses gown in binary mixtures. It is considered a temperate perennial gass and is gown throughout the world including North and South America, Europe, New Zealand and Australia. It gows well in early spring and fall. However, during excessive high temperatures in summer months, it becomes dormant even with irrigation or abundant summer rainfall (Leep, 2004). Perennial ryegass is suitable for pasture due to its high forage quality (Balasko et al., 1995). It can tolerate close frequent gazing, which makes it useful in an intensive gazing system (Jung et al., 1996). Perennial ryegass has a higher IVDMD than other temperate perennial gass species (Pysher and F ales, 1992). Orchard gass (Dactylis glomerata L.) is a major gass species commonly recommended for pastures in the Northeastern and North Central United States, (Van Santen and Sleper, 1996) due to its geater drought tolerance and winter hardiness as compared to perennial ryegass (Christie and McElroy, 1995). It is also well suited for mixtures with one or more legume species because of its fast gowth and tillering ability (Hoveland, 1992). Tillering occurs almost continuously throughout the gowing season with large number of tillers within a clump (the elongated stem). These remain vegetative, retaining the gowth point close to the gound, which produce only leaves. Constant tiller production results in a rapid recovery after gazing (Christie and Mcelroy, 1995). Thus, orchard gass can persist under frequent gazing or clipping more than other gass species such as ryegass, timothy (Phleum pretense L.), or tall fescue (Davies, 1988) F estulolium (F estulolium braunii, K.A.) is derived from crosses between meadow fescue (F estuca pratensis Huds) or tall fescue (F estuca arundinacea Schreb.), and either Italian ryegass (Lolium multiflorum Lam.) or perennial ryegass. This cross combines the palatability of perennial or Italian ryegass with the persistence of meadow or tall fescue. However, festulolium is less palatable and forms a more open sward as compared to perennial ryegass (Wit, 1959). Festulolium combines the disease resistance and winter hardiness of meadow fescue with the high crude protein (CP) and good season- long productivity of Italian ryegass. Winter hardiness of some festulolium varieties may approach that of perennial ryegass (Ohio State University Extension bulletin). Tall fescue (F estuca amndinacea Schreb.) is used widely for forage, turf, and conservation purposes (Collins and Hannaway, 2003). It is the predominant cool-season pasture gass in many southern states. It is tolerant of continuous close gazing and superior to many other cool-season gasses in livestock-carrying capacity. Tall fescue may be used as a hay crop, but needs to be harvested as the first seed heads begin to appear. Tall fescue is also gown as a turf gass species and its use has increased since the introduction of turf-type cultivars (Funk et al., 1981). Some tall fescue cultivars are infected with a fungal endophyte, Neotyphodium coenophr’alum , Margan-J ones & Garns, which produces alkaloids that are toxic to gazing animals (Ju et al., 2006) resulting in reduction of feed intake, weight gain, and milk production . However, non-endophyte and nontoxic endophyte-infected cultivars have been developed for livestock pastures. The nontoxic infected plants have shown improved tolerance to some environmental stresses such a drought and some insects (Collins and Hannaway, 2003). Cool season clovers Red clover (T rifolium pratense L.) is gown as a monoculture or mixed with gasses. Red clover may be gouped into three types: early-flowering, late-flowering and wild red clover. Most red clover gowing in the US is the early-flowering type (Taylor and Smith, 1995). It is a very important legume hay crop in the Northeastern US. The relative performance of red clover cultivars may be different when monoculture and binary mixtures are compared. It is considered a short-lived perennial legume (Nelson and McGraw, 2003). Red clover is most often gown with a companion gass for hay, silage, or gazing. However, little information is available on the performance of red clover cultivars gown with gass species in rotationally gazed pastures. The performance of red clover cultivars is influenced by location, cutting system, and the presence or absence of gass. White clover (Trifolium repens L.) (Common and ladino types) is one of the most important legumes used for gazing in the US. White clover is classified in three general cultivars goups: small, intermediate and large. The small cultivars are usually native and are referred to as wild white clover. Most white clover marketed in the US belongs to the intermediate type. Large cultivars referred to as Ladino, were introduced from Italy 10 (Henning and Wheaton, 1993). White clover should be gown in binary mixtures with gasses to prevent bloat in livestock. Under adequate soil moisture, white clover can gow in every state of the US and province in Canada (Pederson, 1995). White clover is very palatable and is high in forage quality (higher CP and lower fiber) and tolerates continuous, heavy gazing pressures (Spitaleri et al., 2003). Kura clover (T rifolium ambiguim Bieb.) is a long-lived, perennial, rhizomatous legume (Bryant,l974; Taylor and Smith,1998) that tolerates fi'equent defoliation in monoculture (Peterson et al., 1994) or binary mixtures with gass (Kim,1996). It can be used for hay or pasture production (Sheaffer and Marten, 1991; Sheaffer et al., 1992). Kura clover is very compatible with gasses and suitable for mechanical harvest system (Kim, 1996). Kura clover gows slowly during the establishment year (Speer and Allinson, 1985). Slow establishment have limited widespread use of kura clover. This is related in part to the kura clover devoting most of its fixed C to roots and rhizomes during establishment and its slow nodulation, which limits N2 fixation in the seeding year (Peterson etal., 1994; Seguin et al., 2001). However, with its rhizomatous root system, it is able to survive harsh environmental condition at northern latitudes (Pederson, 1995). DM yield of kura clover is lower than alfalfa but similar to red clover and birdsfoot trefoil (Lotus comiculatus L.) (Sheaffer and Marten, 1991). However, kura has higher forage quality (higher CP, lower acid detergent fiber [ADF] and neutral detergent fiber [NDF]) than other legumes (Allinson et al., 1985; Sheaffer and Marten, 1991). Kura clover has a higher risk of causing bloating in gazing animals when compared to white clover or alfalfa (Sheaffer et al., 1992). Because of this, it should be gown in combination with perennial gass to reduce incidence of bloat (Mourifio et al., 2003). ll Grass and legume compatibility in binary mixtures is an important aspect of pasture systems. There are several factors that influence the ecology of gass-legume binary mixtures and many researchers have reviewed this subject. Grass and legumes compete for water and soil minerals when gown in mixtures (Jones, et al., 1988). However, competing for irradiance is often considered to be most critical among all the competition factors (Donald, 1961). Palatability of species can have a geat impact on binary mixture composition. Animals tend to gaze the most palatable species when multiple species are offered (Chapter 2). In addition, gass and legumes have different gowth habits, regowth, and physiological gowth requirements, which make management more difficult for the binary mixtures compared to monocultures of the same species (Smith et al., 1986). Forage gass species vary in their ability to persist with legumes in binary mixtures (Camlin, 1981). For instance, orchardgass is more competitive in binary mixtures with alfalfa than smooth bromegasses (Bromus inermis.Leyss) (Schmidt and Tenpas, 1965; Smith et al., 1973). This criterion is important when evaluating gass- legume associations (Zannone et al., 1986). Unlike alfalfa and red clover, white clover can tolerate both continuous and rotational gazing due to the proliferation of stolon segnents that can gow and spread by forming new plants (Pederson, 1995). Under both rotational and continuous gazing, it is generally expected that DM yield of pastures will decrease to a certain extent during gazing season. Many factors can cause yield reduction. For example, changing botanical composition with a loss of legume can result in nitrogen deficiency. Soil structure and compaction can cause poor gaseous exchange at the root resulting in stand declines especially with legumes. In addition, soil nitrogen 12 and potassium deficiencies as well as disease can also lead to DM yield reduction (Carnlin and Stewart, 1976). It has also been reported that gass-legume balance is very susceptible to changes in respect to environmental conditions (Camlin, 1981). Therefore, for accurate assessment of gass-legume binary mixtures persistence, it is important for this type of research to be conducted under different soil types and environmental conditions. Environmental conditions can regulate gass-legume interaction (Snaydon 1987). Low temperatures during the winter are an important factor in determining geogaphical distribution and persistence of forage species (Lorenzetti et al., 1971; Shimada et al., 1993). Winter injury occurs in most perennial gass and legume species and is related to the length and intensity of the cold weather conditions coupled with the effects of snow cover, soil heaving, and ice encasement. Bélanger et a1. (2002) reported that severe winters in eastern Canada caused recurrent damage to perennial forage crops. For a crop such as alfalfa, winter injury often occurs due to repeated freezing and thawing causing death of plants. Non-winter hardy species such as rye gass (Lolium sp L.) and festuloilum (some cultivars) have limited use in binary mixtures because of their poor cold persistence (Elissa et al., 1995). However, snow cover has a geat impact on increasing forage survival. Leep et a1. (2001) in Michigan concluded that 10 cm of snow cover is sufficient to protect alfalfa from winter injury. The ability to survive freezing temperatures depends upon adequately managing soil fertility, especially N and K, which can increase cold resistance (Nelson and Volenec, 1995). Winter survival of Coastal bermudagass (Cynodon dactylon) decreased with increasing levels of applied nitrogen (N) fertilizer (Adams and Twersky, 1960). Genetic backgound may also influence the 13 severity of winter injury (McKenzie et al., 1988). Past research indicates that tetraploid perennial ryegass cultivars had sigrificantly higher competitive abilities during summer and lower cold tolerances in winter than the diploid cultivars (Dvorak and Fowler, 1978; Sugiyama, 1998). Although the lower cold tolerance of tetraploid cultivars may lead to low persistence in pasture in northern latitudes, their lower survival rate in a cold winter is somewhat counterbalanced by high competitiveness during the summer (Sugiyama, 1998). Tetraploid cultivars of other forage species such as red clover and meadow fescue have been shown to have lower cold tolerance than diploids (Tyler et al., 1978). In recent years, both the gass and legume seed industry have begun marketing new species and cultivars of perennial gasses and clovers to Michigan gowers. For example, orchardgass cultivars have been introduced with value-added traits such as increased tillering, later maturity, and geater winter hardness. Tall fescue has been recently offered endophyte free with smoother leaf blades. Most seed companies have information on how monocultures of their cultivars perform but they do not provide information on how the species perform as binary mixtures in long-term pastures. In addition, the ability of new cultivars to survive the severe winter conditions could be an issue, especially when gown in northern latitudes (44°—460 N). No previous research has been done to evaluate multiple gass and clover cultivars in binary mixtures at different latitudes in Michigan. Therefore, more research is needed to determine how these cultivars perform under Michigan gowing conditions at latitudes 44°-46°. In this study, several improved cool season gass and clover species and cultivars established in monoculture and binary mixtures were evaluated to determine their 14 suitability for Michigan climatic conditions. Several aspects need to be considered for evaluating gass and clover species, including dry matter yield, winter injury, pasture gound cover, and clover composition in the mixtures. MATERIALS AND METHODS Experiment Establishment and Maintenance: Monocultures and binary mixtures experiments were established in 2001 to be evaluated over a 5-year period (2002-2006) at three Michigan State University (MSU) experimental stations: (i) Kellogg Biological Research Station at Hickory Comers (KBS) (42° 24' N, 85° 24' W); (ii) The Beef Cattle and Forage Research Station at Lake City (LC) (44°19' N, 85°12' W) and (iii) Upper Peninsula Experiment Station at Chatham (UPES) (46°33' N, 86°55' W). The locations map is illustrated in Appendix Fig 1A. This research focuses on the period of 2004-2006. The study area was separated into three portions: gass only, legume only (clover), and gass-clover binary mixtures (Appendix Fig. 2A). Each portion was a RCBD with three replications. For the gass-clover binary mixtures, each replication consisted of 67 entries of different combinations of gass and clover cultivars seeded in 1.8 by 5 m plots. Grass and clover monocultures experiments consisted of 16 and 8 gass and clover entries, respectively with plots of the same size as these of the binary mixtures portion. Eight clover cultivars were established in this study included three red clover (VNS', Star Fire, and Start), four white clover (KopulI, Ladino, Alice, and Jumbo), and one kura ‘ Variety Not Stated 15 clover (Endura). The 16 gass cultivars were included two festuloliurns (Duo and Hykor), four orchardgass (Amba, Niva, Sparta and Tekapo), seven perennial ryegass (Aries, Maverick Gold, Quartet, Tonga, Barfort, Mara and Calibra) and three endophyte free tall fescues cultivars (Bronson, K5666V, and Barolex). Appendix Table 1A lists information on soil type, soil pH, harvest schedule, and gass and clover species and cultivars. Soil was analyzed at the MSU soil-testing laboratory; fertilizers and lime were applied as recommended by soil test results. All tested soil parameters were at or above optimal levels (average: P: 60 ppm, K: 139 ppm, and pH: 6.5). In each location, nitrogen (N) was applied to the gass only plots following each cutting in the form of ammonium sulfate at a rate of 45.4 kg ha’1 in four applications through the gowing season. However, since nitrogen deficiency appeared during 2005 in some gass species due to the poor clover stands in the binary mixture treatments, nitrogen was applied in a single application of (45.4 kg ha’l) to the binary mixture treatments in all locations. Weeds were controlled with an herbicide in the gass monoculture treatments when necessary. Weather record: For each experimental location, total monthly precipitation (mm), average daily maximum and minimum air temperatures (°C) during the months of gowing season and the total monthly snowfall (cm) during winter months were recorded. 16 Data Collection and Sampling Procedure: Three to four gazing (cutting) events were obtained from each location with 30 to 35 days interval between each event depending on weather conditions. The following data were collected: Qualitative Measurements (Visual Estimates): In all locations, qualitative measurements were recorded during 2004-2006. However, the clover monoculture portion was excluded in 2006 due to poor stand and weed contamination. Data on winter injury, percent living gound cover, and percent clover in the binary mixtures were obtained by visual rating estimates. The rating estimate was based on the average of the ratings generated by two trained people in each plot. The ratings were based on a 1 to 5 scale (Brummer and Moore, 2000). The scale system used for winter injury data collection is inversed from the one used either for gound cover or percentage clover. For examples, score 1 in winter injury is considered good (survive) and score 5 is poor (highly injured), while for gound cover and percentage clover data collection, score 1 is considered poor (low cover) and score 5 is good (highly covered). Winter Injury: Winter injury ratings were taken during the early season gowth (usually end of April to early May) for both monoculture and binary mixture treatments at all locations. A general percentage score of plots affected with winter injury was placed on the following scale: 1: less than 20% of the vegetation killed; 2: 20-40%; 3 = 40-60%; 4 = 60-80% killed; and 5 = geater than 80% of the vegetation was killed. The cultivars that have low winter injury ranking over time are those that have high cold resistance. 17 Vegetative ground cover: Ground cover was recorded in the spring when the gasses were actively gowing— two weeks after winter injury ratings were taken— and again in the fall before the dormancy period (at the end of October). Ground cover was visually scored by assessing the amount of vegetation cover based on the following scale: 1 = geater than 80% of the vegetation missing; 2 = 60-80%; 3 = 40-60%; 4 = 40 —20% and; 5 = less than 20% of the vegetation missing. The cultivars that have low gound cover ranking over time are those that have less persistence. Percentage clover cover: Clover stands were visually rated for the percentage of clover versus gass in each plot of the binary mixture treatments. The ratings were conducted in the spring (early May) and fall (at the end of October) according to the following scale: 1: less than 20% of the clover stand appears in the mixture; 2 = 20- 40%; 3 = 40-60%; 4 = 60-80%; and 5 = 80% or geater of the binary mixture was covered with the clover stand. The clover cultivars that have low cover ranking over time are those that are less compatible with gasses. Quantitative Measurements: Dry matter yield: Forage biomass of monoculture and binary mixture treatments were collected from all locations. When the average plant height was 20 cm, samples were hand clipped at 8 cm height within a 0.25 m2 quadrate in each plot and dried at 60 °C for 48 hr. Dry samples were then weighted for DM yield. 