# Impacts of Improved Switchgrass and Big Bluestem Selections on Yield, Morphological Characteristics, and Biomass Quality

Authors: Erik Delaquis; Roger Samson; Philippe Seguin; Arif Mustafa; Huguette Martel
Journal: Advances in Agriculture
 (2014)

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## Abstract

Switchgrass