18 Statistical analyses: All the statistical computations were performed using SAS (SAS Institute, 2000). Analysis of variance (ANOVA) was performed separately for binary mixtures, gass monoculture and clover monoculture using PROC GLM. The data from all years and locations were analyzed together. The interactions between years, locations, and cultivars (treatments) were examined and when found sigrificant, mean separations were conducted using Fischer’s LSD at p<0.05. Normality assumption was checked using stem and leaf and normal probability plots in PROC UNIVARIATE. Homogeneity of variance among years and locations was examined and found acceptable. Coefficient of variation (CV) was listed to measure the precision of the experiment. Winter injury was prevalent at LC in the spring of 2005 due to ice-sheeting in the lower portion of the experimental area, which resulted in serious damage in some plots. The affected plots were eliminated from the analyses and reported as missing data. 19 RESULTS AND DISCUSSION 1. Climatic Observations Precipitation: In general, there was a high amount of precipitation recorded in 2004, especially during the months of May and August at the KBS and UPES locations. At LC, there was a higher amount of precipitation during the months of April and May and lower during the months of June, July, August and September. However, in 2005, lower precipitation was observed during most of the gowing season at three locations with some higher amounts recorded in the month of July at KBS, August and September at LC and July and September at the UPES (Appendix Table 2A). Average maximum and minimum daily air temperatures: At both KBS and LC locations, the maximum air temperature during 2004 was above the 30-year average only in April and September and in UPES, the maximum air temperature of 2004 was below the 30-year average throughout the gowing season with the exception of September (Appendix Table 3A). In 2005 gowing season, the average maximum air temperatures at KBS, LC and UPES were above the 30-year average during the entire gowing season except for the month of May (Appendix Table 3A). The lack of precipitation along with above normal temperature in 2005 may have affected the DM yield for all cutting events. Average minimum air temperature (°C) and snowfall (cm) data for the months of January through April of 2003-2006 is listed in Appendix Table 4A. 20 II. Persistence of Grass and Clover Cultivars Grown in Monoculture and Binary Mixtures Persistence results include data obtained from winter injury and gound cover for each monoculture gass and clover cultivar and binary mixtures in all locations over 2004-2006. Si grificant years X location X treatment interactions were present in winter injury, spring and fall gound cover for gass-clover binary mixtures (Appendix Table 6A). In addition, sigrificant interactions were also present in gass monoculture treatment (varieties) for winter injury, spring and fall gound cover (Appendix Table 7 A), and similarly for clover monoculture treatment (varieties) (Appendix Table 8 A). We attribute these interactions primarily to weather conditions varying from locations to location and fi'om year to year. Grass-clover binary mixtures had less winter injury compared to monocultures of gass and clover (Figl ). Differences in winter injury score within cultivars and among locations were observed. Greater winter injury impact on gass cultivars occurred at the UPES as it is farther north than KBS and LC (Appendix Table 4 A). In 2006, the gass and clover species at LC were affected by ice-sheeting, resulting in some native gass such as Kentucky blue gass (Poa pratensis) to dominate the plots. Analyses of winter injury of the gass monoculture showed there were sigrificant differences (p<0.05) among the monoculture gass cultivars at KBS in all years (Tablel). Grass cultivars displayed severe winter injury at the UPES location in the spring of 2006. Even winter hardy species like orchardgass and tall fescue exhibited sigrificant winter 21 injury (Tablel ). Nitrogen applied the previous fall may have accentuated the winter injury. Adams and Twersky (1960) concluded that winter survival of coastal berrnudagass (Cynodon dactylon) decreased with increasing levels of applied nitrogen (N) fertilizer. Cultivars that expressed severe winter injury (score 5) displayed less gound cover in their plots. Ground cover data of gass monoculture, gass-clover binary mixtures and clover monoculture are presented in Tables 3, 4 and 6, respectively. Winter injury and gound cover results will be discussed in more detail for each individual gass species. Persistence of Grass Species F estuloliums: There was no apparent winter injury with the two monoculture festulolium cultivars (Duo and Hykor) at the KBS. There was sigrificant winter injury in Duo in 2006 (Tablel). Duo resulted in significantly more winter injury (p<0.05) than Hykor, at the UPES site (4.3 and 5 in 2005 and 2006, respectively). Analysis of festulolium-clover binary mixtures winter injury showed that sigrificant winter injury occurred at the UPES during 2004-2006 compared to the same years at KBS and LC (Table 2). These data showed that persistence of Duo did not improve when associated with clover in binary mixtures at the UPES, while at KBS and LC, Duo showed improved winter survival when gown with clover in binary mixtures. Analyses of gound cover of the monoculture festulolium cultivars (Duo and Hykor) showed both had excellent gound cover ratings (score 5) at KBS and LC. 22 However, gound cover was different between Hykor and Duo at the UPES with Duo resulting in sigrificantly (p<0.05) less gound cover than Hykor during 2005 (Table3). In conclusion, the results of winter injury and gound cover from the two festuloliums cultivars (Duo and Hykor) established in monoculture and binary mixtures showed Duo was less persistent and more vulnerable to winter injury when gown in the Upper Peninsula of Michigan. Duo has a ryegass backgound (a hybrid resulting from a cross of meadow fescue and a tetraploid perennial ryegass (AMPAC seed company web site). Ryegass parents generally reduce winter survival of festuloliums hybrids and their derivatives (Casler et al., 2002), which helps explain the lower winter hardness of Duo. The lack of the adaptation of Duo in the upper peninsula of Michigan limits its use in pasture systems although it was preferred more by animals than Hykor (Chapter 2). Orchardgrass: Winter injury data analyses showed that orchardgass monoculture cultivars (Tekapo, Amba, Niva, and Sparta) had good winter survival at KBS and LC (Average score 1.3) (Table 1), which was similar to results reported by Christie and McElroy (1995). No sigrificant differences in winter injury appeared at KBS and LC experimental locations, at the UPES, however, sigrificant differences in winter injury between the four orchardgass cultivars occurred during 2004-2006. Tekapo and Sparta demonstrated sigrificant winter injury (p<0.05) at UPES (scores 4 and 5 respectively) when compared to the cultivars Amba and Neva. Winter injury analyses of orchardgass-clover binary mixtures showed a sigrificant difference in winter injury at KBS with one treatment of Amba-red clover (VNS) in 2004 (Table 2). Higher winter injury was observed in Tekapo-clover binary 23 mixtures at LC during 2006. The highest winter injury occurred in the Tekapo-Star Fire red clover binary mixture (score 3.7) (Table 2). Tekapo resulted in sigrificantly higher winter injury when gown with all clover cultivars particularly with white clover K0pu II and Ladino compared to all other orchardgass cultivars in 2006 at the UPES (Table2). These results indicate that Tekapo had sigrificantly lower winter hardiness than all other orchardgass cultivars even when gown with clover in binary mixtures. Ground cover of the monoculture orchardgass cultivars showed geat vegetative cover at both KBS and LC (average score 4) compared to the same cultivars at the UPES in 2006 where scores ranged fi'om 1 to 3 (Table 3). Tekapo resulted in sigrificantly lower gound cover (score of 1 out of 5) than all other orchard gass cultivars due to winter injury. Analysis of gound cover in orchardgass-clover binary mixtures showed sigrificantly lower gound cover for Tekapo when gown with white clover cultivars (K0pu II and Ladino) at UPES in 2006 (Table4). There were no sigrificant differences in gound cover between orchardgass cultivars gown in binary mixtures at the KBS, LC locations in 2004 and fall of 2005 at the UPES. Orchardgass is quite winter hardy when compared to perennial ryegass (Christie and McElroy, 1995). In this study, four orchard gass cultivars gown in monoculture and binary mixtures exhibited good gound cover and persistence when gown at the KBS and LC experimental stations. At the UPES location, however, there were differences in persistence and gound cover among cultivars as a result of colder 24 temperatures. Tekapo resulted in sigrificantly lower persistence at the UPES site whether gown in monoculture or binary mixtures. Perennial ryegrass: Perennial ryegass cultivars were more susceptible to winter injury. However, analysis of perennial ryegass monoculture showed there was no sigrificant winter injury in the first two years of the study at KBS, but Maverick Gold had sigiificantly higher winter injury in 2006 (Tablel). At LC, there were sigrificant differences between perennial rye gass cultivars in all years. Calibra showed sigrificantly higher persistence in each year at LC compared to other cultivars. Calibra resulted in sigrificantly higher winter hardiness and better persistence at the UPES location compared to other cultivars; however, all cultivars including Calibra were completely killed in 2006. Aries, Maverick Gold, and Quartet were all completely killed in 2005 with an injury rating of 5 while Calibra resulted in an injury rating of 3. The remaining cultivars were not significantly different in winter injury. The cultivars, Mara, Tonga, Calibra and Barfort had slightly less winter injury at LC and UPES in 2004. Perennial ryegass-clover binary mixtures resulted in less winter injury compared to the same cultivars gown in monoculture. Maverick Gold-red clover (VNS) binary mixtures at KBS had sigrificantly geater winter injury than other entries (Table 2). Similarly, data from the LC site showed sigrificantly higher winter injury (p<0.05) for the binary mixture of Aries-kura (Endura). All binary mixtures of Maverick Gold- clovers and Quartet-kura (Endura) resulted in significantly higher winter injury (p<0.05) at LC (Table 2). At the UPES, the perennial ryegass-clover mixtures of Maverick Gold had sigrificantly less persistence than all other treatments in 2004. Some treatments of 25 Calibra, Mara, and Tonga gown in binary mixtures resulted in sigrificantly less winter injury compared to other binary mixtures in 2005, however, there was considerable winter injury of those cultivars in 2006 (Table 2). Ground cover analysis of the perennial ryegass cultivars showed better persistence of cultivars established at the KBS and LC sites compared to UPES site (Table 3). Aries had sigrificantly higher in gound cover than Maverick Gold (p<0.05) at KBS in fall 2005 and spring 2006 (Table 3). At LC, lower gound cover observed for Maverick Gold, Aries and Mara in spring of 2005 and Calibra and Quartet resulted in sigrificantly higher gound cover in spring of 2006 compared to all other perennial ryegass cultivars (Table 3). At the UPES, sigrificant lower gound cover was found in Aries, Maverick Gold and Quartet during spring 2005 and sigrificantly lower for all cultivars in 2006 (Table 3). Ground cover analysis of perennial ryegass-clover binary mixtures presented in Table 4 show high gound cover at KBS and LC in 2004-2005 even with less winter- hardy cultivars. There was no sigrificant difference found for gound cover at KBS. However, at LC and UPES, sigrificant differences were found between cultivars in 2005. Analysis of the data from the UPES site showed good gound cover ratings in 2004, however, there were low gound cover ratings for all binary mixtures of perennial ryegass cultivars in 2005 (Table 4). In spring, 2005, all perennial-clover binary mixtures were sigrificantly lower in gound cover compared to binary mixtures of Calibra (Table 4). By fall 2005, all cultivars recovered from winter injury and were higher in gound 26 cover. However, in the spring of 2006, all cultivars were again lower in gound cover with ratings of less than 50 % of the fall, 2005 ratings. In summary, there was geater persistence when perennial ryegass cultivars were gown in binary mixtures compared to the same cultivars gown in monoculture. Perennial ryegass cultivars such as Maverick Gold, Aries, and Quartet had sigrificant higher winter injury at LC and UPES, where colder winter temperatures prevail compared to the KBS location. Tall fescue: Winter injury analyses of the three tall fescue monoculture cultivars (Bronson, K5666V and Barolex) showed Bronson to have sigrificantly less winter injury than Barolex at LC in 2005. No sigrificant differences were found between tall fescue cultivars at LC in 2006. However, in 2004, Bronson was sigrificantly lower winter injury than K5666V and Barolex (Table 1). There was more winter injury at the UPES site for all cultivars in 2006 with scores ranging from 3 for Bronson and 5 for K5666V and Barolex. Bronson resulted in sigrificantly less winter injury than K5666V and Barolex at the UPES in 2006 (Table 1). These data show Bronson has significantly higher winter hardiness than the other cultivars in this study. Bronson is well adapted to all latitudes in Michigan. Winter injury analyses of tall fescue-clover binary mixtures from at locations showed little winter injury (Table 2). However, K5666V resulted in sigrificantly higher winter injury than Bronson when gown with 3 of the 5 clover species and cultivars in 2005 at LC and UPES. 27 Ground cover of all tall fescue monoculture showed excellent cover across all locations (Table 3). However, at LC, Barolex was sigtificantly higher in gound cover than K5666V and Bronson in spring 2005. K5666V was sigrificantly lower in gound cover compared to Bronson at UPES in 2005 while both K5666V and Barolex were sigrificantly lower in gound cover than Bronson in the spring of 2006 at the UPES (Table 3). Ground cover analysis of tall fescue-clover binary mixtures is presented in Table 4. There was higher gound cover for all years and locations (score 4 to 5) with binary mixtures compared to monoculture of tall fescue. Bronson tall fescue gown in binary mixtures of Ladino white clover and VNS red clover was sigrificantly higher in gound cover in 2005 at the UPES compared to other binary mixtures and tall fescue cultivars. There were no differences in gound cover between cultivars and species of clovers in any other treatments and years. These data indicate better gound cover when tall fescue is gown with clovers compared to tall fescue gown in a monoculture. In conclusion, the endophyte free tall fescue cultivars used in this study demonstrated an excellent persistence whether gown in monoculture or binary mixtures at KBS, LC for all years and 2004-2005 at UPES. Binary mixtures of tall fescue —clover showed geater winter hardiness and gound cover at all locations, which is likely due to better distribution of available nitrogen throughout the gowing season for tall fescue gowing in association with clovers. 28 Persistence of Clover Species Kura clover had sigrificantly less winter injury than some red and white clovers cultivars at KBS. No data were recorded at LC during 2005-2006 due to poor stands with the exception of kura clover (Endura), which did not have winter injury (Table 5). However, there was little winter injury in all cultivars at LC during 2004. Star Fire resulted in sigrificantly higher winter injury in 2004 compared to other cultivars. At UPES, kura clover had the geatest winter injury (score 3.8) among all clover cultivars (Table 5). However, this may be an anomaly as kura clover has been shown to have a high winter hardness. It is possible these results were attributed to poor establishment. Overall, there was less winter injury in the clover monocultures compared to the perennial gass monoculture. Ground cover of all clover cultivars was high (scored 3.5 to 4) at KBS in all years Table 6). There were sigrificant differences in gound cover between species or cultivars at KBS. At LC site, there were sigrificant differences between treatment means in gound cover in fall of 2004. The gound cover of kura clover at LC in the spring of 2005 resulted in a high score (3.2) (Table 6). In contrast, kura clover had low gound cover in fall of 2004 at LC, which is likely related to an initial poor stand of kura clover at seeding time due to slower establishment (Cuomo et al., 2003). At the UPES, data analyses showed sigrificantly higher gound cover scores for all white clover cultivars (K0pu 11, Alice, Jumbo and Ladino), which was likely due to excellent stolon production resulting in new plants forming. However, diseases such as root rots eliminated red clover stands (Taylor and Smith, 1995), which helped explain the low gound cover scored at the UPES (scored of 1.8) (Table 6) in spite of their persistence to cold winter. 29 At LC, higher gound cover for all the eight cultivars was found during 2004. Red and white clovers did not persist and resulted in no gound cover in the last two years (2005- 2006) III. Grass-Clover Composition in Binary Mixtures Sigrificant year X location X treatment (binary mixtures) interactions were present for spring and fall clover content (Appendix Table 6A). These interactions resulted primarily from changes in mixture compositions that occurred from year to year due to low persistence of some clovers. Statistical analysis was preformed for the entire 67 binary mixture treatments in this study. However, results were reported separately by gass species. Results presented in Tables 7, 8, 9, and 10 are the mean values of percentage clover gown with festuloliums, orchardgass, perennial ryegass and tall fescue respectively. Clover Composition in F estuloliutn -Clover Binary Mixtures: There was a sigrificant difference (p<0.05) in clover composition between the clover cultivars gown with Duo (Table 7). The clover species and cultivars gown in association with festulolium cultivars resulted in different responses from year to year and location to location. In the fall of 2004 (three years after establishment), kura clover cultivar (Endura) composition surpassed 80% (scored 5) when gown with Duo at KBS. However, kura clover composition gowing with festulolium (Duo) was sigiificantly less at both LC and UPES locations (scored 2.4 and 1.9 respectively) (Table 7). Analysis of the data showed that red clover cultivars (Star Fire, VNS) at KBS had a high clover composition (scored 4 to 5) when associated with the two festulolium cultivars during the first three years of 30 production followed by a progessive decline in their composition (scored 1 to 1.7) (Table 7). The LC site showed a high clover composition in the fall of 2005, however, much of this was from volunteer white clover, which filled in after the red clover plants died. As mentioned previously, red clover is susceptible to root rot diseases, which cause a decline in their stands (Taylor and Smith, 1995). There was low clover composition of white clover cultivars (Jumbo and Ladino) in all locations during spring 2005 and spring 2006 when associated with Hykor (scored 1 to 1.7) (Table 7). Hykor was more dominant in the binary mixture, which contributed to the lower clover botanical composition. In conclusion, Endura kura clover botanical composition increased each year when gown with festulolium (Duo) binary mixtures at the KBS location. However, this was not the case at LC or UPES locations where kura clover stands were not as competitive as kura established at KBS. A possible reason may be related to the poor establishment at LC and UPES, which resulted in lower stands over time. It may also be attributed to the highly competitive festuloliums, which gow more vigorously at northern locations. Clover Composition in Orchardgass-Clover Binary Mixtures: There was a sigrificant difference (p<0.05) in clover botanical composition between orchardgass-clover binary mixture treatments (Table 8). Previous research has suggested that orchardgass is well suited for mixtures with one or more legume species (Hoveland, 1992). Orchardgass is also characterized by the extensive tillering that occurs throughout the gowing season, 31 enabling the species to have quick re-gowth following harvest or gazing. This vigorous gowth makes this species highly competitive in binary mixtures (Casler, 1988). Red and white clover cultivars in binary mixtures with the orchardgass cultivars were lower in composition during the final two years of the study at KBS and UPES (scored 1 to 1.7) (Table 8). This may be due to less persistence in red clover caused by root rots or winter injury in white clover. At LC, however, there was moderate clover composition in the mixtures of red (VNS) and white clover (Ladino) stands when gown with Niva and red clover (Star Fire) when gowing with Tekapo (Table 8). In contrast, kura clover (Endura) resulted in sigrificantly higher composition at the KBS location when gown with Tekapo, which persisted throughout all years in this study (scored 4.3) (Table 8). These results are supported by the observations of Hoveland (1992) and Casler (1988), which concluded that orchardgass is more competitive in binary mixtures with clovers. The quick re-gowth following harvest enables orchardgass cultivars to be more dominant in the binary mixtures. In addition, with adequate moisture, kura clover is considered an excellent choice for Southern Michigan with orchardgass in binary mixtures. However, slow establishment of kura clover made it less competitive with orchardgass at LC and UPES. Perhaps if kura was seeded by itself and allowed to establish first followed by seeding the perennial gass, it would result in good stands. Clover Composition in Perennial Ryegrass-Clover Binary Mixtures: Perennial ryegass- clover binary mixtures were sigrificantly different (p<0.05) in clover composition between the seven perennial ryegass cultivars used in this study at KBS in the fall 2005 and spring 2006 (Table 9). Sigrificant differences in the clover composition 32 of perennial ryegass- clover was found in LC, spring and fall, of 2004 at UPES. There were sigrificant differences in clover composition between perennial-clover binary mixtures for all years. At KBS, kura clover (Endura) had the geatest clover composition among perennial ryegass cultivars over all years (average score 4). These results were different at the other locations. At LC, the clover composition during spring 2005 of white clover (Kopu II and Ladino) was higher when gown with Tonga. Red clover (Star Fire) composition was geater than other clovers when gown with Quartet. Clover composition of white clover (Ladino) was geater than other clovers when gown with Barfort, Tonga, Maverick Gold and Quartet at the UPES site. Alice and Kopu 11 white clover clover composition was higher when gown with Mara and Maverick Gold perennial ryegass respectively (Table 9). All red clovers gowing with perennial ryegass cultivars at KBS and UPES persisted well until the fall of 2005 but nearly disappeared by the spring of 2006 with average percentage cover rating of 1.5 (Table 9). This was likely due to root rots, which red clovers are susceptible to. On the other hand, the increase of clover composition in red clover observed in LC binary mixtures was likely related to the appearance of volunteer native legume from the soil seed bank. White clover cultivars persisted similarly to red clovers at KBS (Ladino, Kopu 11, Alice and Jumbo) with good clover cover until the spring of 2006. In conclusion, kura clover’s persistence was excellent with all perennial ryegass cultivars at the KBS location and though to a lesser extent at the LC site. A study conducted by Cuomo et al. (2003) in Minnesota showed that kura clover was able to 33 compete, persist, and spread under intermittent gazing and has the potential to be an important and persistent component of cool-season gass pasture in north-central USA. However, white clovers, in particular, Kopu II and Ladino were higher in clover composition (scored 3 to 4) at the UPES site compared to red clover and kura clover cultivars. The initial stand of kura clover at the UPES site was not as good as the other two locations, which may have contributed to the lower botanical composition with perennial gasses at this site. Clover Composition in T all F escue-Clover Binary Mixtures: Tall fescue cultivars (Barolex, K5666V and Bronson) were more competitive with all clover species at all locations (average scores from 1.3 to 3) (Table 10). Results showed kura clover composition was sigrificantly geater than all other clovers when gown in binary mixtures with K5666V cultivar at the KBS location (average score 3.9) (Table 10). Tall fescue was more aggessive when gown with all clover species compared to some cultivars of festulolium, orchardgass, and perennial ryegass. Tall fescue resulted in good stand persistence at all locations. This species should be considered when developing new pastures. However, according to this study, white and red clover cultivars may need to be reseeded more often when associated with tall fescue with the exception of kura clover, which showed better compatibility than other species when gown with tall fescue (K5666V) at KBS (Table 10). In conclusion, binary mixtures behaved differently depending on the gass and clover gowing in the mixtures. There was variation in clover composition among gass cultivars and years. For example, some gass cultivars that had low clover composition 34 in LC in the first two years showed excellent clover composition in the fall of 2005 such as festuloliums (Duo)-red clover (Star Fire) (Table 7), orchardgass (N iva)-red clover (VN S) (Table 8), and most perennial ryegass cultivars (Table 9). This was likely due to winter injury in gass cultivars resulting in little or no gass competition and higher composition of clover in these binary mixtures. IV. Dry Matter Yield of Grass And Clover Cultivars Grown in Monoculture And Binary Mixtures. Seasonal differences in DM production of species and cultivars occurred across gazing events and locations. There was also an overall decline in DM production in time across species. Sigrificant year X location X cut X treatment (binary mixtures) interactions were observed in DM yield (Appendix Table 9 A). In addition, sigrificant year X location X cut X treatment (varieties) interactions in DM yield was found in clover monocultures (Appendix Table 11 A). These interactions are primarily due to changes in DM yield production resulting from different weather conditions, locations and variation among cultivars. DM yield (tons acre") analyses were reported for each individual location, year, and cutting event. However, there was no interaction between gass monoculture treatments (Appendix Table 10 A). These data are presented by location, where Tables 11, 12 and 13 present the mean values of the gass monoculture yield at KBS, LC and UPES respectively; Tables 14, 15 and 16 give the mean yield values of the gass-clover binary mixtures at KBS, LC and UPES respectively and Tables 17, 18, and 19 provide the mean yield values of clover monoculture at KBS, LC and UPES locations respectively. 35 Dry Matter Yield of Grass Monocultures Yield (tons acre ") analyses of gass monocultures are presented in Tables 11,12 , and 13. Cultivar and species varied in DM yield. DM yield for each individual gass type within a cutting event are presented in details as follows: Festulolium: The monoculture Duo and Hykor were sigrificantly different in DM yield. Hykor had sigrificantly higher (p<0.05) DM yield than Duo in four of eight cutting events at KBS during 2004 and 2005 gowing season (Table 11). LC dry matter yield analysis showed Hykor was sigrificantly higher (p<0.05) than Duo in three of six cutting events during 2004-2005 (Table 12). Hykor was also sigrificantly higher at two of eight gazing events during 2004-2005 at UPES (Table 13). Total two year DM yield of Hykor was sigrificantly higher than Duo at all locations. Total DM yield production of Duo festulolium at the UPES site was geater than either KBS or LC (Tables. 11, 12 and 13), which indicates that Duo performs better in a cooler climate such as Northern Michigan. Orchardgass: There was a sigrificant difference in DM yield between monoculture orchardgass cultivars in one of eight cutting events at KBS (Table 11). There was a sigrificant difference in DM yield in two cutting events between orchardgass cultivars at LC and UPES (Table 12 and 13 respectively). Total two-year DM yield was numerically geater (tons acre ") in each monoculture orchardgass cultivar at UPES compared to KBS and LC. Perennial ryegrass: DM yield ranged from 2.37 tons acre 4 for Maverick Gold to 5.92 tons acre ‘1 for Mara at the UPES location (Table 13). Lower DM yield resulted from 36 Maverick Gold since it was severely affected by winter injury at the UPES location in 2005 (Table 13). Some of the Maverick Gold stands were recovered, but did not contribute sigrificantly to yield. Statistically, there was a sigrificant difference in DM yield between monoculture perennial ryegass cultivars in three of eight cutting events at KBS (Table 11). At the LC site, a sigrificant difference in DM yield occurred in two cutting events (Table 12). There was a sigrificant difference in DM yield in six of seven cutting events at UPES (Table 13). DM yield of perennial ryegass was excluded from the fourth cutting event (October) in 2004 at UPES due to lack of moisture that occurred in perennial ryegass cultivars at the UPES (Appendix Table 2A). Tall fescue: Monoculture tall fescue resulted in the highest DM yield among all gass species. DM yield ranged from 3.95 with K5666V at the KBS site (Table 11) to 6.88 tons acre '1 with Barolex at the UPES (Table 13). High DM yield productivity (average of 1.41 tons acre '1) for all gass cultivars was obtained at the second cutting event at UPES in 2004 (Table 13). There was a sigrificant difference in DM yield between monoculture tall fescue cultivars in four of eight cutting events at KBS (Table 11). At LC, a sigrificant difference in DM yield occurred in one of six cutting events (Table 12). At the UPES, there was a sigrificant difference in DM yield in two cutting events during 2004- 2005 (Table 13). Dry Matter Yield of Grass-Clover Binary Mixtures There were sigtificant differences in DM yield of festulolium Hykor- clover binary mixtures compared with Duo-clover mixtures and results varied between locations. For example, Hykor-Ladino binary mixtures were sigtificantly higher in DM 37 yield compared to Duo-Ladino mixtures in four of eight cutting events at KBS (Table 14), while there was no significant difference between these mixtures at the LC site (Table 15). At the UPES there was a sigrificant difference in two cutting events (Table 15). In addition, Hykor gown in binary mixture with white clover (Jumbo) and red clover (VNS) resulted in a sigrificantly higher DM yield at KBS site (Table 14). There were sigrificantly higher DM yield in Hykor binary mixtures at KBS (Table 14) and LC sites (Table 15) compared to Duo-binary mixtures. However, Duo- Star Fire red clover binary mixture was sigrificantly higher in DM yield than Hykor-red clover (VNS) and white clover (Ladino) at the UPES site (Table 16). Orchardgass- clover binary mixtures were higher in DM yield at KBS (Tables 14) and LC (Tables 15) compared to the UPES site (Tables 16). Sparta gown with VNS red clover was significantly higher yielding than other orchardgass-clover binary mixtures at the KBS location (Tablel4). Tekapo gown with VNS red clover had a sigrificantly higher DM yield at the LC location (Table 15). Orchard gass (Sparta)- jumbo white clover binary mixtures were the highest in DM yield. Tekapo associated with Endura kura clover was the lowest yielding among the orchardgsas-clover binary mixtures at the UPES location (Table 16). Even though orchardgass is considered an excellent cool season gass for binary mixtures due to its fast re-gowth and tillering ability (Hoveland, 1992), there are some factors, which might limit its success. For instance, winter injury of some orchardgass-clover binary mixtures such as Tekpao-kura (Endura), and Tekapo gowing with white clover (Kopu II and Ladino) were lower in DM yield at the UPES site (Table 16). Since orchardgass is an aggessive gass, it may crowd out associated clovers gowing in binary mixtures, thus causing reduction in clover 38 content with resultant nitrogen deficiency from lack of fixed nitrogen from lower clover content. Perennial ryegass- clover binary mixtures were highly in DM yield compared to monoculture treatments of perennial ryegass at all locations. In all locations, the total DM yield ranged from 2.05 tons acre'1 in Maverick Gold- kura (Endura) at UPES (Table 16) to 5.36 tons acre" in Calibra-red clover (VNS) at LC (Table 15). The UPES site resulted in lower DM yield of perennial ryegass-clover binary mixtures. Winter injury of non hardy perennial ryegass cultivars was likely the reason for the lower yield at this location. The low yield of the Maverick Gold-Endura kura clover binary mixture in the UPES was likely related to a combination of winter injury to the Maverick Gold perennial ryegass and poor establishment of Endura kura clover. Likewise, at the UPES the higher yield of Tonga-Star Fire red clover was likely due to geater winter hardiness of Tonga perennial ryegass and more vigorous gowth of Star Fire red clover (Table 16). Mara perennial ryegass gown with VNS red clover had sigrificantly higher DM yield than Aries-Endura kura clover, Quartet-Endura kura clover, and Quartet-Kopu II at the KBS location. Tall fescue- clover binary mixtures ranged from 3.90 to 6.29 tons acre"1 in DM yield for K5666V- Koppu II and Bronson-Endura kura clover treatments, respectively at the KBS location (Table 14). DM yield of Barolex-Start was sigrificantly higher than Barolex-Alice but not different than other Barolex-clover binary mixtures at KBS (Table 14). 39 In general, KBS, tall fescue cultivars gown in binary mixtures with clovers performed similarly to orchardgass- clover cultivars in yield but were higher than both perennial ryegass and festulolium- clover mixtures. For LC, DM yield of tall fescue- clover binary mixtures ranged from 3.96 to 5.33 tons acre'1 for K5666V-Star Fire red clover and Bronson-VNS red clover mixes (Table 15) and for the UPES, DM yield of tall fescue- clover binary mixtures ranged from 2.81 to 4. 90 tons acre'1 with Bronson-Endura kura clover and Barolex-Start red clover mixtures (Table 16). The average total DM yield of tall fescue- clover binary mixtures was geatest at the KBS location followed by LC and UPES locations. Tall fescue-clover binary mixtures appear to be a good choice for all the locations in this study. These data indicate good yield stability for tall fescue-clover binary mixtures in Michigan However, as mentioned previously, it is important to select the proper cultivars of both tall fescue and clovers as each performed differently depending on location. Dry Matter Yield of Clover Monocultures Dry matter yield of clover monoculture at KBS is presented in Table 17, at LC in Table18 and at UPES in Table 19. There was a sigrificant difference (p<0.05) in DM yield observed among clover species and cultivars within cutting events at KBS, UPES 2004-2005 and LC 2004. Endura kura clover resulted in sigrificantly higher total DM yield than red clover (VNS) and white clover (Kopu II, Alice and Ladino) KBS (Table 17). At LC, DM yield ranged from 1.95 to 3.24 tons acre'l at LC with Endura kura clover being also the highest in DM yield (Table 18). At UPES, no siglificant difference was found in total two year DM yield between clover species and cultivars (Table 19). 40 These data clearly showed Endura kura clover to be well adapted to southern Michigan where it had the highest yield of all clover cultivars in this study. Some cultivars of clover such as red clover (VNS) and white clover (Kopu II) had higher total one-year production at LC (Table 18) than the same cultivars produced in two years at the UPES site (Table 19). CONCLUSIONS Grass-clover binary mixtures resulted in increased DM yield and had higher resistance to winter injury compared to gasses and clovers in monoculture. However, this study demonstrated the importance of proper species and cultivar selection. Grass and clover species in binary mixtures showed sigrificant differences between species and cultivars. In the early part of this study, there was a balance in botanical composition between gass and clover content. However, this balance disappeared after two seasons with either the gass or clover soon becoming more or less dominant. Vigorous gass species such as tall fescue and orchardgass tended to be more dominating in the mixtures resulting in decreased clover content. In contrast, some clovers persisted better than gasses. Environmental conditions are a factor that changes the gass-clover balance (Camlin, 1981). Thus, winter injury leading to a loss in vegetative gound cover of some gasses, especially perennial ryegass provided an opportunity for the associated clover to dominate the mixtures. When clover disappeared from the binary mixtures, there was limited nitrogen (N) fixation, which resulted in nitrogen deficiency and subsequent loss of DM yield of the associated gass species. Therefore, when the clover content becomes low in the mixtures, nitrogen application is 41 necessary to maintain high DM yield. This study demonstrated the importance of compatible clovers and gasses species in binary mixtures. Non-winter hardy cultivars of gass such as perennial ryegass (Maverick Gold and Aries) used in this study showed geater persistence when they were gown in binary mixtures due to reduced winter injury. Nitrogen fixation by clovers has a positive effect upon winter survival of perennial gasses. In binary mixtures, available nitrogen from N fixation of clover is provided to gasses in the critical spring and summer months in a steady supply. However, in the fall months, N fixation slows in clovers with subsequent less N available to gasses resulted in hardening of gasses and better winter hardness. Insulation from snow cover also increases gass survival in the winter (Leep et al., 2001). Growing gass with clover in binary mixtures can help to intercept snow resulting in less winter injury. Binary mixtures of clover and gass resulted in a higher total DM yield and more uniform dry matter distribution through the season. These results are similar to those observed by Charnblee and Collins (1988). Tall fescue resulted in excellent yield stability and broad adaptation to different environments compared to other gass species in this study, while perennial ryegass yield was found to be unstable. However, there were siglificant differences in the performance of perennial ryegasses cultivars due to differences winter hardiness. Kura clover (Endura) provided the highest DM yield and exceptional persistence under gazing compared to other clover cultivars in this study, particularly at 42° N 42 latitude zone. Thus, the influence of latitude on the performance of clover was observed in this study. Kura clover (Endura) demonstrated the highest persistence, which is similar to results found by Woodman et al., (1992). However, the establishment of kura is somewhat difficult, as it gows more slowly during the establishment year than other clover species (Speer and Allinson, 1985). For northem latitudes, kura clover dry matter yield was low due to the poor establishment, which indicates that improved establishment of this species need more attention for it to be successful in binary mixtures. 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The mean values of winter injury rating of 16 gass cultivars established in monoculture at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (U PES) over a three-year period. Grass Grass KBS LC UPES Species cultivars 20041200512006 3-yr ave 20041200512006 3-yr ave120041200512006 3-yr ave Duo 1.6 1.0 1.0 1.2 1.6 2 2.3 2.0 1.8 4.3 5.0 3.7 Fest Hykor 1.3 1.0 1.0 1.1 1.0 1.0 1.0 1.0 1.3 1.0 2.0 1.4 Tekapo 1.5 1-0 1-0 1.2 1.0 2.7 1.0 1.6 1.3 3.0 5.0 3.1 Amba 1.1 1-0 1-0 1.0 1.0 1.4 1.0 1.1 2.0 2.0 2.8 2.3 OR Niva 1-0 1-0 1-0 1.0 1.1 1.5 1.0 1.2 1-0 1.6 3.3 2.0 Sparta 1-0 1-0 1.0 1.0 1.6 1.4 1-0 1.3 1-0 1.3 4.0 2.1 Aries 1.8 1.2 1.2 1.4 3.0 4.4 5.0 4.1 4.1 5.0 5.0 4.7 MvrckGld 2.0 1.8 4.0 2.6 4.0 3.7 4.3 4.0 4.0 5.0 5.0 4.7 Quartet 2.1 1.0 1.0 1.4 3.0 3.7 4.0 3.6 2.6 5.0 5.0 4.2 PR Tonga 1.3 1.0 1.0 1.1 1.8 3.0 3.0 2.6 2.1 4.0 5.0 3.7 Barfort 1.5 1.0 1.0 1.2 2.0 3.0 3.0 2.7 2.0 4.0 5.0 3.7 Mara 1.5 1.0 1.0 1.2 2.6 4.4 3.3 3.4 2.0 4.0 5.0 3.7 Calibra 1.3 1.0 1.0 1.1 2.0 2.7 1.3 2.0 1.8 3.3 5.0 3.4 Bronson 1.0 1.0 1.0 1,0 1.0 1.0 1.0 1.0 1.0 1,3 3,5 1,9 TF K5666V 1.5 1.0 1.0 1.2 1.1 1.4 1.0 1.2 1.5 2.8 5.0 3.1 Barolex 1.6 1-0 1-0 1.2 2.0 2.5 1.3 1.9 2.0 2.3 5.0 3.1 Mean 1.4 1.1 1.2 1.6 2.5 2.2 1.8 3.1 4.4 cv 27.2 9.9 6.0 35.9 33.0 23.9 34.8 15.4 5.9 LSD (0.05) 0.6 0.2 0.2 0.9 1.4 0.8 1.1 0.8 0.4 1= less than 20% of the vegetation was killed. 5= Greater than 80% of the vegetation was killed. Fest=Festulolium ; OR=Orchardgrass, PR=Perennial ryegass and TF= Tall fescue. 51 Table 2. The mean values of winter injury rating of 67 gass-clover binary mixture treatments established at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (U PES) over a three-year period (continued on the next page). Grass Clover KBS LC UPES Cultivars Cultivars ‘041 ‘051 ‘06 AVE ‘04 I ‘051‘06 AVE 04105 I ‘06 AVE Duo Endura 1.6 1.0 1.0 1.2 1.5 1.3 2.3 1.7 2.0 4.0 4.7 3.6 Duo StarFire 1.6 1.0 1.0 1.2 1.0 2.8 1.7 1.8 2.1 4.3 4.7 3.7 Duo VNS 1.6 1.0 1.0 1.2 1.6 1.0 2.7 1.8 1.8 3.7 4.5 33 Duo Ladino 2.0 1.0 1.0 13 1.3 2.5 3.5 2.4 1.5 4.7 4.7 3.6 Duo Kopu 11 1.6 1.0 1.0 1.2 1.2 2.0 2.7 2.0 1.3 4.3 4.8 3.5 Hykor VNS 1.0 1.0 1.0 1.0 1.3 1.0 1.0 1.1 1.0 1.3 1.0 1.1 Hykor Jumbo 1.5 1.0 1.0 1.2 1.5 1.6 1.3 1.5 1.0 1.2 1.0 1.1 Hykor Ladino 1.0 1.0 1.0 1.0 1.1 1.0 1.0 1.0 1.0 1.5 1.0 1.2 Amba VNS 1.8 1.0 1.0 1.3 1.3 1.1 2.3 1.6 1.0 1.0 1.0 1.0 Amba Jumbo 1.6 1.0 1.0 1.2 1.0 1.3 1.0 1.1 1.0 1.2 1.7 1.3 Amba Ladino 1.0 1.0 1.0 1.0 1.1 1.0 1.3 1.1 1.1 1.0 1.3 1.1 Niva VNS 1.1 1.0 1.0 1.0 1.1 1.1 2.0 1.4 1.0 1.0 1.0 1.0 Niva Jumbo 1.1 1.0 1.0 1.0 1.0 1.5 2.3 1.6 1.0 1.0 1.7 1.2 Niva Ladino 1.0 1.0 1.0 1.0 1.7 1.6 2.3 1.9 1.0 1.0 1.3 1.1 Sparta VNS 1.0 1.0 1.0 1.0 1.5 1.1 2.3 1.6 1.3 1.0 1.5 1.3 Sparta Jumbo 1.1 1.0 1.0 1.0 1.0 1.1 2.3 1.5 1.0 1.0 2.2 1.4 Sparta Ladino 1.1 1.0 1.0 1.0 1.0 2.1 2.7 1.9 1.3 1.0 2.2 1.5 Tekapo Endura 1.1 1.0 1.0 1.0 1.3 1.0 1.0 1.1 1.3 2.0 3.3 2.2 Tekapo VNS 1.3 1.2 1.2 1.2 1.3 1.2 2.3 1.6 1.1 2.0 2.5 1.9 Tekapo Star Fire 1.5 1.0 1.0 1.2 1.5 2.5 3.7 2.6 1.1 2.0 2.8 2.0 Tekapo Kopu II 1.6 1.0 1.0 1.2 1.1 1.1 2.6 1.6 1.6 3.0 4.0 2.9 Tekapo Ladino 1.3 1.0 1.0 1.1 1.0 2.0 1.0 1.3 1.8 2.8 3.8 2.8 Aries Endura 1.6 1.0 1.0 1.2 2.6 3.6 4.0 3.4 2.1 4.7 4.8 3.9 Aries VNS 2.3 1.5 1.5 1.8 2.1 2.5 3.7 2.8 3.0 4.7 5.0 4.2 Aries Star Fire 2.1 1.0 1.0 1.4 1.8 1.2 2.3 1.8 3.0 4.7 5.0 4.2 Aries Kopu II 1.5 1.0 1.0 1.2 2.3 3.0 3.5 2.9 2.1 5.0 5.0 4.0 Aries Ladino 1.5 1.0 1.0 1.2 1.6 2.3 2.7 2.2 1.8 5.0 5.0 3.9 Barfort VNS 1.5 1.0 1.0 1.2 1.8 1.6 2.7 2.0 2.1 3.3 3.8 3.1 Barfort Start 1.6 1.0 1.0 1.2 2.0 1.5 3.0 2.2 1.6 3.0 4.5 3.0 Barfort Alice 1.6 1.0 1.0 1.2 2.0 2.3 2.7 2.3 1.3 4.3 5.0 3.5 Barfort Ladino 1.3 1.0 1.0 1.1 1.8 2.3 2.8 2.3 1.0 4.3 5.0 3.4 Calibra VNS 1.5 1.2 1.2 1.3 1.0 1.7 2.7 1.8 1.3 1.6 3.8 2.2 Calibra Jumbo 1.1 1.0 1.0 1.0 1.6 1.8 1.0 1.5 1.1 3.3 4.7 3.0 Calibra Ladino 1.6 1.0 1.0 1.2 1.6 3.1 2.3 2.3 1.0 3.0 4.2 2.7 Mara VNS 1.3 1.0 1.0 1.1 1.8 2.0 1.0 1.6 1.5 3.0 3.0 2.5 Mara Start 1.6 1.0 1.0 1.2 2.3 2.5 3.0 2.6 1.3 3.8 4.3 3.1 Mara Alice 1.1 1.0 1.0 1.0 2.0 2.0 1.8 1.9 1.5 4.2 5.0 3.6 52 Table 2 continued Orchardgass (Amba, Niva, Sparta and Tekapo) Perennial ryegass (Aries, Barfort, Calibra, Mara, Maverick Gold, Quartet, and Tonga,) Tall fescue (Bronson, K5666V, and Barolex) Clover cultivars: Red clover (Start Fire, Start and VNS); white clover (Ladino, Alice, Kopu II and Jumbo); Kura (Endura) 53 Grass Clover KBS LC UPES Cultivars Cultivars ‘04 1 ‘05 1 ‘06 AVE ‘04 1 ‘05] ‘06 AVE ‘04 1 ‘05 I ‘06 AVE Mara Ladino 1.0 1.0 1.0 1.0 2.1 1.3 1.7 1.7 1.3 3.3 4.0 2.9 Mvck G Endura 2.0 1.4 1.3 1.6 2.3 3.3 4.0 3.2 4.6 5.0 5.0 4.9 Mvck G VNS 2.3 2.2 2.2 2.2 2.1 3.0 4.0 3.0 4.1 5.0 5.0 4.7 Mvck G Star Fire 2.0 1.4 1.3 1.6 2.6 4.0 4.3 3.6 3.6 5.0 5.0 4.5 Mvck G Kopu II 2.3 1.0 1.0 1.4 2.5 3.6 3.7 3.3 2.8 5.0 5.0 4.3 Mvck G Ladino 2.1 1.0 1.0 1.4 2.8 3.0 4.3 3.4 2.8 5.0 5.0 4.3 Quartet Endura 1.3 1.0 1.0 1.1 1.5 3.5 4.0 3.0 1.3 3.7 5.0 3.3 Quartet VNS 2.0 1.0 1.0 1.3 1.6 3.1 4.3 3.0 2.0 3.7 5.0 3.6 Quartet Ladino 1.5 1.0 1.0 1.2 1.5 1.1 3.0 1.9 2.0 5.0 5.0 4.0 Quartet Star Fire 2.0 1.0 1.0 1.3 1.3 1.3 2.7 1.8 2.0 4.2 4.8 3.7 Quartet Kopu II 2.0 1.0 1.0 1.3 1.5 1.8 3.0 2.1 2.0 4.5 4.7 3.7 Tonga Endura 1.3 1.0 1.0 1.1 1.1 2.4 3.3 2.3 1.0 2.7 4.0 2.6 Tonga VNS 1.6 1.0 1.0 1.2 1.0 2.4 3.7 2.4 1.3 3.0 4.7 3.0 Tonga Star Fire 2.0 1.0 1.0 1.3 1.0 1.6 2.3 1.6 1.0 3.7 4.7 3.1 Tonga Kopu II 1.3 1.0 1.0 1.1 1.1 1.0 1.7 1.3 1.1 4.0 4.7 ‘ 3.3 Tonga Ladino 1.5 1.0 1.0 1.2 1.1 1.1 2.7 1.6 1.3 5.0 5.0 3.8 Bronson VNS 1.3 1.0 1.0 1.1 1.0 1.2 1.0 1.1 1.1 1.3 1.0 1.1 Bronson Endura 1.5 1.0 1.0 1.2 1.0 1.2 1.0 1.1 1.0 2.3 1.0 1.4 Bronson Kopu II 1.5 1.0 1.0 1.2 1.1 1.1 2.0 1.4 1.0 1.3 1.0 l l Bronson Ladino 1.1 1.0 1.0 1.0 1.0 1.0 1.0 1.0 1.0 1.3 1.0 Bronson Star Fire 1.1 1.0 1.0 1.0 1.1 1.3' 1.3 1.2 1.3 1.6 1.0 1.3 K5666V VNS 1.6 1.0 1.0 1.2 1.3 2.4 2.0 1.9 1.8 2.3 1.3 1.8 K5666V Endura 1.1 1.0 1.0 1.0 1.5 2.4 1.7 1.9 1.6 2.0 1.0 1.5 K5666V Kopu II 1.8 1.0 1.0 1.3 1.1 2.1 2.2 1.8 1.8 2.0 1.3 1.7 K5666V Ladino 1.3 1.0 1.0 1.1 1.1 1.1 1.2 1.1 2.0 1.8 1.3 1.7 K5666V Star Fire 1.3 1.0 1.0 1.1 1.6 1.0 1.0 1.2 1.5 2.0 1.7 1.7 Barolex Alice 1.6 1.0 1.0 1.2 1.8 1.4 1.0 1.4 1.0 1.6 1.0 1.2 Barolex VNS 1.5 1.0 1.0 1.2 1.0 1.0 1.3 1.1 1.3 1.6 1.3 1.4 Barolex Ladino 1.3 1.0 1.0 1.1 1.0 1.0 1.3 1.1 1.1 1.8 1.0 1.3 Barolex Start 1.5 1.0 1.0 1.2 1.3 1.7 2.0 1.7 1.3 1.5 1.3 1.4 Mean 1.5 1.0 1.0 1.5 I 1.8 2.4 1.6 2.9 33 CV 29 20 20 28 1 47 51 23 l9 l4 LSD(0.05) 0.7 0.3 0.4 0.7 1 0.0 0.0 0.6 0.9 0.8 _ 1= less than 20% of the vegetation killed; 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Dry matter yield (tons acre") of 16 grass cultivars established in monoculture at Kellogg Biological Research (KBS) over a two-year period. 2004 2005 Grass 24- 24- 26- 9- 4- 14- 2- 13- Total Species / Cultivars May Jun Jul Sep Max Jun Aug Oct 2-yr DM tons acre”1 Duo 0.75 0.52 0.27 0.29 0.41 0.16 0.31 0.13 2.84 Fest Hykor 1.08 0.84 0.82 0.39 1.16 0.56 0.51 0.30 5.66 Tekapo 1.04 0.56 0.61 0.27 0.60 0.73 0.50 0.26 4.57 OR Amba 0.85 0.82 0.46 0.20 0.88 0.33 0.39 0.22 4.15 Niva 0.99 0.72 0.62 0.24 0.84 0.54 0.40 0.28 4.63 Sparta 0.95 0.84 0.73 0.23 0.91 0.55 0.49 0.30 5.00 Aries 0.87 0.64 0.47 0.63 0.83 0.38 0.34 0.26 4.42 Maverick Gold 0.79 0.95 0.46 0.16 0.63 0.38 0.38 0.21 3.96 PR Quartet 0.40 0.43 0.24 0.33 0.70 0.70 0.35 0.26 3.41 Tonga 0.81 0.34 0.50 0.16 0.82 0.24 0.25 0.20 3.32 Barfort 0.64 0.41 0.54 0.28 0.75 0.20 0.28 0.20 3.30 Mara 0.77 0.58 0.50 0.23 0.74 0.45 0.37 0.53 4.17 Calibra 0.60 0.56 0.43 0.63 0.65 0.47 0.25 0.22 3.81 Bronson 0.69 0.70 0.90 0.74 0.86 0.65 0.78 0.47 5.79 TF K5666V 0.79 0.52 0.83 0.42 0.58 0.29 0.30 0.22 3.95 Barolex 0.82 1.02 1.03 0.46 0.68 0.38 0.54 0.30 5.23 Mean 0.8 0.6 0.6 0.4 0.8 0.4 0.4 0.3 4.3 CV 46.2 38.9 39.0 92.3 48.9 42.3 35.6 36.1 18.4 LSD (0.05) 0.6 0.4 0.4 0.5 0.6 0.3 0.2 0.2 1.3 65 Table 12. Dry matter yield (tons acre'l) of 16 grass cultivars established in monoculture at Lake City (LC) over a two-year period. Grass 2004 2005 Total Species / Cultivars 19-May I 21-Jun I S-Aug 23-Mafl 7-Jul I 9-Aug 2-yr DM tons acre' Duo 0.51 0.88 0.51 0.37 0.44 0.44 3.15 Fest Hykor 0.91 0.74 0.74 0.55 0.87 0.89 4.70 Tekapo 0.73 0.69 0.85 0.18 0.57 0.27 3.29 OR Amba 0.89 0.56 0.69 0.57 0.47 0.24 3.42 Niva 0.71 0.70 0.77 0.46 0.26 0.34 3.24 Sparta 1.12 0.71 0.86 0.61 0.52 0.51 4.33 Aries 0.35 0.72 0.54 0.35 0.33 0.25 2.54 Maverick Gold 0.14 0.45 0.62 0.69 0.35 0.42 2.67 PR Quartet 0.42 0.84 0.43 0.33 0.34 0.43 2.79 Tonga 0.50 0.44 0.32 0.44 0.47 0.32 2.49 Barfort 0.28 1.25 0.61 0.20 0.48 0.29 3.11 Mara 0.24 1.24 0.51 0.18 0.47 0.37 3.01 Calibra 0.52 0.84 0.34 0.23 0.55 0.33 2.81 Bronson 0.91 0.93 0.94 0.48 0.52 0.46 4.24 TF K5666V 1.05 0.96 0.79 0.70 0.53 0.43 4.46 Barolex 0.63 0.87 0.78 0.65 0.50 0.74 4.17 Mean 0.7 0.9 0.6 0.4 0.5 0.4 3.4 CV 36.6 25.1 33.4 55.7 43.2 51.3 17.0 LSD( 0.05) 0.4 0.4 0.3 0.4 0.3 0.4 1.2 66 Table 13. Dry matter yield (tons acre'l) of 16 grass cultivars established in monoculture at Upper Peninsula Experiment Station (UPES) over a two- year period. 2004 2005 Grass 7- 12- 22- 17- 1- 10- 23- 29- Total Species / Cultivar Jun Jul Aug Oct Jun Jul Aug Sep 2-yr DM tons acre'l Duo 0.56 1.67 0.48 0.30 0.63 0.47 0.45 0.65 5.21 Fest Hykor 0.86 1.12 1.30 0.27 0.80 0.56 0.87 0.79 6.57 Tekapo 0.94 1.33 0.96 0.31 0.72 0.64 0.60 0.77 6.27 OR Amba 1.06 1.25 0.70 0.30 1.04 0.37 0.46 0.60 5.78 Niva 0.78 1.09 0.93 0.28 0.97 0.66 0.70 0.57 5.98 Sparta 0.82 1.11 1.01 0.30 1.01 0.56 0.62 0.54 5.97 Aries 0.23 1.27 0.43 0.00 0.10 0.31 0.00 0.15 2.49 Maverick Gold 0.36 0.78 0.58 0.00 0.00 0.37 0.00 0.28 2.37 PR Quartet 0.42 1.76 0.35 0.00 0.16 0.33 0.12 0.42 3.56 Tonga 0.59 1.44 0.74 0.00 0.60 0.42 0.48 0.54 4.81 Barfort 0.75 1.93 0.59 0.00 0.67 0.30 0.54 0.77 5.55 Mara 0.86 2.03 0.92 0.00 0.58 0.36 0.62 0.55 5.92 Calibra 0.74 1.71 0.62 0.00 0.58 0.58 0.51 0.85 5.59 Bronson 0.82 1.23 1.19 0.38 0.65 0.65 0.92 0.71 6.55 TF K5666V 0.80 1.31 0.96 0.19 0.32 0.51 0.72 0.74 5.55 Barolex 1.02 1.47 1.09 0.25 0.78 0.62 0.84 0.81 6.88 Mean 0.7 1.4 0.8 0.3 0.6 0.5 0.5 0.6 . 5.3 CV 34.2 25.4 31.6 17.78 23.4 44.9 24.6 23.1 10.7 LSD(0.05) 0.4 0.6 0.4 0.1 0.2 0.4 0.2 0.2 0.9 Data of Perennial ryegrass cultivars in last cutting event of 2004 were not included 67 Table 14. Dry matter yield (tons acre") of 67 grass- clover binary mixtures treatments established at Kellogg Biological Research (KBS) over a two-year period (continued on the next page). 2004 2005 Grass Clover Total Cultivars Cultivars 24-Maj 24-Jun 26—Ju1 9-Sep 4-May 14-Jun Z-Qg l3-Oct 2-yr DM tons acre‘I Duo Endura 0.91 0.53 0.52 0.72 0.48 0.55 0.28 0.28 4.27 Duo Star Fire 0.57 0.67 0.77 0.63 0.75 0.71 0.30 0.24 4.64 Duo VNS 0.65 0.70 0.62 0.71 0.85 0.65 0.30 0.38 4.86 Duo Ladino 0.83 0.60 0.51 0.57 0.35 0.57 0.24 0.22 3.89 Duo Kopu II 0.60 0.48 0.54 0.53 0.76 0.57 0.32 0.25 4.05 Hykor VNS 0.92 0.84 0.66 0.61 0.99 0.65 0.68 0.43 5.78 Hykor Jumbo 0.75 0.78 1.06 0.96 1.07 0.64 0.62 0.60 6.48 Hykor Ladino 0.85 0.62 0.93 0.85 1.34 0.41 0.78 0.54 6.32 Amba VNS 0.54 0.62 0.52 1.32 0.54 0.56 0.60 0.24 4.94 Amba Jumbo 0.22 0.91 0.74 0.62 0.60 0.40 0.50 0.26 4.25 Amba Ladino 0.66 0.61 0.75 0.79 0.74 0.40 0.54 0.34 4.83 Niva VNS 0.51 0.64 0.66 0.82 0.60 0.48 0.55 0.36 4.62 Niva Jumbo 0.75 0.64 0.66 0.77 0.50 0.45 0.55 0.30 4.62 Niva Ladino 0.61 0.71 0.71 0.44 0.85 0.62 0.60 0.35 4.89 Sparta VNS 0.73 0.75 1.02 0.70 0.83 0.48 0.50 0.36 5.37 Sparta Jumbo 0.75 0.75 0.91 0.49 0.63 0.32 0.40 0.24 4.49 Sparta Ladino 0.55 0.75 0.56 0.56 0.61 0.44 0.48 0.32 4.27 Tekapo Endura 0.80 0.69 0.62 0.64 0.76 0.68 0.42 0.38 4.99 Tekapo VNS 0.64 0.89 0.59 0.99 0.66 0.73 0.47 0.28 5.25 Tekapo Star Fire 0.79 0.81 0.60 0.67 0.58 0.35 0.53 0.41 4.74 Tekapo Kopu II 0.60 0.62 0.54 0.72 0.60 0.38 0.43 0.37 4.26 Tekapo Ladino 0.94 0.60 0.73 0.57 0.73 0.70 0.45 0.34 5.06 Aries Endura 0.53 0.61 0.44 0.37 0.59 0.40 0.30 0.32 3.56 Aries VNS 0.62 0.48 0.47 0.65 0.48 0.26 0.43 0.26 3.65 Aries Star Fire 0.78 0.44 0.83 0.92 0.53 0.55 0.38 0.30 4.73 Aries Kopu H 0.62 0.61 0.40 0.52 0.65 0.51 0.40 0.28 3.99 Aries Ladino 0.72 0.69 0.75 0.74 0.51 0.43 0.36 0.18 4.38 Barfort VNS 0.99 0.56 0.69 0.55 0.40 0.37 0.35 0.34 4.25 Barfort Start 0.64 0.58 0.56 0.68 0.55 0.96 0.35 0.22 4.54 Barfort Alice 0.65 0.76 0.51 0.51 0.48 0.43 0.25 0.21 3.80 Barfort Ladino 0.78 0.70 0.42 0.38 0.44 0.48 0.31 0.25 3.76 Calibra VNS 0.54 0.44 0.46 0.98 0.78 0.37 0.32 0.36 4.25 Calibra Jumbo 0.83 0.58 0.59 0.58 0.66 0.44 0.41 0.30 4.39 Calibra Ladino 0.71 0.58 0.34 0.47 0.70 0.48 0.39 0.24 3.91 Mara VNS 0.69 0.54 0.89 0.85 0.53 0.53 0.44 0.31 4.78 Mara Start 1.05 0.73 0.32 0.65 0.65 0.37 0.51 0.33 4.61 Mara Alice 0.74 0.66 0.57 0.62 0.43 0.50 0.43 0.40 4.35 Mara Ladino 0.29 0.71 1.03 0.77 0.45 0.51 0.50 0.37 4.63 Mav. Gold Endura 0.74 0.60 0.42 0.65 0.76 0.64 0.34 0.00 4.15 Mav. Gold VNS 0.64 0.58 0.73 0.82 0.59 0.46 0.19 0.00 4.01 Mav. Gold Star Fire 0.71 0.71 0.95 0.64 0.80 0.62 0.52 0.00 4.95 Mav. Gold Kopu II 0.81 0.57 0.52 0.69 0.47 0.76 0.40 0.00 4.22 Mav. Gold Ladino 0.65 0.66 0.44 0.61 0.48 0.75 0.39 0.00 3.98 Quartet Endura 0.47 0.47 0.62 0.51 0.50 0.53 0.26 0.21 3.57 Quartet VNS 0.99 0.40 0.63 0.50 0.52 0.38 0.30 0.36 4.08 68 Table 14 continued 2004 2005 Grass Clover Total Cultivars Cultivars 24-May 24-Jun 26-Jul 9-Sep 4-May 14-Jun 2-Aug 13-Oct 2- r Quartet Ladino 0.78 0.61 0.53 0.65 0.50 0.55 0.28 0.22 4.12 Quartet Star Fire 0.75 0.71 0.63 0.77 0.45 0.61 0.35 0.22 4.49 Quartet Kopu II 0.89 0.60 0.44 0.59 0.24 0.33 0.25 0.25 3.59 Tonga Endura 0.70 0.57 0.54 0.60 0.90 0.48 0.38 0.25 4.42 Tonga VNS 0.52 0.60 0.69 0.89 0.78 0.50 0.31 0.20 4.49 Tonga Star Fire 0.42 0.60 0.67 0.59 0.50 0.51 0.40 0.23 3.92 Tonga Kopu II 0.60 0.65 0.84 0.64 0.43 0.45 0.33 0.18 4.12 Tonga Ladino 0.59 0.60 0.67 0.59 0.58 0.34 0.26 0.12 3.75 Bronson VNS 0.99 0.64 0.68 0.83 0.82 0.80 0.47 0.65 5.88 Bronson Endura 0.73 0.59 0.87 0.95 1.20 0.84 0.51 0.60 6.29 Bronson Kopu II 0.55 0.67 0.82 0.86 0.81 0.43 0.55 0.28 4.97 Bronson Ladino 0.84 0.74 0.75 0.61 0.73 0.70 0.40 0.54 5.31 Bronson Star Fire 0.64 0.67 0.44 0.86 1.03 0.64 0.55 0.58 5.41 K5666V VNS 0.57 0.55 0.86 0.91 1.30 0.40 0.42 0.66 5.67 K5666V Endura 0.97 0.72 0.55 0.54 0.64 0.52 0.27 0.40 4.61 K5666V Kopu II 0.61 0.52 0.59 0.44 0.54 0.50 0.32 0.38 3.90 K5666V Ladino 0.86 0.72 0.79 0.74 0.67 0.54 0.41 0.47 5.20 K5666V Star Fire 0.59 0.54 0.65 0.88 0.71 0.68 0.36 0.47 4.88 Barolex Alice 0.73 0.99 0.68 0.59 0.46 0.56 0.44 0.28 4.73 Barolex VNS 0.73 0.77 0.84 0.69 0.64 0.75 0.69 0.51 5.62 Barolex Ladino 0.51 0.85 1.07 0.79 0.74 0.76 0.61 0.40 5.73 Barolex Start 0.93 0.70 0.99 0.85 0.69 0.74 0.51 0.56 5.97 Mean 0.7 0.6 0.7 0.7 0.6 0.5 0.4 0.3 4.6 CV 33 30 37 41 36 36 26 41 16 LSD(0.05) 0.4 0.3 0.4 0.4 0.4 0.3 0.2 0.2 1.2 Grass cultivars: F estulolium (Duo and Hykor) Orchardgrass (Amba, Niva, Sparta and Tekapo) Perennial ryegrass (Aries, Barfort, Calibra, Mara, Maverick Gold, Quartet, and Tonga,) Tall fescue (Bronson, K5666V, and Barolex) Clover cultivars: Red clover (VNS', Star Fire, and Start) White clovers (KopuII, ladino, Alice, and Jumbo) Kura clover (Endura) ‘ Variety Not Stated 69 Table 15. Dry matter yield (tons acre") of 67 grass- clover binary mixtures treatments established at Lake City (LC) over a two -year period (continued on the next page). 2004 2005 Grass Clover Total Cultivars Cultivars l9-May 21-Jun 5-Aug 7-Sep 23-May 7-Ju1 9-Aug 2-Oct 2-yr DM tons acre'I Duo Endura 0.64 0.99 0.27 0.41 0.23 0.63 0.29 0.28 3.74 Duo Star Fire 1.00 0.81 0.36 0.71 0.46 0.38 0.35 0.31 4.38 Duo VNS 0.74 1.00 0.67 0.83 0.41 0.38 0.48 0.34 4.85 Duo Ladino 0.78 1.01 0.34 0.53 0.59 0.39 0.47 0.45 4.56 Duo Kopu II 0.75 0.92 0.21 0.42 0.24 0.39 0.25 0.22 3.40 Hykor VNS 1.08 0.71 0.59 0.76 0.66 0.23 0.33 0.54 4.90 Hykor Jumbo 1.15 0.83 0.48 0.55 0.38 0.49 0.30 0.43 4.61 Hykor Ladino 1.09 0.68 0.35 0.66 0.40 0.30 0.58 0.58 4.64 Amba VNS 0.93 0.68 0.47 0.83 0.66 0.43 0.38 0.42 4.80 Amba Jumbo 0.91 0.69 0.51 0.70 0.77 0.61 0.40 0.38 4.97 Amba Ladino 0.83 0.67 0.36 0.78 0.72 0.63 0.37 0.34 4.70 Niva VNS 1.00 0.58 0.51 0.91 0.56 0.37 0.33 0.49 4.75 Niva Jumbo 0.72 0.70 0.35 0.85 0.58 0.54 0.22 0.45 4.41 Niva Ladino 0.87 0.75 0.43 0.70 0.44 0.74 0.39 0.35 4.67 Sparta VNS 0.83 0.69 0.54 0.65 0.40 0.44 0.26 0.38 4.19 Sparta Jumbo 0.8 0.65 0.44 0.82 0.50 0.27 0.31 0.31 4.10 Sparta Ladino 0.94 0.8 0.40 0.63 0.81 0.57 0.26 0.42 4.83 Tekapo Endura 0.69 0.68 0.42 0.63 0.38 0.53 0.38 0.37 4.08 Tekapo VNS 0.81 0.93 . 0.45 1.01 0.89 0.60 0.38 0.42 5.49 Tekapo Star Fire 0.96 0.62 0.52 0.83 0.53 0.44 0.20 0.42 4.52 Tekapo Kopu II 1.08 0.72 0.55 0.65 0.29 0.43 0.29 0.28 4.29 Tekapo Ladino 0.78 0.62 0.59 0.54 0.46 0.65 0.21 0.22 4.07 Aries Endura 0.65 0.68 0.21 0.00 0.56 0.36 0.25 0.43 3.14 Aries VNS 0.54 0.97 0.97 0.00 0.79 0.48 0.23 0.34 4.32 Aries Star Fire 0.81 0.96 0.48 0.00 0.51 0.40 0.21 0.34 3.71 Aries Kopu II 0.47 0.92 0.49 0.00 0.26 0.33 0.22 0.45 3.14 Aries Ladino 0.63 0.75 0.42 0.00 0.35 0.31 0.19 0.28 2.93 Barfort VNS 0.83 1.14 0.55 0.00 0.42 0.36 0.25 0.32 3.87 Barfort Start 0.75 1.05 0.51 0.00 0.23 0.31 0.35 0.27 3.47 Barfort Alice 0.52 1.02 0.19 0.00 0.23 0.53 0.27 0.25 3.01 Barfort Ladino 0.72 l .06 0.35 0.00 0.42 0.39 0.40 0.42 3.76 Calibra VNS 0.59 1.40 0.68 0.00 1.07 0.92 0.30 0.40 5.36 Calibra Jumbo 0.71 0.97 0.31 0.00 0.18 0.39 0.31 0.26 3.13 Calibra Ladino 0.65 1.05 0.30 0.00 0.25 0.55 0.24 0.41 3.45 Mara VNS 0.65 1.16 0.48 0.00 0.54 0.63 0.53 0.47 4.46 Mara Start 0.54 1.25 0.48 0.00 0.44 0.39 0.49 0.46 4.05 Mara Alice 0.62 1.22 0.42 0.00 0.23 0.40 0.41 0.61 3.91 Mara Ladino 0.56 0.97 0.44 0.00 0.25 0.33 0.25 0.32 3.12 Mav. Gold Endura 0.76 1.01 0.34 0.00 0.58 0.68 0.30 0.21 3.88 Mav. Gold VNS 0.61 0.81 0.77 0.00 0.45 0.40 0.31 0.20 3.55 Mav. Gold Star Fire 0.56 0.86 0.95 0.00 0.34 0.29 0.30 0.27 3.57 Mav. Gold Kopu II 0.79 0.70 0.46 0.00 0.46 0.46 0.18 0.20 3.25 Mav. Gold Ladino 0.45 1.00 0.47 0.00 0.70 0.42 0.14 0.26 3.44 Quartet Endura 0.74 1.03 0.29 0.00 0.41 0.40 0.52 0.37 3.76 Quartet VNS 0.75 0.89 0.79 0.00 0.36 0.37 0.49 0.46 4.11 Quartet Ladino 0.69 1.01 0.55 0.00 0.58 0.35 0.35 0.14 3.67 Quartet Star Fire 0.88 0.85 0.63 0.00 0.45 0.40 0.37 0.42 4.00 7O Table 15 continued 2004 2005 Grass Clover Total Cultivars Cultivars l9-May 21-Jun 5-Atg 7-Sep 23-May 7-Jul 9-Aig 2-Oct 2-yr Quartet Kopu II 0.68 1.11 0.42 0.00 0.51 0.56 0.41 0.35 4.04 Tonga Endura 0.76 0.78 0.33 0.00 0.67 0.40 0.27 0.20 3.41 Tonga VNS 0.83 0.62 0.70 0.00 0.29 0.80 0.37 0.35 3.96 Tonga Star Fire 0.99 0.87 0.45 0.00 0.80 0.42 0.34 0.39 4.26 Tonga Kopu II 0.74 0.67 0.27 0.00 0.78 0.32 0.26 0.29 3.33 Tonga Ladino 0.62 0.79 0.35 0.00 0.78 0.43 0.32 0.66 3.95 Bronson VNS 0.76 1.10 0.51 0.74 0.7 5 0.58 0.30 0.59 5.33 Bronson Endura 0.79 0.72 0.45 0.80 0.39 0.53 0.48 0.46 4.62 Bronson Kopu II 0.88 1.00 0.51 0.60 1.03 0.45 0.37 0.34 5.18 Bronson Ladino 0.87 0.65 0.47 0.67 0.46 0.40 0.39 0.43 4.34 Bronson Star Fire 0.78 0.82 0.55 1.11 0.69 0.32 0.39 0.43 5.09 K5666V VNS 0.78 0.92 0.38 0.66 0.49 0.35 0.32 0.38 4.28 K5666V Endura 0.89 0.86 0.48 0.47 0.55 0.39 0.46 0.50 4.60 K5666V Kopu II 0.74 0.90 0.41 0.57 0.83 0.55 0.24 0.35 4.59 K5666V Ladino 0.78 0.76 0.38 0.68 0.32 0.34 0.31 0.56 4.13 K5666V Star Fire 0.76 0.73 0.55 0.59 0.34 0.29 0.28 0.42 3.96 Barolex Alice 0.75 1.34 0.60 0.65 0.39 0.33 0.37 0.43 4.86 Barolex VNS 0.86 1.16 0.80 0.76 0.74 0.37 0.20 0.39 5.28 Barolex Ladino 0.66 0.97 0.49 0.80 1 .03 0.22 0.40 0.49 5.06 Barolex Start 0.61 0.69 0.54 0.97 0.74 0.37 0.24 0.34 4.50 Mean 0.8 0.9 0.5 0.7 0.5 0.4 0.3 0.4 4.5 CV 30 28 42 33 53 43 52 37 14 LSD (0.05) 0.4 0.4 0.3 0.4 NS NS NS NS NS Data of Perennial ryegrass cultivars in last cutting event of 2004 were not included Grass cultivars: Festulolium (Duo and Hykor) Orchardgrass (Amba, Niva, Sparta and Tekapo) Perennial ryegrass (Aries, Barfort, Calibra, Mara, Maverick Gold, Quartet, and Tonga,) Tall fescue (Bronson, K5666V, and Barolex) Clover cultivars: Red clover (VNS', Star Fire, and Start) White clovers (KopuII, ladino, Alice, and Jumbo) Kura clover (Endura) ' Variety Not Stated 71 Table 16. Dry matter yield (tons acre") of 67 grass- clover binary mixtures treatments established at Upper Peninsula Experiment Station (U PES) over a two-year period (continued on the next page). 2004 2005 Grass Clover 2-yr Cultivars Cultivars 7-Jun 12-Jul 22-Aug l7-Oct l-Jun lO-Jul 23-Aug 29-Sep Total DM tons aere'I Duo Endura 0.37 0.31 0.64 0.23 0.58 0.35 0.34 0.31 3.13 Duo Star Fire 0.79 0.72 0.81 0.40 0.91 0.64 0.83 0.30 5.40 Duo VNS 0.69 0.72 0.37 0.28 0.70 0.50 0.50 0.37 4.13 Duo Ladino 0.95 0.81 0.76 0.32 0.60 0.44 0.18 0.12 4.18 Duo Kopu II 0.87 0.67 0.58 0.31 0.55 0.33 0.24 0.20 3.75 Hykor VNS 0.71 0.47 0.43 0.29 0.74 0.33 0.52 0.38 3.87 Hykor Jumbo 1.11 0.77 0.88 0.28 0.86 0.50 0.44 0.25 5.09 Hykor Ladino 0.75 0.65 0.39 0.30 0.67 0.50 0.42 0.42 4.10 Amba VNS 0.66 0.40 0.43 0.30 0.74 0.27 0.52 0.43 3.75 Amba Jumbo 0.72 0.65 0.66 0.30 0.75 0.34 0.28 0.34 4.04 Amba Ladino 0.77 0.35 0.44 0.31 0.77 0.20 0.28 0.37 3.49 Niva VNS 0.68 0.49 0.63 0.27 0.70 0.37 0.38 0.40 3.92 Niva Jumbo 0.64 0.71 0.57 0.29 0.56 0.40 0.27 0.27 3.71 Niva Ladino 0.63 0.52 0.36 0.30 0.68 0.33 0.24 0.50 3.56 Sparta VNS 0.76 0.48 0.51 0.30 0.57 0.24 0.34 0.35 3.55 Sparta Jumbo 0.78 0.83 0.79 0.29 0.70 0.30 0.35 0.53 4.57 Sparta Ladino 0.83 0.71 0.41 0.24 0.70 0.26 0.30 0.33 3.78 Tekapo Endura 0.36 0.40 0.32 0.23 0.66 0.32 0.26 0.38 2.93 Tekapo VNS 0.62 0.51 0.57 0.34 0.67 0.32 0.33 0.38 3.74 Tekapo Star Fire 0.51 0.65 0.71 0.36 0.83 0.46 0.37 0.48 4.37 Tekapo Kopu II 0.57 0.67 0.63 0.31 0.67 0.38 0.24 0.41 3.88 Tekapo Ladino 0.60 0.73 0.59 0.26 0.66 0.30 0.25 0.41 3.80 Aries Endura 0.31 0.42 0.77 0.00 0.50 0.40 0.24 0.1 l 2.75 Aries VNS 0.51 0.46 0.83 0.00 0.51 0.60 0.60 0.13 3.64 Aries Star Fire 0.35 0.76 0.79 0.00 0.73 0.44 0.40 0.31 3.78 Aries Kopu II 0.55 0.62 0.46 0.00 0.55 0.34 0.30 0.10 2.92 Aries Ladino 0.54 0.73 0.55 0.00 0.51 0.30 0.13 0.15 2.91 Barfort VNS 0.64 0.74 0.51 0.00 0.62 0.70 0.64 0.36 4.21 Barfort Start 1.26 0.74 0.55 0.00 0.62 0.66 0.53 0.28 4.64 Barfort Alice 0.94 1.40 0.67 0.00 0.62 0.42 0.30 0.25 4.60 Barfort Ladino 0.78 1.02 0.47 0.00 0.57 0.35 0.25 0.18 3.62 Calibra VNS 0.58 0.55 0.51 0.00 0.61 0.26 0.44 0.30 3.25 Calibra Jumbo 0.71 1.39 0.68 0.00 0.64 0.20 0.36 0.20 4.18 Calibra Ladino 0.90 0.81 0.62 0.00 0.60 0.30 0.33 0.30 3.86 Mara VNS 0.70 0.60 0.60 0.00 0.62 0.27 0.46 0.53 3.78 Mara Start 0.74 0.86 0.80 0.00 0.70 0.64 0.50 0.52 4.76 Mara Alice 0.72 1.16 0.72 0.00 0.62 0.31 0.21 0.25 3.99 Mara Ladino 0.78 0.79 0.70 0.00 0.55 0.34 0.24 0.36 3.76 Mav. Gld Endura 0.13 0.32 0.25 0.00 0.58 0.38 0.24 0.15 2.05 Mav. Gld VNS 0.32 0.46 0.82 0.00 0.62 0.63 0.65 0.13 3.63 Mav. Gld Star Fire 0.60 0.66 1.02 0.00 0.77 0.90 0.34 0.21 4.50 Mav. Gld Kopu II 0.50 0.69 0.53 0.00 0.54 0.22 0.23 0.17 2.88 Mav. Gld Ladino 0.52 0.86 0.61 0.00 0.55 0.15 0.17 0.12 2.98 Quartet Endura 0.37 0.35 0.34 0.00 0.50 0.50 0.20 0.30 2.56 Quartet VNS 0.58 0.73 0.56 0.00 0.65 0.55 0.38 0.32 3.77 72 Table 16 continued 2004 2005 Grass Clover 2-yr Cultivars Cultivars 7-Jun 12-Jul 22-Aug 17-Oct l-Jun 10-Jul 23-Aig 29-Sep Total Quartet Ladino 0.70 0.83 0.66 0.00 0.65 0.27 0.15 0.20 3.46 Quartet Star Fire 0.65 0.88 1.02 0.00 0.82 0.50 0.52 0.40 4.79 Quartet Kopu 11 0.83 0.88 0.75 0.00 0.58 0.36 0.14 0.18 3.72 Tonga Endura 0.40 0.44 0.37 0.00 0.68 0.46 0.30 0.33 2.98 Tonga VNS 1.07 0.62 0.53 0.00 0.72 0.64 0.41 0.60 4.59 Tonga Star Fire 0.88 0.73 0.84 0.00 0.80 0.54 0.70 0.34 4.83 Tonga Kopu II 0.75 0.70 0.91 0.00 0.50 0.22 0.24 0.25 3.57 Tonga Ladino 1.01 0.66 1.13 0.00 0.58 0.36 0.23 0.20 4.17 Bronson VNS 0.75 0.38 0.52 0.25 0.60 0.47 0.62 0.43 4.02 Bronson Endura 0.55 0.31 0.31 0.22 0.50 0.31 0.36 0.25 2.81 Bronson Kopu II 0.83 0.67 0.55 0.29 0.63 0.42 0.38 0.32 4.09 Bronson Ladino 0.77 0.64 0.57 0.44 0.68 0.22 0.40 0.30 4.02 Bronson Star Fire 0.80 0.54 0.63 0.29 0.71 0.37 0.50 0.37 4.21 K5666V VNS 0.55 0.45 0.54 0.28 0.70 0.41 0.45 0.46 3.84 K5666V Endura 0.39 0.45 0.51 0.29 0.40 0.78 0.27 0.25 3.34 K5666V Kopu II 0.63 0.54 0.70 0.32 0.55 0.33 0.36 0.26 3.69 K5666V Ladino 0.60 0.83 0.80 0.16 0.58 0.40 0.35 0.40 4.12 K5666V Star Fire 0.77 0.58 0.80 0.35 0.65 0.67 0.63 0.34 4.79 Barolex Alice 0.69 0.58 0.58 0.32 0.70 0.58 0.47 0.50 4.42 Barolex VNS 0.68 0.43 0.56 0.28 0.58 0.46 0.28 0.48 3.75 Barolex Ladino 0.59 0.64 0.60 0.38 0.50 0.34 0.33 0.42 3.80 Barolex Start 0.79 0.73 1.04 0.36 0.80 0.43 0.40 0.35 4.90 Mean 0.7 0.6 0.6 0.3 0.6 0.4 0.4 0.3 3.8 CV 26 27 34 25 18 46 48 36 15 LSD(0.05) 0.3 0.3 0.3 0.1 0.2 0.3 0.3 0.2 0.9 Data of Perennial ryegrass cultivars in last cutting event of 2004 were not included Grass cultivars: Festulolium (Duo and Hykor) Orchardgrass (Amba, Niva, Sparta and Tekapo) Perennial ryegrass (Aries, Barfort, Calibra, Mara, Maverick Gold, Quartet, and Tonga,) Tall fescue (Bronson, K5666V, and Barolex) Clover cultivars: Red clover (VNS', Star Fire, and Start) White clovers (KopuII, ladino, Alice, and Jumbo) Kura clover (Endura) ‘ Variety Not Stated 73 Table 17. Dry matter yield (tons acre!) of eight clover cultivars established in monoculture at Kello Biological Research Station (KBS) over a two-year period. Clovers 2004 2005 Total Species / Cultivars 24-May I 24-Jun I 26-Jul I 9-Sep 4-May I 14-Jun I 2-Au 2-yr DM tons acre'l Kura Endura 1.53 0.64 0.68 0.60 0.57 0.63 0.50 5.15 Clover Red Star Fire 094 0.52 0.51 0.69 0.53 0.43 0.27 3.89 Clover Start 0.64 0.57 0.64 0.61 0.53 0.48 0.08 3.55 VNS 0.65 0.50 0.70 0.70 0.56 0.42 0.16 3.69 White Kopu II 0.74 0.38 0.40 0.51 0.36 0.32 0.38 3.09 Clove, Alice 0.56 0.60 0.63 0.45 0.42 0.37 0.36 339 Jumbo 0.88 0.91 0.69 0.69 0.41 0.43 0.08 4.09 Ladino 0.79 0.67 0.43 0.44 0.40 0.36 0.15 3.24 Mean 0.8 0.6 0.6 0.6 0.5 0.4 0.3 3.8 CV 51.8 43.6 44.9 38.5 66.1 45.4 78.4 20.8 LSD L005) 0.8 0.5 0.5 0.4 0.5 0.3 0.3 1.4 Table 18. Dry matter yield production (tons acre'l) of eight clover cultivars established in monoculture at Lake City (LC) over a two-year period. Clovers 2004 2005 T088] Species/Cultivar l9-May I 21-Jun I 5-Aug 23-May I 7-Jul I 9-Aug I 2-Oct 2-yr DM tons acre'l ’Kura Endura 0.57 0.90 0.25 0.38 0.82 0.21 0.11 3.24 Clover Red Star Fire 0.80 0.58 0.70 0.00 0.00 0.00 0.00 2.08 Clover Start 0.71 0.68 0.80 0-00 0.00 0.00 0.00 2.19 VNS 0.64 0.72 1.20 0-00 0.00 0.00 0.00 2.56 White Kopu II 0.59 0.88 0.59 0.00 0.00 0.00 0.00 2.06 Clove, Alice 0.73 0.78 0.44 0.00 0.00 0.00 0.00 1.95 Jumbo 0.73 0.79 0.55 0-00 0-00 0-00 0-00 2.07 Ladino 0.63 0.84 0.49 0.00 0.00 0.00 0.00 1.96 Mean 0.7 0.8 0.6 0.0 0.0 0.0 0.0 0.0 CV 22.2 29.6 27.4 0.0 0.0 0.0 0.0 0.0 LSD ( 0.05) 0.3 0.4 0.3 0.0 0.0 0.0 0.0 0.0 LSD is not available due to missing data * Kura clover (Endura) is the only cultivar reported in 2005. 74 Table 19. Dry matter yield (tons acre") of eight clover cultivars established in monoculture at Upper Peninsula Experiment Station (U PES) over a two-year eriod. Clover, 2004 2005 Total Species/Cultivar 7-Jun I 12-Jul I 22-Aug r-JuriI 10-Ju1 I 23-Aug 2-yr DM tons acre‘l Kura Endura 0.52 0.23 0.28 0.69 0.40 0.02 2.14 clover Star Fire 0.44 0.77 0.75 0.70 0.04 0.04 2.74 Red Start 0.70 0.71 0.46 0.58 0.00 0.00 2.45 Clover VNS 0.29 0.50 0.68 0.38 0.05 0.00 1.90 White Kopu 11 0.39 0.32 0.45 0.61 0.24 0.03 2.04 Clove, Alice 0.40 0.32 0.55 0.53 0.25 0.08 2.13 Jumbo 0.46 0.32 0.52 0.69 0.21 0.02 2.22 Ladino 0.41 0.46 0.45 0.59 0.20 0.16 2.27 Mean 0.5 0.5 0.5 0.6 0.2 0.1 2.3 cv 36.7 32.4 44.3 28.9 99.4 163.9 23.6 LSD (0.05) 0.3 03 0.4 0.3 0.3 0.1 0.9 75 Chapter 2 ANIMAL GRAZING PREFERENCE AND FORAGE QUALITY OF PERENNIAL COOL SEASON GRASSES AND CLOVERS GROWN IN MONOCULTURE AND BINARY MIXTURES UNDER ROTATIONAL GRAZING ABSTRACT Grass-legume forage pasture mixtures are important to animal production in the temperate United States. The objective of this study, which was conducted from 2004-06 at Hickory Comers, MI, was to assess animal grazing preferences and forage quality of introduced grass and clover cultivars grown in monoculture and binary mixtures. Results indicated that grazing preference depends on the type of pasture species and the species within the mixtures; binary mixtures were preferred over the monocultures. Higher crude protein (CP), lower acid detergent fiber (ADF), and neutral detergent fiber (NDF) were found in binary mixture treatments compared to grass and clover monoculture treatments. Perennial rye grass cultivars demonstrated higher forage quality and animal preferences when associated with clover cultivars. Tall fescue was less preferred by animals compared to perennial rye grass, particularly when grown in a monoculture. The results showed that animal preference of festulolium (Duo) monoculture was similar to that of perennial ryegrass cultivars. The binary mixtures of festulolium (Duo)-clover and perennial ryegrass-clover enhanced preferences and forage quality compared to monoculture festulolium and perennial ryegrass, which indicate these mixtures are a good choice for livestock producers to use for grazing. Total dry matter yield and animal preferences were not always positively correlated. 76 INTRODUCTION AND BACKGROUND The most important forage legumes in the North-Central US are alfalfa (Medicago sativa L.), red clover (T rifolium pratense L.), birdsfoot trefoil (Lotus corniculatus L.), and white clover (T rifolium repens L.) (Knight, 1985). However, their ability to remain in the pasture under grazing is often limited (F orde et al., 1989; Van Keuren and Matches, 1988). Kura clover (T rifolium ambiguim Bieb.) is a perennial legume that has extensive rhizomes with a wide range of adaptation, which makes it potentially more suitable as a pasture crop and for soil conservation purposes (Bryant, 1974; Speer and Allison, 1985). White clover (common and ladino types) is one of the most important legumes, which can be used for grazing. Beside its palatability and high forage quality, white clover also has the ability to tolerate continuous, heavy grazing (Spitaleri et al., 2003). This characteristic makes it successfully adapted for rotational grazing. White clover may be grazed continuously or rotationally and may be grazed closely (2.54 to 5.08 cm) (Penn State University Agronomy guide 2005-2006). Plant performance in pastures cannot be fully understood without reference to animals. Animals tend to prefer and consume the most palatable plants first if given a choice from various forage species. Hence, animals are always selective in what they eat. The word “select” is defined as the action of choosing in preference to others (Cruz and Ganskopp, 1998). 77 Animal preferences refer to the selective response made by animals, which is mostly behavioral (Vallentine, 2001). Relative preference indicates a proportional choice among two or more feeds (Heady, 1964). Preference is important because it afi‘ects animal intake and any factor limiting intake can impact animal performance (McCaughey, 1998). On the other hand, consumption of the more palatable species can have a great impact on grass-legume binary mixture composition. Hence, animal preference is a factor that influences the pasture community as a result of overgrazing of the most preferred species in the pasture. Animal grazing preference has been researched for many years. Several studies have investigated the factors that make animals prefer certain plant species over others. Some of these factors are plant-related while others are animal-related. Plant growth stage is a major factor that influences animal preference. Advanced grth stage has been indicated as a factor, which is correlated with decreasing preferences (Heady, 1964) Fresh immature forages is highly palatable and livestock will selectively graze those forages (Rohweder and Albrecht, 1995). The high preferences for rough fescue appeared to be determined by the accessibility of the large tufted plants to cattle (Willma and Rode, 1998). Animals graze the most palatable species when multiple species are offered. If no alternative is available, they will consume the specific feed even if it is less palatable. Preference can be associated with plant physical characteristics. Within plant parts, young leaves and stems are higher in crude protein and lower in lignin than older stems and leaves (Heady, 1964). Thus, the younger leaves and stems are more likely to be preferred by animals. Animals avoid consuming plants with spines, pubescence or 78 poisonous leaves. MacAdam and Mayland (2003) found that there was a negative correlation between tall fescue leaf strength and preference. They concluded that the cultivars that have the highest tensile strength would have the most fiber making it difficult to break down by grazing. Plant chemical composition also influences animal preference. Forage species high in sugar content tend to be preferred by cattle (Plice, 1952), calves (Kare and Halpem, 1961), and deer (Mitchell and Hosley, 1936). Additionally, animals are able to preferentially select aftemoon cut alfalfa hay over morning cut hay due to higher sugar content. Three ruminant species, sheep (Ovis aries), goats (Capra hircus), and cattle (Bos taurus) preferred alfalfa hay cut in the afiemoon over hay cut in the morning (Fisher et al., 2002). High positive correlation between protein content and preference by cattle and sheep has been reported (Saltonstall, 1948; Cook, 1959; Blaser et al., 1960). In addition, lignin and crude fiber were observed to be negatively correlated with animal preference (Collins and Fritz, 2003). In most recent study, Smit et al., (2006) concluded that dairy cows selection among six perennial ryegrass cultivars was positively related to high water soluble carbohydrates (WSC) concentration and negatively to ash and fiber. Past experience of animal diet selection influences animal preference. Vallentine (2001) stated in his book (Grazing Management) “Animals can acquire preferences for familiar food, first from their dams and second from their peers, but also by trial and ’9 error . Several methods have been reported to measure animal preferences. In general, the food that is eaten has been defined as the most preferable (Smit et al., 2006). 79 Preferences can be measured indoor by weighing the offered herbage and the residual then preferences is expressed as the food that has been consumed (offered- residual) (Aderibigbe et al., 1982; Provenza et al., 1996; Tolkamp et al., 1998). However, in a grazing system, preferences can be measured using the sward-cutting method (Meijs, 1981; Macoon., 2003). Animal preference can also be determined visually by estimating the herbage yield before and after grazing using preference scoring of 0 to 10 (O to 100% of forage eaten) (Shewmaker et al., 1997) or a scale of l to 5 (1=least preferred ; 5 = most preferred ) described by McCaughey (1998). Forage quality is extremely important for livestock producers. The term forage quality is defined as the capacity of forage to supply animal nutrient requirements. Crude protein (CP), acid detergent fiber (ADF) and neutral detergent fiber (N DF) are the most common criteria that can be used to evaluate forage quality. Forage species with low NDF or ADF content are considered higher in quality than one with a high NDF or ADF content. In addition, as CP increases in forage, livestock perform greater (i.e., gain more weight, produce more milk, etc.) (Clemson, University Cooperative Extension Service). Buxton and Mertens (1995) defined forage quality in terms of performance of animals when fed herbage. It also refers to the physical and chemical characteristics of forage that make it valuable to animals as a source of nutrients (Balasko and Nelson, 2003). Collins and Fritz (2003) found that forage species vary in their quality components. They stated that “Legumes usually have 15% to 20% crude protein, while tropical forage grasses have about half as much and cool season grass had intermediate concentration “. Differences in forage quality within grass and legume species may exist. Collins and Fritz (2003) reported that cool season grasses averaged about 13% higher in 80 digestibility than warm season gasses. Leaf anatomy contributes to differences in forage quality. It has been found from leaf cross sections that bermudagass (a C4 plant) is generally higher in the low digestible vascular bundle, epidermis and sclerechyma tissues than tall fescue (a C3 plant) (Akin and Burdick, 1975). Forage species can also differ in forage quality based on weather conditions. For instance, high temperatures decrease forage quality due to increased plant ligrin content (Castle and Halley, 1953; Corbett, 1953). Anti-quality components are considered a major factor that decreases forage quality and animal preferences (Collins, and Hannaway, 2003). Grass-legume mixtures vary in fiber depending on the Species. Pastures consisting of kura clover with gasses had lower levels of fiber, greater protein concentration, and higher digestibility than the pasture consisting of red clover with gasses (Mourifio et al., 2003). It has been concluded that in a temperate pasture, white clover is selectively gazed in preference to perennial ryegass (Curll and Wilkins, 1982). It was also observed that plant species selection was influenced by the relative maturities of the gass and legume (Grant.et al., 1985). Animals are able to select the legume from the lower quality gasses in a mixed stand of legume and gasses (Laidlaw, 1983). Forage quality of the gass-legume binary mixtures appears to be higher than gass monocultures. Binary mixtures tend to have geater CP and lower NDF than pure stands of gass (Collins and Hannaway, 2003). In contrast, few studies reported that forage quality of gass-legume mixture is more likely to be lower in quality than the pure legume due to the addition of the gass component (Van Soest, 1982). 81 In recent years, both the gass and legume seed industry has began marketing new perennial gass and clover species and cultivars to Michigan gowers. For example, orchardgass has been introduced with value-added traits such as increased tillering, later maturity, and better winter hardness. Tall fescue has been recently offered with smoother leaf blades, endophyte free, and geater palatability. Because of the potential high forage dry matter yield of these species and cultivars, dairy and livestock producers may benefit by adapting these species and cultivars in their gazing systems. Currently, there has been no research done to evaluate animal preferences and forage quality for introduced gass cultivars of festuloliums, orchardgass, tall fescue and perennial ryegass cultivars and clover cultivars of red clover, white clover and kura clover gown in a binary mixture. Therefore, more research is needed to determine animal preference and forage quality when gown in a mixture. Thus in this research, different gass and clover cultivars combinations were tested for their animal preference and forage quality under rotational gazing. The objectives of this study were to determine animal preference of introduced gass and clover Species and cultivars under rotational gazing, and determine forage quality based 0 NDF, ADF and CP, of the same gass and legume gowing in monoculture and binary mixture under rotational gazing. 82 MATERIALS AND METHODS Experiment Establishment and Maintenance: The gazing trial was conducted in the Kellogg Biological Research Station at Hickory Corners, M1 at the same experimental area established for evaluating persistence and productivity trial mentioned in Chapter 1. The study area was separated into three portions: gass only, legume only (clover), and gass- clover binary mixtures (Appendix Fig. 2A). Each portion was arranged in a randomized complete block desigi (RCBD) with three replications. Each replication of the binary mixture portion consisted of 67 entries of different combinations of gass and clover mixtures. Each replication of clover and gass portion consisted of 8 and 16 monocultures of clover or gasses entries respectively (Chapter 1). Soil was analyzed at Michigan State University (MSU) soil laboratory for fertilizer recommendation as indicated in the first chapter. Appendix Table 1A presents soil information and the gass and clover cultivars used in this study. Grazing procedure and data collection: All treatments were rotationally gazed during the 2004-2006 seasons. The gazing season began in late April and continued until early to late September, depending on the weather conditions. Grazing was started when the average gass height ranged from 20 to 30 cm. Four gazing events were typically obtained at the site of the study (Hickory Comers, MI). A total of eight gazing events were taken over the three years of the study. Four gazing events in 2004, three gazing events in 2005 and a single gazing event in 2006 were conducted. For animal gazing, the whole area (binary mixture portion, gass and clover monoculture portions) was divided into two sections using electric fencing. One section 83 consisted of replications 1 and 2 of the binary mixtures portion. The second section consisted of the replication 3 of the binary mixtures and all three replications of the monoculture portions (gasses and clovers). For all gazing events, animals began gazing in section 1 for 48 hr then they were moved to section 2 for another 48 hr. The gazing map of the arrangement used in this trial is illustrated in Appendix Fig 3A. The number of cattle released to gaze depended upon their body weight. In each year, approximately 10 Holstein steers, each weighting 226 kg was used for the first gazing event (Holstein heifers were used for 2006 gazing). However, for the subsequent gazing events, the number of animals was reduced to maintain the same stocking density (Appendix Table 5A). After each gazing event, plots were mechanically mowed to a uniform height (8 cm) and cattle were kept in different paddocks until the next gazing event. Adequate water and minerals were available during the gazing time in the gazing area. Preference scores were visually assigred to assess the degee to which each of the plots had been gazed off after allowing the animals to gaze each section for 48 hr. The preference rating was conducted by assessing the amount of remaining vegetation on a scale of (1-5) (McCaughey, 1998) where: 1 = less than 20% of the plot gazed; 2 = 20- 40%; 3 = 40 - 60 %; 4 = 60 - 80 %; and 5 = 80% or geater of the plot was gazed. The cultivars that have high preference score over the course of the study are potentially more palatable. 84 Forage quality analyses: Prior to each gazing event, forage samples were hand clipped within 0.25 m2 quadrate in each plot of the gass, clover and binary mixtures portions. Additional samples were also collected from Lake City Experiment Station (LC) and the Upper Peninsula Experiment Station at Chatham (UPES), MI. Samples were dried at 60 °C for 48 hr for dry matter determination (Data on dry matter yield presented in Chapter 1). For forage quality analyses, dried samples were gound to pass through a 2 mm screen using a Wiley Grinding Mill (Authur H. Thomas Co., Philadelphia, PA) and then passed through a 1mm screen using a UDY Cyclone Mill, (Udy Mill Corp., Fort Collins, CO.). 1n the crude protein analysis, total N was determined for the subset by the Hach modified Kjeldahl procedure (Watkins et al., 1987), and CP was estimated by multiplying total N by 6.25 because N makes up about 16% of the protein in the plant (Collins and Fritz, 2003). The Goering and Van Soest (1970) method was used for NDF and ADF determination with the addition of one ml of alpha-amylase to the neutral detergent solution for the breakdown of starch. A sub-sample of ~20 gams of each sample was retained for forage quality analysis using Near-Infi'ared Reflectance Spectroscopy (N IRS). Each sample was scanned with a 6500 near-infrared spectrophotometer (FOSS NIRSystems, Inc., Eden Prairie, MN) with wavelengths between 400 and 2500 nm. Reflected wavelengths were recorded. CP, ADF and NDF were determined fi'om equations developed by the NIRS consortium (Madison, WI). All the chemical analyses and NIRS procedures were performed at the MSU Forage and Physiology Lab. 85 Statistical analyses: All the statistical computations were performed using SAS (SAS Institute, 2000). Analysis of variance was conducted using PROC GLM procedure. Experimental units were the individual plots. The data for 2004 and 2005 were analyzed separately. Experiment type and gazing event were the fixed factors and blocks (replication) nested within type was a random factor used as an error term to test the effect of type. Grazing by blocks by type interaction term was used as an error term to test the effect of gazing and the effect of gazing by type interaction. When the interaction between gazing and type was found to be significant (p<0.05), mean separations between the types were conducted separately within each gazing. Mean separation of animal preference scores and CP, ADF and NDF was achieved using Fischer’s LSD at p<0.05. Normality assumption was checked using stem and leaf and normal probability plots in PROC UNIVARIATE. Coefficient of variation (CV) was listed to measure the precision of the experiment. 86 RESULTS AND DISCUSSION Animal preferences Sigiificant years X gazing events X treatment (binary mixtures) interactions were found in animal preferences for gass-clover binary mixtures (Appendix Table 9A). Similar interactions were observed for gass monoculture (Appendix Table 10A). These interactions were primarily due to changes in plant maturity from one gazing event to the other and also from year to year. However, these interactions were not sigiificant for clover monoculture (Appendix Table 11A). In general, there was a trend toward higher preference scores of early gazing events compared to later gazing events in 2004 (Figl) and 2005 (Fig2). During the early season, animals had less experience selecting among the forage species and as the season progessed, they started to acquire preferences for their diet selection (Vallentine, 2001). This may also be a result of lower plant ligrin and/or higher sugar levels in the early spring. Animals in this study showed varying degees of preference between monocultures and binary mixtures. Results showed binary mixtures were preferred by the animals over monoculture treatments (Figl and 2). Binary mixtures were sigiificantly higher in animal preference compared to gass monoculture (p<0.01) in three of four gazing events in 2004 and significantly (p<0.05) higher than clover monoculture in two gazing events in the same year (Fig 1). However, in 2005, gass- clover binary mixtures were significantly (p<0.05) higher than gass monoculture in one of three gazing events and higher than clover monoculture in two gazing events (Fig 2). 87 No sigrificant differences were found between monoculture and binary mixtures in the single gazing event of 2006 (data not shown). Animals showed a preference between gasses and clovers gown separately as monocultures. Clovers were significantly (p<0.05) geater in animal preference than the gasses in two gazing events in 2004 (Figl). The gass monoculture was significantly preferred over the clover monoculture (p<0.05) in only the first gazing event in 2005 (Fig. 2). These data provide evidence of the importance of the binary mixtures as well as clovers for increased animal preference. Grass monoculture data presented in Table 1 shows a sigiificant difference in animal preference (p<0.05) between gass species and cultivars, while the preferences among clover species (Table 2) were less distinguishable than for gass species. Only one gazing event was Si grificantly different in preferences rating among eight clover cultivars in 2004 (Table 2). In 2005, even though there were sigtificant differences among the clovers cultivars across all the gazing events, the scores were lower for all gazing events compared to 2004 (Table 2), which is likely due to the higher maximum temperature causing increased lignification in gass and clover species. In addition, animal dry matter intake decreases with heat stress. In 2006, there was no data recorded on clovers due to the insufficient gowth of the clover portion at the gazing event. There was a Sigiificant difference in animal preference for the binary mixture treatments. The preference was more dependent upon the gass species than the associated clovers (Table 3). The animal preferences results of each gass species gown in monocultures or in binary mixtures are described as follows: 88 Festulolium: Duo gown in m0noculture was sigiificantly (p<0.05) higher in animal preference than Hykor in five of eight gazing events during the three year period (Table 1). When gown with clover in a binary mixture, Duo was sigiificantly higher in animal preference (p<0.05) in six gazing events especially when associated with white clover (Kopu II) and kura clover (Endura) (Table 3). Duo was most likely preferred over Hykor because it has finer leaf blades, thus making it more desirable for animals (MacAdam and Mayland, 2003). In addition, since festuloliums are derived from a cross between Italian or perennial ryegass and either meadow or tall fescue, it is likely that the genetic make up was a factor that influenced the difference in preference. Tall fescue has thicker and more course leaf blades than that of meadow fescue. Duo is the result of a cross of Meadow fescue and a tetraploid perennial ryegass, with leaf blades and sugar content more like a ryegass (AMPAC seed company web site). Thus, with the average of three gazing years, animal preference of Duo was similar to perennial ryegass cultivars (Tablel ). These data confirm that Duo and Hykor festulolium cultivars differed in their animal preference and animals distinguish between them either when gown in monoculture or a binary mixture with a clover. However, even though Hykor appeared to be less palatable and had not been selected over Duo when they were gown in monocultures, it was gazed relatively well when gown in binary mixtures with clovers (Table 3). This would indicate that clovers in a binary mixture of somewhat unpalatable gasses can increase the consumption of the gasses which may not be normally preferred by animals due to the reduction of NDF in the binary as it associated with animal intake. There was no sigrificant difference in animal preference between the three Hykor-clover binary mixtures (Table 3). 89 Orchardgrass: Hoveland, (1992) found that orchardgass is a well suited perennial cool season gass for using in binary mixtures. Orchardgass cultivars were less preferred by animals when gazed as a monoculture compared to binary mixtures of clover. Preference scores of four orchardgass cultivars (Tekapo, Amba, Niva, and Sparta) were sigrificantly (p<0.05) different in one of eight gazing events (Table 1). However, the binary mixture analysis presented in Table 3 showed geater preference for some cultivars in 2004 versus 2005 and 2006. For example, Tekapo had a very high preference score when gown with kura clover during the 2004 gowing season and a low preference score for all the gazing events of 2005 and the single gazing event of 2006. As indicated earlier, the reduction of 2005 preference ratings may be due to weather related stress causing higher ligiification and heat stress in animals. Orchardgass cultivars Tekapo, Sparta, and Niva had lower preference scores when gown with certain white and red clover cultivars (Table 3). Over the three year gazing period, the best orchardgass-clover combination was Tekapo with kura clover and with the white clover cultivar, Kopu II. Based on these data, Tekapo orchardgass would be best suited as a binary mixture with clovers for Michigan producers under rotational gazing although Tekapo had lower persistence at the northern latitude whether gown in monoculture or binary mixtures (Chapter 1), which indicated that cultivar selection Should be based on both the persistence and animal preference. Perennial ryegrass: Perennial ryegass is considered one of the most desirable species for gazing livestock because of its high palatability and forage quality (Balasko et al., 1995). Results showed that perennial ryegass cultivars in the monoculture trial were high in animal preference in the first gazing event of 2004 and 2005 gazing seasons 90 (Tablel). There was a sigrificant difference in animal preference (p<0.05) among the seven perennial ryegass cultivars when gown in monoculture (Aries, Maverick Gold, Quartet, Tonga, Barfort, Mara, and Calibra) at only two of eight gazing events (Table 1). Animals showed higher (p<0.05) selectivity for perennial rye gass cultivars in all gazing events over the three years period when gown in binary mixtures with clovers. For example, Aries-kura (Endura), Quartet-white clover (Kopu II)‘, Quartet-kura (Endura) and Tonga -white clover (Ladino) binary mixtures resulted in the highest preference among perennial ryegass-clover mixtures (Table 3) Perennial ryegass does not tolerate heat stress or drought and its production during hotter and drier summer months will be lower (Balasko and Nelson, 2003). This explains the decline in average preference during the second, third, and fourth gazing events of 2004 (Table 1). The preference of forages varies with seasonal conditions and stage of gowth (Am.Soc.Range Mgnt, 1962). Tall fescue: Tall fescue is considered less preferred by animals compared to perennial rye gass particularly when gown in monoculture. There was one gazing event which resulted in a sigrificant difference (p<0.05) among the three monoculture tall fescue cultivars in this study (Bronson, K5666V, and Barolex) (Table 1). Tall fescue cultivars resulted in higher preference scores when gown in binary mixtures. There were sigiificant differences between the tall-fescue binary mixtures (Table 3). Bronson and Barolex had Sigiificantly lower animal preferences when gown with red clover. Kura clover gown with K5666V resulted in the highest preference among the tall fescue mixtures. 91 Tall fescue cultivars demonstrated geater yield production, better compatibility with clovers, better winter hardness and good gound cover compared to other gass species in this study (Chapter 1), yet they were less preferred by animals compared to the other gass species even when gown in binary mixtures. The reason for the decreased preference for tall fescue cultivars was likely due to increased leaf width and thickness as explained by MacAdam and Mayland (2003). However, if animals are only offered tall fescue cultivars in pastures, they will likely consume it. Some of the cultivars in this experiment displayed leaf blades, which were narrower and less thick than others. However, it would be still more useful for Michigan gowers to use tall fescue cultivars with clovers to enhance preference. Forage Quality Significant years X location X cutting (gazing) X treatment (binary mixtures) interactions were present for CP, ADF and NDF (Appendix Table 9A). These interactions were due primarily to change in sward composition of the mixtures, which occurred from one gazing event to another and from year to year, which was similar to results found by Zemenchik et al. (2001). Significant years X location X cutting (gazing) X treatment interactions were found for CP, ADF and NDF for gass and clover monoculture treatments (Appendix Tables 10A and 11A, respectively), which was due to the change in plant forage quality that occurred between gazing events and year to year. However, there was no interaction for (N DF) in gass treatments (Appendix Table 10A) and in (CP) clover (Appendix Table 11A). Results from forage quality analysis have proven the hypothesis, which states that binary mixtures have higher forage quality than monocultures (gass or clover). Results of forage quality Show that clovers had highest 92 CP, lowest NDF and ADF compared to gass monocultures and binary mixtures (Table 4). Grass monoculture had lower forage quality (Greater ADF and NDF and lower CP) than binary mixtures. Combining clover with any of the cool-season gasses sigrificantly reduced concentration of NDF and ADF and increased CP compared to gass monocultures (Table 5). These results concur with Zemenchick et al., (2002) in which they found that legume proportions in binary mixtures were positively correlated to CF concentrations and negatively correlated to NDF concentrations. There was a Sigiificant difference in forage quality among species as well as between cultivars of each gass. In 2003, the first gazing event resulted in low ADF and NDF content in perennial ryegass (Barfort) and orchardgass (Tekapo) and higher CP than other gass cultivars when gown in binary mixtures. Wamock (2004) concluded that Barfort perennial ryegass and Tekapo orchardgass had lower NDF and ADF values than other cultivars such as perennial ryegass (Aries). The 2004-2005 analysis of data revealed higher forage quality in all perennial ryegass cultivars especially Maverick Gold, Quartet and Tonga. The forage quality of festulolium (Duo) was higher in CP and lower in ADF and NDF than that of Hykor festulolium. In addition, tall fescue (Bronson) and festulolium (Hykor) cultivars were lower in forge quality compared to the other cultivars within their species (Table 5). In the orchard gass monocultures, Sparta had the highest CP compared to Amba, Niva and Tekapo. Clover species also were significantly different in forage quality. Kura clover (Endura) and white clover (Kopu 11, Alice, Jumbo and Ladino) were higher in CP and lower in ADF and NDF compared to all red clover cultivars (Table 6). However, all red 93 clover cultivars were much higher in CF and lower in ADF and NDF compared to perennial gass species. Total yield and animal preferences were not positively correlated. For example, white clover (J umbo)- festulolium (Hykor) mixtures that produced the highest total dry matter yield were less preferred by animals than perennial ryegass-clover mixtures, which had lowest yield and a higher animal preferences rating (Data not shown). These results concur with a study conducted by Shewmaker et al. (1997). CONCLUSIONS Livestock producers should consider adapting forage species and cultivars, which show higher animal preferences and have higher forage quality for profitable systems. Thus, cultivar selection should be based upon animal preference, persistence and yield. The binary mixtures of festulolium (Duo)-clover increased preferences and forage quality compared to monoculture festulolium. In addition, perennial ryegass cultivars demonstrated good forage quality and animal preferences when associated with clover cultivars, which indicate these mixtures are a good choice for livestock producers to use for gazing. However, their ability to survive the harsh winter could be an issue especially, when gow in northern latitudes (44°-46° N). Cultivars that have shown a higher preference to animals with higher forage quality (Aries, Maverick Gold) were more vulnerable to the winter injury. 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Hanson et al. (ed.) Alfalfa and alfalfa improvement. Agon. Monog. 29. ASA, CSSA, and SSSA, Madison, WI. Van Soest, P.J. 1982. Nutritional ecology of the ruminant. O & B Book, Corvallis, OR. Wamock, D.L. 2004. Adaptation of diploid and tetraploid cultivars of perennial ryegass throughout Michigan as gowing in association with or without ladino white clover. Master Thesis, Michigan State University. East Lansing, MI. Watkins, KL. 1987. Total nitrogen determination of various sample types: A comparison of the Hach, Kjeltec and Kjeldahl methods. J. Assoc. of Anal. Chem 70:3. Willms, W.D., and L.M. Rode. 1998. Forage selection by cattle on fescue prairie in summer or winter. J. Range Manage. 51 :496-500. 98 Zemenchik, R.A., K.A. Albrecht, and MK. Schultz. 2001. Nitrogen replacement value of kura clover and birdfoot trefoil in binary mixtures with cool-season gass. Agon.J.93:451-458. Zemenchik, R.A., K.A. Albrecht, and RD. Shaver.2002. Improved nutritive value of Kura clover —and birdsfoot trefoil-gass mixtures compared with gass monoculture. Agon.J. 94: 1131-1138. 99 Fig.1. The differences in animal grazing preference for the binary mixture (BM), clover, and grass treatments during 2004 grazing season (Bars with different letters within grazing event are significantly different at p<0.05). lGrassuOou—rrlBM Grazirg evert Fig 2. The differences in animal gazing preference for the binary mixture (BM), clover, and grass treatments during 2005 grazing season (Bars with different letters within grazing event are significantly different at p<0.05). 100 Table 1. Animal preference score of 16 gass cultivars established in monoculture treatments over eigrt gazing events. Grass 2004 2005 2006 Species Cultivars 28-May 26-Jun 28-Ju1 9-Sep 6-May l6-Jun 4-Aug lZ-May Duo 4.8 3.3 1.2 1.1 4.7 1.0 2.7 3.0 Fest Hykor 1.5 2.1 1.7 1.1 1.7 1.7 1.0 1.2 Tekapo 2.0 1.5 1.3 1.0 1.5 1.0 1.2 2.3 Amba 2.3 3.5 2.6 1.0 2.7 1.0 1.0 1.7 0R Niva 1.5 3.5 3.3 1.8 2.0 1.0 1.0 3.2 Sparta 3.0 3.0 3.3 1.8 1.9 1.3 1.0 3.2 Aries 3.3 3.6 1.5 1.0 4.5 1.5 1.7 1.8 Maverick Gold 4.8 3.5 2.0 1.5 4.2 1.0 2.2 1.2 Quartet 4.0 3.0 1.8 1.0 3.5 1.0 2.0 1.5 PR Tonga 4.0 3.5 1.5 1.0 4.8 2.0 2.4 3.3 Barfort 4.8 3.6 1.5 1.3 4.7 1.3 1.7 3.3 Mara 5.0 3.5 1.6 1.1 4.4 1.0 1.0 3.0 Calibra 4.1 3.1 1.6 1.0 4.7 1.0 2.4 3.3 Bronson 1.3 2.6 3.0 1.0 1.2 1.3 1.0 1.0 TF K5666V 1.3 2.6 3.3 1.0 2.4 1.5 1.0 1.2 Barolex 1.0 2.8 2.0 1.0 2.4 1.0 1.0 1.3 Mean 3.1 3.1 2.1 1.2 3.2 13 1.5 2.2 cv 21 30 38 34 20 54 42 47 LSD(0.05) 1.1 1.6 13 . 0.7 1.0 NS 1.0 1.7 1 = less than 20% of the plot grazed 5 = 80% or geater of the plot was grazed. Grass cultivars: Fest=Festulolium ; OR=Orchardgass, PR=Perennial ryegrass and TF= Tall fescue 101 Table 2. Animal preference score of eight clover cultivars established in monoculture over seven gazing events. Clover 2004 2005 Species Cultivars 28-May 26-Jun 28-Jul 9- Sep 6-May l6-Jun 4-Aug Kura Endura 3.8 3.0 3.3 1.3 1.0 3.7 2.5 Red Star Fire 3.6 4.1 4.1 1.8 1.0 1.4 1.0 Clover Start 2.8 3.0 3.6 1.6 1.2 1.5 1.0 VNS 2.6 2.8 2.5 2.5 1.0 1.7 1.0 Kopu II 3.8 3.6 3.8 3.3 1.7 1.9 1.2 White Alice 3.8 3.0 3.5 2.5 1.0 1.0 1.0 Clover Jumbo 3.0 2.3 3.6 2.1 1.7 3.2 1.0 Ladino 3.3 4.3 3.8 2.8 1.2 1.0 1.0 Mean 3.3 3.2 3.5 2.2 1.2 1.9 1.2 CV 37 48 37 41 32 57 18 LSD (0.05) NS NS NS 1.6 0.7 1.9 0.4 l = less than 20% of the plot grazed 5 = 80% or greater of the plot was gazed. 102 Table 3.Animal preference score of 67 gass-clover binary mixtures over eight gazing events (continue next page). Grass Clover 2004 2005 2006 Cultivars Cultivars 28-May 26-Jun 28-Jul 9-Sep 6-May 16-Jun 4-Aug l2-May Duo Endura 4.8 3.3 3.0 2.8 3.2 2.5 4.8 5.0 Duo Star Fire 4.5 3.3 2.5 2.8 4.4 1.0 2.5 1.3 Duo VNS 4.8 3.1 2.3 2.1 3.0 1.2 1.9 2.7 Duo Ladino 4.6 2.8 2.8 3.1 4.5 1.0 3.7 2.7 Duo Kopu 11 4.8 4.6 3.1 4.0 4.7 1.0 2.0 3.0 Hykor VNS 2.3 2.3 2.3 1.6 3.6 1.5 1.0 1.0 Hykor Jumbo 2.3 2.3 3.5 2.0 3.3 1.0 1.0 1.3 Hykor Ladino 2.6 2.3 3.3 1.8 3.5 1.3 1.5 1.3 Amba VNS 3.8 3.8 3.8 3.0 3.3 3.0 1.3 1.0 Amba Jumbo 3.8 4.5 4.1 4.1 3.8 1.8 2.2 1.0 Amba Ladino 4.6 4.6 4.1 3.5 4.1 1.7 1.7 1.0 Niva VNS 3.5 3.5 3.8 3.0 2.0 2.0 1.5 2.3 Niva Jumbo 4.3 3.6 3.5 3.6 1.4 1.7 1.4 2.5 Niva Ladino 3.3 4.3 4.3 3.3 2.7 2.0 2.0 2.7 Sparta VNS 3.8 3.8 3.5 3.6 2.7 1.0 1.0 2.0 Sparta Jumbo 3.8 4.5 4.5 4.0 3.4 3.0 1.9 3.2 Sparta Ladino 3.8 2.8 4.5 3.3 2.9 1.5 1.9 2.2 Tekapo Endura 3.8 4.0 5.0 4.5 2.5 3.9 3.5 2.2 Tekapo VNS 4.0 2.8 3.6 2.8 1.4 1.7 1.4 2.7 Tekapo Star Fire 3.8 2.1 2.0 3.5 2.0 3.4 2.2 1.2 Tekapo Kopu 11 4.1 4.5 4.5 3.6 2.4 3.0 3.5 2.0 Tekapo Ladino 4.6 3.1 4.8 3.8 1.7 2.5 2.2 1.2 Aries Endura 4.6 4.5 4.0 4.8 4.2 3.7 4.5 3.3 Aries VNS 4.1 3.8 3.5 4.0 3.2 2.8 3.0 2.2 Aries Star Fire 3.8 3.8 3.8 3.0 4.4 2.2 3.7 2.0 Aries Kopu 11 3.6 4.6 4.5 4.8 3.4 1.8 3.7 1.2 Aries Ladino 4.8 3.5 3.1 3.0 4.2 1.5 3.0 2.3 Barfort VNS 4.5 3.1 1.3 2.3 3.8 1.8 3.0 2.0 Barfort Start 4.5 3.6 4.1 3.0 3.83 1.0 3.7 1.7 Barfort Alice 4.0 3.8 3.6 3.8 3.7 1.2 3.7 2.3 Barfort Ladino 4.6 4.3 4.1 3.1 4.0 1.5 2.5 2.5 Calibra VNS 4.8 3.3 2.1 3.0 4.4 1.5 1.9 1.8 Calibra Jumbo 4.3 4.3 3.3 3.8 5.0 1.4 4.0 2.0 Calibra Ladino 5.0 4.1 4.1 2.6 2.7 2.7 4.7 2.7 Mara VNS 4.0 2.0 1.5 1.5 3.5 1.5 2.5 4.3 Mara Start 4.3 2.6 1.8 2.6 4.5 1.0 1.4 2.5 Mara Alice 5.0 3.1 2.1 2.6 4.5 1.0 2.9 3.3 Mara Ladino 4.5 2.1 2.0 2.3 4.5 1.0 2.4 3.5 Mavrick Gold Endura 4.8 3.8 3.6 4.0 3.7 2.4 2.7 2.2 Mavrick Gold VNS 4.1 2.8 2.1 2.3 3.0 2 2.9 1.5 Mavrick Gold Star Fire 4.1 3.3 3.1 2.6 3.7 1.2 2.4 1.0 Mavrick Gold Kopu 11 4.5 4.0 3.8 4.5 4.4 1.0 2.7 2.2 Mavrick Gold Ladino 4.3 4.0 2.6 3.8 4.0 1.9 3.0 1.5 Quartet Endura 4.8 4.0 4.3 4.5 4.5 3.9 4.7 2.5 103 Table 3 continued Grass Clover 2004 2005 2006 Cultivars Cultivars 28-May 26-Jun 28-Jul 9-Sgp 6-May 16-Jun 4-Au 12-May Quartet VNS 4.6 4.5 4.1 4.5 2.9 2.2 3.2 2.0 Quartet Ladino 4.6 4.6 3.5 3.6 3.5 1.0 3.9 1.5 Quartet Star Fire 4.8 4.6 4.6 3.3 3.5 1.4 3.5 1.5 Quartet Kopu 11 5.0 4.5 4.8 2.6 3.4 3.7 4.5 2.0 Tonga Endura 4.6 3.6 2.6 2.5 3.5 1.9 4.2 3.2 Tonga VNS 4.0 3.5 2.8 1.8 4.0 1.0 4.0 2.0 Tonga Star Fire 4.3 4.5 3.5 3.3 3.5 2.9 3.2 1.8 Tonga Kopu 11 4.5 3.8 3.6 3.1 4.5 1.6 2.7 2.5 Tonga Ladino 4.8 4.6 4.6 3.3 4.0 3.2 4.7 2.3 Bronson VNS 2.5 1.6 3.0 1.1 3.4 1.7 1.0 1.0 Bronson Endura 2.8 2.1 3.1 1.8 3.7 3.5 2.7 1.0 Bronson Kopu 11 2.6 2.1 4.0 2.0 3.2 1.5 1.4 1.0 Bronson Ladino 3.6 2.5 4.1 3.1 4.0 2.9 1.4 1.0 Bronson Star Fire 3.5 2.0 3.1 1.6 2.9 1.0 1.0 1.3 K5666V VNS 3.6 3.3 4.5 2.6 3.7 1.0 1.7 1.7 K5666V Endura 4.0 3.8 4.6 4.0 4.2 2.5 4.7 2.3 K5666V Kopu 11 3.8 4.1 5.0 4.5 3.9 1.3 2.9 1.8 K5666V Ladino 4.1 3.1 3.8 2.1 3.7 2.4 2.7 1.3 K5666V Star Fire 3.3 2.5 3.5 2.6 3.4 1.7 3.2 1.0 Barolex Alice 3.3 4.0 3.8 3.1 4.8 1.5 2.2 1.7 Barolex VNS 2.5 3.5 2.6 1.6 4.2 1.8 1.5 1.2 Barolex Ladino 3.5 3.5 3.1 1.6 3.7 1.2 1.0 1.0 Barolex Start 2.5 2.6 3.0 1.5 2.5 1.2 1.0 1.3 Mean 4.1 3.5 3.5 3.1 3.5 1.9 2.6 1.9 CV 18.1 26.1 30.5 33.3 26.6 53.5 37.3 51.7 LSD (0.05) 1.2 1.5 1.7 1.6 1.5 1.6 1.6 1.7 1 = less than 20% of the plot grazed 5 = 80% or geater of the plot was gazed Grass cultivars: Festulolium (Duo and Hykor) Orchardgass (Amba, Niva, Sparta and Tekapo) Perennial ryegass (Aries, Barfort, Calibra, Mara, Maverick Gold, Quartet, and Tonga,) Tall fescue (Bronson, K5666V, and Barolex) Clover cultivars: Red clover (Start Fire, Start and VNS) White clover (Ladino, Alice, Kopu II, and Jumbo) Kura (Endura) 104 Table 4 . The mean values (%) of forage quality components (CP, ADF and NDF) for pasture species of gass, clover and binary mixtures over 2004-2005 gowing seasons in three different locations. 2004 2005 pasture Type CP" I ADF” | NDF' CP I ADF I NDF Grass 16.9 28.2 45.6 20.2 28. 2 54.2 Clover 20.2 26.4 33.4 20.6 20.9 29.8 Binary Mixtures 20.1 25.9 43.9 17.7 25.8 42.4 Values based on the (Lsmeans) of all locations and cuts x Crude protein y Acid detergent fiber (ADF) 2 Neutral detergent fiber (NDF) Table 5. Average forage quality parameters (CP, ADF and NDF) of 16 gass cultivars established in monoculture and binary mixtures in three locations. Grass Grass Monoculture Binary Mixtures Species Cultivars CF I ADF I NDF CP I ADF I NDF % Duo 19.4 25.6 48.2 23.6 22.1 37.1 Fest Hykor 17.6 29.7 51.5 20.5 25.2 44.6 Tekapo 19.2 27.8 52.2 22.5 24.3 42.7 Amba 18.9 26.1 49.3 21.7 23 .7 41.9 OR Niva 19.3 25.2 50.7 22.4 24.3 42.9 Sparta 20.2 26.4 50.2 22.3 23.8 42.4 An'es 19.1 24.9 48.8 23.7 22.2 36.7 Maverick Gold 20.6 23.9 49.1 23.5 22.0 373 Quartet 20.1 25.1 45.7 24.3 21.4 35.7 PR Tonga 20.1 23.4 46.2 24.0 21.5 35.5 Barfort 19.8 23.7 46.9 23.7 21.7 36.4 Mara 18.8 25.8 49.5 22.3 23.2 39.7 Calibra 19.4 25.8 47.4 23.6 22.0 36.9 Bronson 18.6 29.3 54.3 21.3 24.5 43.8 TF K5666V 18.5 28.1 50.3 22.4 23 .2 40.2 Barolex 17.5 28.9 52.8 21.6 24.1 42.5 F est= Festuloliums. OR= Orchardgass. PR=Perennial ryegass. TF= Tall fescue. 105 Table 6. Average forage quality parameters (CP, ADF and NDF) of eight clover cultivars established in monoculture in three locations. Clover Forage Quality Parameters Species Cultivars CP ADF NDF % Kura Endura 24.3 2 l .7 27 .9 Red Star Fire 23.7 23.1 29.8 Clover Start 21.6 21.9 28.5 VNS 23.9 22.9 29.3 Kopu II 24.5 20.6 26.0 White Alice 25.3 20.3 26.1 Clover Jumbo 25.3 20.2 25.1 Ladino 25.0 20.1 26.1 106 Chapter 3 PREDICTING BOTANICAL COMPOSITION OF GRASS-CLOVER PASTURES MIXTURES USING NEAR-INFRARED REFLECTANCE SPECTROSCOPY ABSTRACT Hand separation is a common method used to determine the botanical species composition of gass-legume swards. However, this method is very laborious and is time consuming. This study was conducted to evaluate the use of Near-Infrared Reflectance Spectroscopy (N IRS) to predict the species composition of several gass-clover binary mixtures with samples collected from three locations and over three-year period. Samples were taken during 2003-2005 gowing season from clover-gass binary mixture experiments at Kellogg Biological Research Station at Hickory Comers (KBS), Lake City Research Station (LC) and Upper Peninsula Experiment Station at Chatham (UPES), MI. Second cutting event from each location was hand separated into gass, clover and weeds. All samples were dried, gound and scanned with NIRS. Three calibration equations were developed to predict the Species composition. The first equation was developed using artificially mixed samples in 10% increments of pure gass and clover samples collected from monoculture plots at LC location in 2004. The second equation was created from hand-separated samples clipped at LC location in 2004. The third equation was created from selected subsets of hand-separated samples collected from all three locations and three years. The equations developed based on artificially mixed samples and the hand-separated samples from the Single location and year resulted in a poor prediction of gass and clover components. Prediction coefficients of determination (R2) of gass and clover were, 0.24 and 0.31, respectively for artificially mixed samples 107 equation and were equal 0.25 and 0.37 for the hand-separation equation. Standard errors of prediction (SEP) were relatively high for both calibration equations. However, the equations developed based on selected hand-separated samples from all three locations and all three years had higher prediction accuracy with R2 ranging from 0.67 to 0.72 and SEP from 6.9 to 12.8, respectively. These results suggest that using either artificially mixed or hand separated samples from a single location in a Single year is unsuitable to predict species composition at different locations and years. It can be concluded that NIRS can be applied to replace the hand separation method using the calibration equation developed from hand separation data from different locations and years with some limitations. 108 INTRODUCTION AND BACKGROUND Legume content in a binary mixture is a key parameter for the quantification of N2 fixation and diet quality. Pastures with less than 30% legume should either be fertilized with up to 168 kg of N ha'l or improved by introducing legumes in the sward. Determination of botanical composition is important, since animal performance is dependent on the proportion of desired plant species in the diet (Petersen et al., 1987). The development of a reliable and rapid approach for determining botanical composition has been a research goal for many years. There are several indirect methods for estimating botanical composition of gass and legume mixtures including visual estimates (Marten, 1964; Tanner et al., 1966; Tiwari et al., 1963), point quadrate methods (Leasure, 1949; Vankeuren and Ahl gen 1957), dry-weight rank method (Mannetij and Haydock, 1963; Walker, 1970) and chemical composition based method (Cooper et al., 1957). The method that is commonly used for determining botanical composition is hand-separation (Vankeuren and Ahl gen, 1957). Hand separation requires manually separating the mixture into its components such as legumes, gasses, and weeds and the component percentage is then determined by dry matter weight. However, hand- separation is not practical since it is laborious, time-consuming, costly, and prone to operator errors, especially when a large number of samples are being processed. Up to 2 to 3 hr may be required for identification and separation of sown pasture samples (Grant, 1981). Therefore, Near Infrared Reflectance Spectroscopy (N IRS) may be able to replace hand-separation as a rapid and more convenient technique. The primary use of NIRS in forages is to determine nutrient composition values of feedstuffs (Norris et al., 1976). NIRS is an inexpensive method, which allows the 109 dried forage samples to be stored and then processed. Hand separation requires the samples to be fresh and processed as soon as possible after harvest (Shaffer et al., 1990). NIRS instruments use light at different wavelength in the NIR region to make measurements. The light is either absorbed or reflected by the sample and the wavelengths are determined at intervals between 700-2500 nm by a sensor. The absorption of the light in the NIRS region is primarily due to the fi'equency and arrangement of X-H bounds (Shenk and Westerhaus, 1994). Based on the absorption of light, the forage composition may be predicted. Calibration equations are developed from samples with known entities of interest (i.e acid detergent fiber or crude protein). These entities are associated with their spectral values. The most accurate calibration equations are developed from samples that represent all the variables that affect the NIRS. Shenk et al. (1979) demonstrated that the percent legume in gass-legume mixtures could be predicted within i 10 % by NIRS. Several researchers have attempted to use NIRS as an approach to determine botanical compositions. Some researchers have already proven the capability of NIRS to determine legume content in legume-gass mixtures (Petersen et al., 1987; Pitrnan et al., 1991 ). Coleman et al. (1985) concluded that with proper calibration (R2 from 0.95 to 0.99 and SEP from 1.9 to 6.9), NIRS could accurately determine species composition. Petersen et al. (1987) reported a high R2 when predicting species composition in tall fescue (F estuca arundinacea Schreb.) and white clover (T rifolium repens L) mixtures. Wachendorf et.al.(1999) successfully predicted red clover (T rifolium pratense L.) and white clover-gass mixtures content by using calibration equations from samples that included gass-clover mixtures collected at different years and locations. Coleman et al. 110 (1990) predicted the botanical composition of legumes and gasses mixtures using a calibration equation from a goup of pure samples, each sample consisting of one of three botanical components to be validated by hand separation. They reported excellent prediction of the legume component with prediction coefficient of determination R2 of 0.96 compared with caucasian bluestem [Andropogon caucasicus (Trin) C.E. Hubb] and cheatgass (Bromus tectorum L.) that had R2 of 0.77 and 0.84, respectively. Shaffer et a1. (1990) predicted alfalfa (Medicago sativa L.) and ryegass (Lolium perenne L.) in mixtures using an equation developed based on data from different locations and years. However, higher SEP was observed in prediction botanical composition of alfalfa- ryegass from locations not included in the calibration equation. This may infer that calibration equations should be derived from samples representing all the variables that might influence the NIRS results, such as climate, soil type and species. Shaffer et al. (1990) concluded that approximately 200 samples were required to provide sufficiently accurate botanical composition prediction. Locher et al. (2005) obtained an accurate prediction of legume content over a broad variation of multispecies clover-gass, plant age, and Site conditions. It is generally believed that NIRS will accurately quantify the botanical composition of binary mixtures of vegetative gasses and legumes. However, no work has been done to develop calibration equations from several vegetative pasture gass- clover mixtures established at various latitudes over multiple— years period under North- central US gowing conditions. The objectives of this study were (i) to determine if NIRS could accurately predict species composition of several vegetative pasture gass-clover mixtures in three different 11] locations over three-year period and (ii) to compare prediction accuracy of two calibration equations, one developed from pure laboratory-mixed samples and the other developed from hand separation samples, both clipped from a Single location and year. MATERIALS AND METHODS Plant Material and Locations: Cool-season gass and clover binary mixtures were established in summer of 2001 at three Michigan State University (MSU) experimental stations: (i) Kellogg Biological Research Station at Hickory Comers (KBS) (42° 24' N, 85° 24' W); (ii) The Beef Cattle and Forage Research Station at Lake City (LC) (44°19' N, 85°12' W), and (iii) Upper Peninsula Experiment Station at Chatham (U PES) (46°33' N, 86°55' W). Three to five cutting events, depending on the location, were used to obtain samples during 2003-2005 gowing seasons with 30 to 35 days interval between cutting events. More cuttings were taken at the KBS site since it is located filrther south than LC and UPES sites and has a longer gowing season. Twenty-four clover and gass cultivars were used for this study. Clovers included three red clover cultivars (VNS', Star Fire, and Start), four white clover (Kopull, Ladino, Jumbo, and Alice), one kura clover cultivar (Endura). The gasses included two festuloliums cultivars (Duo and Hykor), four orchardgass (Tekapo, Amba, Niva, and Sparta), seven perennial ryegass (Aries, Maverick Gold, Quartet, Tonga, Barfort, Mara and Calibra) and three tall fescue cultivars (Bronson, K5666V, and Barolex). At each location, the experiment was arranged in a randomized complete block design (RCBD) with three replications. Each replication consisted of 67 entries of different combinations of the above mentioned gass and clover cultivars seeded in 1.8 by 5 m plots. ' Variety Not Stated 112 In addition, the gass and clover cultivars were established as monocultures in plots of the same size as these of the binary mixtures portion as previously explained in chapter 1. Samples were hand clipped within a 0.25 m2 quadrate in each plot when plants were 20 cm in height. Clipped samples were dried at 65 °C in a forced-air oven for 48 hr. All samples were gound to pass through a 1mm-screen in a Christy-Norris cyclone mill (Christy-Norris, lnc., Ipswitch, UK). NIRS procedure: Two gams of each dried sample was packed into a sample holder with a 30 mm diameter quartz window and scanned with a NIRS monochromator (FOSS 6500). The wavelength range of 400-2500 nm was scanned at every 2 nm giving a total of 1050 data points. All the spectral data were recorded as log R], where R is reflectance. Reflectance data were regesses on each constitute of the binary mixtures, that is, measured percentages of gass, legume and weed components to develop calibration equations. Standard deviation of calibration (SD), standard error of calibration (SEC) and calibration coefficient of determination (R2) were used to evaluate the calibration equation. The calibration equation was validated by comparing the reference standards (hand separated or artificially pure samples) with NIRS predicted values. Prediction coefficient of determination (R2), standard error of prediction (SEP), Slope, and bias were used as validation criteria. Calibration equations were developed using two different strategies described below. 113 1. Calibration Equation Developed From Artificially Pure Mixed Samples of 2004 Lake City data. Pure gass and clover samples were clipped from monoculture plots at the Lake City site during the 2004 season. The samples were dried and gound as previously indicated. Artificially pure samples were hand mixed at 10% increments to a total of 4 g providing 11 possible combinations between each individual gass (Perennial ryegass, orchardgass, festuloliums and tall fescue) and clover species (white, red and kura clover). For instance, one mixture might contain 90% of perennial rye gass with 10% white clover, where a second mixture may include 80% of perennial rye gass with 20% white clover and so on). A total of 132 artificially mixed samples were made from the 4 gass and 3 clover species combinations. Mixed samples were packed into sample holders and scanned by NIRS as described previously. The calibration equations were developed (wavelengths 400 to 2492 nm) using an equation development progam within the NIRS software from WinISI ver. 1.5 (FOSS NIRSystems, Inc., Eden Prairie, MN). The partial least-squares method was used to eliminate outliers. Five outliers were eliminated and remaining 127 samples were used to generate the calibration equation. Weeds were not included in the calibration equation. I II. Calibration Equation Developed From Hand-Separated Mixed Samples :— In each location, a total of 201 (67 entries at three replications) samples were clipped from binary mixtures treatments and hand separated into three components: gasses, clovers, and undefined weeds species, mostly dandelion (T araxacum oflicinale). The three separated components were dried, weighed separately, recombined and then gound using the same ginding method as the pure mixed samples. Each sample was 114 scanned using NIRS following the previously described protocol. Two calibration equations were developed from hand-separated samples. a. Calibration equation developed from hand-separation of 2004 Lake City data This equation was derived from selected hand-separated samples from the 201 binary mixtures samples collected from LC during 2004 (weeds not included). Two outliers were eliminated from gass data and remaining 199 gass samples were used to develop the calibration equation. In addition, 60 outliers were eliminated from clover data and remaining 141 samples were used to generate the calibrating equation. The geater number of outliers eliminated fi'om clover samples was due to the poor persistence of the clover over a period of years causing reduction in clover portion in the mixed samples (Chapterl ). The purpose was to determine whether this calibration equation, which created from hand separation at single location and year, could provide a higher prediction accuracy of the binary mixtures composition than the calibration equation developed from artificial mixed samples obtained from the same single location and year. Validation statistics (R2 and SEP) values obtained from artificial pure mixed and hand-separation equations were reported. b. Calibration equation developed from multiple locations and years This calibration equation was obtained based on the hand-separated mixtures samples collected from the three locations (KBS, LC and UPES) over 2003-2005 seasons. The reason for creating this equation was to determine if the prediction of the binary mixtures improved when more samples from different locations and years were included. A total of 1809 samples (201 *3 locations *3 years) were clipped from the 115 second cutting events in the three locations over three years. The samples were hand- separated as explained earlier. Half of the samples was randomly selected (904 samples) to create an equation to predict gass-clover species composition. The reflectance data from 471 gass, 455 clover and 381 weed samples were selected after outliers were eliminated using the Select progam from WinISI, v. 1.5 software (Infrasofl International, LLC, Silver Springs, MD). Reflectance data were regessed on the proportion of each botanical component to develop three equations: one for gasses, one for clovers and one for weeds. All the equations were developed to predict the gass-clover botanical composition samples collected from all cutting events during 2003 -2005 in three locations (KBS, LC, and UPES). i 116 RESULTS AND DISCUSSION 1. Artificially pure mixed samples method: Table 1 lists the results of the NIRS calibration and validation statistics for estimating gass and clover content using the artificial pure mixed method. Data presented in Table 1 shows a very strong calibration equation with R2 of 0.99 and standard error of calibration (SEC) of 1.4. The high R2 of this equation is likely due to accurate handling of the pure mixtures samples with high precision in sample preparation and weighing samples using a sensitive scale. However, regession analyses of the spectral data with botanical composition resulted in prediction coefficient of determination (R2) of 0.31 and 0.24 and SEP of 28.1 and 26.7 for gass and clover respectively (Tablel ). This indicated that this equation failed to predict the actual botanical composition of the pasture species. The reason for poor performance is that all artificially mixed samples were collected from one location and a single year. Additionally, the variation in plant maturity and weed content observed in the field samples were not represented in the lab mixed samples. Thus, the calibration equation developed from the artificially mixed samples of several gass and clover Species collected from one location in a Single year did not accuracy predict the species composition in field samples clipped fiom three different locations over three gowing seasons. A higher prediction may obtain if the calibration equation was derived from samples representing all locations and years (Shaffer et. al., 1990). 11. Hand separation methods: a. Equation developed from Hand-separation of LC 2004: Table 2 represents the calibration equation and validation statistics for predicting the botanical composition from an equation developed from hand separated samples collected in the single location 117 and year. Calibration equations had R2 of 0.97 for gass and 0.95 for clover. However, when this equation was applied to predict the botanical composition of samples collected from three locations and three years, similar prediction results were obtained to the results of the artificial pure mixed samples with validation R2 of 0.25 for gass with somewhat improvement prediction for clovers with R2 of 0.37 (Table 2). This clearly reflects the problem of obtaining enough representative samples that can include all Spectra data from other locations. b. Equation developed from multiple locations and years: Table 3 lists the calibration equations developed fiom hand-separated samples collected from three locations over three years. Calibration equations had R2 of 0.82 for gass and 0.84 for both clovers and weeds (Table 3). The validation statistics for these equations resulted in an R2 of 0.67 to 0.72, SEP of 6.9 to 12.8, and a bias of 0.3 to 0.6% (Table 3). The regession of each component is illustrated in Fig. 1. Slopes were close to one for the gass and clover. Calibration samples comprised a wide range of values from 0 to 100 (g g’1 DM) for gass, 0 to 95 (g g‘1 DM) for clover, and 0 to 85 (g g'1 DM) for weed (Figl). Unlike the previous methods, this result suggests that using the same gass and clover species for both . calibration and validation Should improve the accuracy of NIRS predictions of these species. In spite of there being multiple species in the weeds portion, SEP for weeds was lower than gass and clover components. It is possible the weed species were more similar in reflectance values than the different Species of gasses. In conclusion, even though we had some success in predicting gass-clover mixtures based on multiple locations and years as compared with the equation created from a single location and year, this study did not result in as high R 2 as those observed 118 in other studies (Locher et al., 2005). The lower R2 observed in this study might be related to various factors. The calibration equations were derived from a large number of samples including different gass and clover cultivars in three different locations. Different cultivars, environmental conditions, the grinding processing and storing the samples can affect NIRS prediction (Shaffer, et al., 1990). In addition, clover and gass samples used in developing calibration equations were less mature than samples used in other studies. This may increase the difficulty of differentiation by NIRS since fiber content (hydrogen bonds arrangement and quantity) of immature gass and clover species were very similar. Coleman et al. (1985) indicated that the errors found with hay species were associated with (i) composition error (ii) machine error (iii) sampling error and (iv) methodology error. Hence, it is possible to generate a calibration equation developed from hand separation samples if the handing of the samples were controlled to reduce the variability among the samples. CONCLUSIONS Previously conducted research has Shown success in predicting the botanical composition of gass-legume mixtures using artificial mixed pasture samples. This study showed that NIRS did not accuracy determine botanical composition of pasture gass- clover mixtures based on equation generated from artificial pure mixtures or hand- separated samples collected from a single location and year, since it may not represented the maturities of samples to be predicted. However, equations generated from hand separations of several gasses and clovers across all locations and years resulted in a more accurate prediction with some limitations. Some pasture gasses and clovers that are harvested at earlier maturities have similar fiber content (Chapter 2). This may explain 119 the lower R2 obtained in this study compared to other studies conducted using more mature hay samples. Environmental conditions may also cause variation in spectral properties of samples. Therefore, it is necessary to select diverse samples for calibration in order to obtain the best prediction from the pure sample equations. This study, which presented two different strategies for developing a calibration equation, has shown that creating an equation from representative samples of a larger database of previously hand-separated mixtures can increase the prediction accuracy. Thus, NIRS can replace the hand separation method for botanical composition determination to a prediction accuracy (SEP) of d: 12%, and R2 ranging from 0.67 to 0.72. 120 l l:- LITERATURE CITED Coleman, S.W., F .E. Barton 11, and RD. Meyer. 1985. The use of near- infrared reflectance to predict species composition of forage mixture. Crop Sci. 25: 834- 837. Coleman, S.W., S.Christiansen, and J .S.Shenk.1990. Prediction of botanical composition using NIRS calibration developed fi'om botanically pure samples. Crop Sci. 30:202-207. Cooper, C.S., D.N. Hyder, R.G. Petersen, and RA. Sneva. 1957.The constituent differential method of estimating species composition in mixed hay. Agon. J. 49:190-193. Grant, S.A.1981. Sward components. p. 71-92. In J. Hodgson et al.(ed) Sward measurement handbook. British Grassland Society, Berkshire, UK. Locher, F ., H. Heuwinkel, R.Gutser, and U. Schmidhalter. 2005. Development of near infrared reflectance spectroscopy calibration to estimate legume content of multispecies legume-gass mixtures. Agon. J. 97:11-17. Leasure, L.K. 1949. Determining the species composition of swards. Agon. J .41 :204- 206. Mannetij, LT, and K.Haydock. 1963. The dry-weight-rank method for botanical analysis of pasture. J .Br.Grassl. Soc. 1 8:263-275. Marten, G.C. 1964. Visual estimation of botanical composition in simple legume-gass mixtures. Agn. J. 56:549-552. Norris, K.H., R.F.Bames, J .E. Moore, and J .S. Shenk. 1976. Predicting forage quality by infrared reflectance spectroscopy .J. Anim. Sci. 43: 889- 897. Petersen, J .C., F .E Barton, 11, W.R. Windham, and CS. Hoveland. 1987. Botanical composition definition of tall fescue-white clover mixture by near infrared reflectance spectroscopy. Crop Sci. 27: 1077-1080. Pitman, W.D., C.K. Piacitelli., G.E Aiken., and RE. Barton 11. 1991. Botanical composition of tropical gass-legume pasture estimated with Near-Infrared Reflectance spectroscopy. AgnJ . 83: 103-107. Shaffer, J. A., J .S. Shenk., and SM Abrams. 1990. Estimation of botanical composition in alfalfa/ryegass mixtures by Near Infrared Spectroscopy. Agon. J 82:669-673. 121 Shenk, J. S., and M .O Westerhaus.. 1994. The application of Near infrared reflectance spectroscopy (NIRS) pp. 406-449. In Fahey, G. C., Jr. et al. (Eds) Forage quality, evaluation and utilization. American Society of Agonomy, Madison, WI. Shenk, J. S., MD. Westerhaus and MR. Hoover. 1979. Analysis of forage by near infrared reflectance. J. Dairy Sci. 62: 807-812. Tanner, J .W., E.E. Gamble, and WE. Tossel. 1966. Determination of botanical composition of two-component forage mixtures. Can. J. Plant Sci. 40:225-234. Tiwari, D.K., J .A. J ackobs, and S.G.Garmer.l963. Statistical technique for correcting botanical or floristic estimates in pasture research. Agon. J. 55:226-228. r Vankeuren, R.W., and H.L. Ahlgen. 1957. A statistical study of several methods used in _ determining the botanical composition of a sward: I.A study of established .j pastures. Agon.J.49z532-536. Walker, B.H. 1970. An evaluation of eight methods of botanical analysis on gasslands in h Rhodesia. J. Appl . Ecol. 7:403-416. Wachendorf, M., B.Ingwersen and F. Taube. 1999. Prediction of the red clover-and white clover-gass mixtures by near-infrared reflectance spectroscopy. Grass Forage Sci. 541287-90. 122 Tablel. Calibration and validation statistics for NIRS determination of botanical composition of gass- clover mixture samples collected over 2003-2005 in KBS, LC and UPES using calibration equations developed from artificial mixed samples of 2004 Lake City data. Calibration Validation Mixtures type n+ SD: SECrr R211 n Bias Slope SEP§ R244 Grass 127 31.93 1.14 0.99 1440 -14.1 0.44 28.1 0.31 Clover 127 31.93 1.14 0.99 1375 6.7 0.40 26.7 0.24 Tab1e2. Calibration and validation statistics for NIRS determination of botanical composition of gass- clover mixture samples collected over 2003-2005 in KBS, LC and UPES using calibration equations developed from hand-separation samples of 2004 Lake City data. Calibration Validation Mixtures type n+ SD: SECrt R211 n Bias Slope SEP§ R24: Grass 199 19.13 3.22 0.97 1437 -20.81 0.36 27.41 0.25 Clover 141 20.53 4.17 0.95 1375 -0.88 0.56 20.95 0.37 Table.3. Calibration and validation statistics for NIRS determination of botanical composition of gass- clover mixture and weed samples collected over 2003-2005 in KBS, LC and UPES using calibration equations developed from the three years and three locations hand separation samples. Calibration Validation Mixtures type n+ SD: SECn RZ1| n Bias Slope SEP§ R24! Grass 471 21.8 9.3 0.82 946 0.53 0.90 12.8 0.67 Clover 455 22.1 8.9 0.84 902 0.35 0.94 12.22 0.72 Weed 381 10.0 4.0 0.84 763 0.64 1.04 6.99 0.68 + Number of samples. 1: Standard deviation of calibration sample set. 21:1 Standard error of calibration sample set. 1] Calibration coefficient of determination. § Standard error of prediction. # Prediction coefficient of determination. 123 A 50. ° 3‘ 40« . :g 20 . Sltzipe: 0.90 10 R = 0.67 0 . . r . . 0 20 40 60 80 100 NIRS predicted grass content % 8 (a) Hand separated % grasses A 888883888 10 NIRS predicted clover content % 100 (b) Hand separated "/o clovers 100 401 Slope: 1.04 if = 0.68 T r O 20 40 60 80 100 (c) Hand separated % weeds N IRS predicted weed content “/e Figl. Relationship of NIRS predicted percentage to hand-separated of gasses (a), clovers (b), and weeds (c) using a calibration equation of the hand separation of each component over three years at three experimental research stations. The solid line represents the regession with a slope and the coefficient of determination R2 124 GENERAL SUMMARY This research was conducted to evaluate the effects of gowing pastures as binary mixtures of perennial gass and clovers upon animal preference, forage quality, plant persistence, botanical composition, and dry matter production. Growing clovers with perennial gasses in binary mixtures resulted in increased pasture dry matter yield, persistence, forage quality, and animal preference. Grass monoculture treatments resulted in lower persistence and sigiificantly more winter injury compared to the same gass species and cultivars gown in binary mixtures. Differences in persistence and winter injury due to location were observed. At northern latitudes (44°-46° N), where cold temperature predominate, higher incidence of winter injury occurred with less winter hardy cultivars. Tall fescue and orchardgass cultivars resulted in better persistence than perennial ryegass and festulolium. Orchardgasses dry matter yield was slightly less than tall fescue but higher in animal preference. Among clover species, kura clover Showed a high persistence at KBS and increased in clover content over time in all binary mixtures, which would indicate its potential as an excellent clover for gazing. Limited precipitation and high temperatures in 2005 can explain the reduction in pasture productivity at all locations. There were significant differences in animal preferences among monoculture perennial gass species and cultivars. Forage quality of binary mixtures was higher in CP, and lower in ADF, and NDF than gass monoculture, which resulted in higher animal preferences for binary mixtures compared to monocultures of gass. Perennial ryegass-clover binary mixtures resulted in significantly higher forage quality and animal preference compared to perennial ryegass monocultures. However, 125 “M.H-Dir-.. l' - some perennial ryegass cultivars that demonstrated a higher animal preference was less winter hardy. Binary mixtures of festulolium (Duo)-clover and perennial ryegass-clover increased animal preference and forage quality compared to monoculture festulolium and perennial ryegass, indicating these mixtures are a good choice for livestock producers to use for gazing. Total dry matter yield and animal preferences were not always positively correlated. The study of Near-Infrared Reflectance Spectroscopy (NIRS) showed that using either pure mixed samples or hand separation from single location and year resulted in low prediction accuracy in determining gass-clover binary mixtures samples collected from KBS, LC and UPES locations during 2003-2005 gowing season. In contrast, NIRS prediction accuracy was improved when the calibration equation was derived from hand- separated samples collected from the same locations and years. In summary, this research provided a better understanding of the importance of species and cultivar selection for performance in gazing systems across three latitudes in Michigan. It also provided helpful information on gass-clover relationships in pastures over time under rotational gazing. In addition, the study documented the positive benefits of proper gass-clover cultivar and species selection for higher animal preference and plant persistence. Finally, NIRS has the potential to replace hand-separation in determining pasture species composition when calibration equation was developed from a large data set, which represents environments between locations and years. 126 APPENDICES 127 I I,Supe Ito'r‘.‘ I" I ..... -‘ ‘4. . E“~ "r :1? I £T'IOquMon I \ ‘ ‘~ . ‘7: :f 3 00111064190? , nMarquette I . H O R I ‘ _ . Hunting" =2 . . boygan * Iriilpenasi ' 44°N Fig 1A. Michigan map Showing the three experimental locations representing different latitudes in Michigan: Kellogg Biological Research Station at Hickory Comets (KBS) (1), Lake City Research Station (LC) (2), and Upper Peninsula Experiment Station at Chatham (UPES) (3). 128 Grass-clover binary mixture plots Plot trt Plot trt Plot trt Plot trt Plot trt Plot tl‘t Plot trt Plot trt 101 1 110 10 119 19 128 28 137 37 146 46 155 55 164 64 102 2 111 11 120 20 129 29 138 38 147 47 156 56 165 65 103 3 112 12 121 21 130 30 139 39 148 48 157 57 166 66 104 4 113 13 122 22 131 31 140 40 149 49 158 58 167 67 R1 105 5 114 14 123 23 132 32 141 41 150 50 159 59 168 68* 106 6 115 15 124 24 133 33 142 42 151 51 160 60 169 69* 107 7 116 16 125 25 134 34 143 43 152 52 161 61 170 70" 108 8 117 17 126 26 135 35 144 44 153 53 162 62 171 71* 109 9 118 18 127 27 136 36 145 45 154 54 163 63 172 72* 201 56 210 31 219 63 228 36 237 64 246 43 255 61 264 55 202 48 211 27 220 29 229 9 238 41 247 40 256 3 265 35 203 21 212 39 221 18 230 15 239 54 248 37 257 2 266 57 R2 204 72* 213 16 222 26 231 50 240 11 249 59 258 47 267 4 205 53 214 60 223 8 232 30 241 22 250 14 259 49 268 65 206 70* 215 44 224 52 233 17 242 6 251 25 260 45 269 38 207 1 216 33 225 62 234 23 243 34 252 24 261 51 270 69* 208 67 217 58 226 5 235 66 244 12 253 20 262 42 271 71* 209 10 218 28 227 7 236 13 245 68* 254 32 263 46 272 19 301 7 310 17 319 50 328 45 337 35 346 23 355 3 364 67 302 28 311 27 320 12 329 71* 338 43 347 47 356 46 365 44 303 58 312 59 321 53 330 72* 339 18 348 24 357 48 366 22 R3 304 70* 313 15 322 6 331 20 340 40 349 9 358 51 367 32 305 2 314 42 323 63 332 19 341 38 350 57 359 8 368 68* 306 54 315 69* 324 39 333 62 342 60 351 25 360 16 369 10 307 31 316 4 325 1 334 29 343 30 352 11 361 61 370 37 308 52 317 21 326 33 335 34 344 49 353 65 362 13 371 56 309 14 318 66 327 41 336 5 345 26 354 55 363 64 372 36 Clover lots R1 101 73 102 74 103 75 104 76 105 77 106 78 107 79 108 80 R2 201 79 202 77 203 75 204 80 205 78 206 73 207 74 208 76 R3 301 76 302 78 303 74 304 73 305 80 306 79 307 77 308 75 Grassplots 101 81 103 83 105 85 107 87 109 89 111 91 113 93 115 95 R1 102 82 104 84 106 86 108 88 110 90 112 92 114 94 116 96 201 89 203 83 205 85 207 93 209 88 211 81 213 96 215 95 R2 202 87 204 94 206 90 208 92 210 86 212 82 214 91 216 84 301 96 303 92 305 89 307 87 309 82 311 90 313 85 315 84 R3 302 91 304 88 306 95 308 94 310 93 312 86 314 81 316 83 Fig. 2 A. The design map of grass-clover binary mixtures and grass and clover monoculture treatments. (* Trt.# 68,69,70,7l and 72 in the binary mixtures plots are blanks) 129 Binary mixtures portion (Rep 1) Binary mixtures portion (Rep2) Grazing area “ Section 1” Binary mixtures portion (Rep 3) Clover monocultures portion Grazing area “section 2” f Grass monocultures portion Fig. 3A. The experimental area grazing arrangement. 130 E, L5 eoasm 82 55> . x0355 00:80.0 :5. >ooomM 838$ :3. 5305 8380.: fig 05:00 mew—w?»— 3500: 0.8.2 $.25».— 35:23 team magma: 38:20: 05:0— :0>20 0:55 mwfidr mafiwob 358$ ugmém .80-: BEE. :03? 0:55 000.830 mmfiwPC 3:50: ws< -mm .m:<-m~ avenue—amt 29? 8:< 633 833 Boo 3.85.2 3:09: 3:880 .23 -2 337$ 20$ .858 552 = :moM :0>o_0 0:55 005 mag.— EE:0:0& 0:3. A 0:341 0.5 00:38 :82 ~A:Em mmmD :00..N E0m -5 9233320 050me 8.8mm mamawcbfiouo wa< -a ws< -m Emma 6200383 .mZ> :05? com «3 Z 00mmflwusao5 bi. -b 0:3. -3 £058 65% team :05? 00% BE 8mmfiwubw€5 32 -mm 52.2 :0 :82 30:3 0302 04 2E gm 005—0 3m came—0... 00mmfiwubfio5 000$: Bomd £35133 0E3. .w:<-m 33.6w 200:. 638388 .803: 9:23:50”— 0:3.-E 0:3... cm 605:: $802-0:E 820R.“ :05? 83— 0:9 meg—238m .32 -v >037 em 06 :82 8meme mmx 20.5—:0 0200mm 235—=0 momoomw mccu SEN In 09:. =em 25 820—0 3380 033:5 wfitsu Seam £5 :_ “00:02:88 mugs—:0 02:0 0:: $8» 05 :5 AmmmDv :ozfim #:085me 235:0: 0.52 b5 65 55 00—04 .6va :038m £8008”: Romwgomm wwo=0¥ «a 8808 wEBEw moom EB 38 :0>o 033:8 wfizso .3: :8 .089 mom .< 330:. 131 Table 2 A. Total monthly precipitation (mm) at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) during the growing season of 2004-2005 comparing with 30-year average. KBS Month of growing 2004 2005 1 30-yr Ave. season mm April 19.8 6.3 97.0 May 248.4 50.8 89.0 June 85.2 124 98.0 July 76.1 122.4 93.7 Aug. 131 11.4 100.1 Sep. 44.1 69.9 108 Total 604.6 384.8 585.8 Seasonal Average 100.8 64.2 97.7 LC Month of growing 2004 2005 1 30-yr Ave. season mm April 100.6 26.4 70.4 May 161.3 65.5 70.8 June 61.7 52.1 75.0 July 46.7 93.7 72.6 Aug. 53.0 113.8 92.9 Sep. 21.8 103.1 94.5 Total 445.1 454.6 476.2 Seasonal Average 74.2 75.8 79.4 UPES Months of growing 2004 2005 I 30-yr Ave. season mm April 60.7 36.8 40.13 May 107.4 51.0 72.4 June 75.9 41.4 77.7 July 92.9 98.5 90.6 Aug. 145.8 61.4 78.1 Sep. 50.5 123.4 93.7 Total 533.2 412.5 452.6 Seasonal Average 88.9 68.8 75.5 132 Table 3 A. Average daily maximum air temperatures (°C) at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) during the growing season of 2004-2005 comparing to 30-year average. KBS Months of growing 2004 I 2005 I 30—yr Ave. season ................ ° C April 17.3 18.2 15.3 May 22.0 19.9 22.3 June 25.2 30.0 27.1 July 27.5 30.4 29.2 Aug. 25.7 29.4 27.9 8g). 26.7 27.3 23.8 E" LC Months of growing 2004 I 2005 I 30-yr Ave. season ----------------- ° C April 13.1 14.8 11.4 May 17 16.4 19.3 June 22.7 27.5 24.2 _ July 25.5 27.4 26.6 Aug. 23.5 26.0 25.1 F Sep. 24.9 23.8 20.3 UPES Months of growing 2004 I 2005 I 30—yr Ave. season ----------------- ° C April 7.7 13.0 10.4 May 15.4 15.7 18.9 June 19.9 25.5 24.3 July 23.6 27.2 25.6 Aug. 22.4 26.4 24.9 Sep. 23.3 23.3 20.6 133 Table 4 A. Average daily minimum air temperatures (°C) and snow fall (cm) at Kellogg Biological Research Station (KBS), Lake City (LC) and Upper Peninsula Experiment Station (UPES) from January through April of 2003-2006 comparing with 30-yr. average KBS 2003 2004 2005 2006 30-yr Ave. Temp Snow Temp Snow Temp Snow Temp Snow Temp Snow Month °C cm °C cm °C cm °C cm °C cm Jan -9.8 18.9 -8.4 30.09 -9 17.6 -2 19.8 ~8.8 20.5 Feb -10.1 10.4 -7.7 11.6 -5 6.4 -6 9.2 -8.1 13.5 Mar -3.2 1.7 0.2 1.5 -5 1.2 -2 4.2 -3.2 10.2 Apr 3.3 0.5 2.3 0 4 0 4 0.3 2.4 2.9 L C Jan -12.6 l8 -14 19 -13 15 -5 14 -13 19.3 Feb -15.4 13 -11 12 -8 14 -11 16 -12.8 15.4 Mar -9.3 12 -4 11 -10 11 -6 13 -7.9 12.2 Apr -2.3 4 0 2 0 5 0 2 -0.9 4.4 UPES Jan -15.6 35 -15.8 32 -14 37 -7 31 -12.7 35.9 Feb -l8.4 26 -l4.0 29 -10 24 -13 28 —12.4 29 Mar -12.8 28 -7.4 22 -10 21 -6 22 -8.3 18.9 Apr -5.8 10 -2.7 8 -1 ll 0 7 -2.3 6.6 134 Table.5 A. Average animal weight (kg), and the number of animals in each grazing event during 2004-2006 grazing seasons. 2004 2005 2006* Animal Info 28-May 26-Jun 28-Jul 9-Sep 6-May l6-Jun 4-Aug 12-May Ave animal _ weight (kg) 266.22 31 1.85 384.42 41 l .11 243.46 365.60 403. 10 443.72 Number of Animals used 10 4 4 3 6 3 3 16 Breed: Holstein Steers Steers Steers Steers Steers Steers Steers Heifers * Single grazing was taken during 2006 season 135 8822: so: a 3% Sea 356 ea "EN ego—U wfiim ”Umz 8822: so: a as 83 53o 2:55 =£ noon: 830 9580 wqtam HUOm» has .253 us, F 88¢ 42. 58v 03 88v :._ 88v Ra 88v :.N Em 3.8.1.: 58... won 38v :.m 88.0 NS 58v 2 .o 58v «3 N: :52 88¢ 03 58v 2...“ 88v 8... 88v :2 58v 2a m: 5.3: 585 v: 58v 2.: 58v 3.: 58v 3% 88v 3. _ m 8 E 88¢ 3.3 58v 3.3 Ego N2 88v 3.2.. 58v no.2 a. 8.18» 886 a? 386 03m 2de 3m 58v 8.8 88¢ 32 N 8. 886 as 58v E: 203 a: 886 3.2 38v 218 N .3» n— A un— 03_m>ou— nm A Man 03—fl>..n~ ..m A ham 03—M>unw n— A ham 03—M>un~ ”— A ham 03—M>nnm ”—9 #00:” .8 .8 .08 . E5 .Aacoésaafiae 5:3 3 Ba $95 Ba 3 we: 25:82 608-3% e8» Set 83 0.3328 .935 Sm ago—o =£ can macaw Ea 8>oo 933w zfl .98 watam 55.? SE?» 8% <>OZ< .< o 035. 136 Table 7 A. ANOVA for winter injury, spring, and fall ground cover for grass monoculture data from years 2004-2006, locations (KBS, LC and UPES) and 16 grass varieties (Cultivars) WI‘ soc‘ FGC" Effect DF F-value Pr > F F-value Pr > F F-value Pr > F year 2 121.83 <.0001 83.55 <.0001 9.19 0.0387 Ice 2 152.05 <.0001 171.50 <.0001 13.93 0.0158 year*loc 4 133.52 <.0001 125.36 <.0001 49.22 0.0022 var 15 50.09 <.0001 43.27 <.0001 30.55 <.0001 year*var 30 2.23 <.0007 1.98 <.0034 2.85 <.0022 loc*var 30 8.74 <.0001 5.30 <.0001 4.97 <.0001 year*loc*var 60 4.47 <.0001 4.42 <.0001 4.02 <.0001 1] WI= Winter Injury *SGC= Spring Ground Cover xFGC= Fall Ground Cover (2006 data is not included) 137 Table 8 A. ANOVA for winter injury, spring, and fall ground cover for clover monoculture data from years 2004-2006, locations (KBS, LC and UPES) and eight clover varieties (Cultivars). 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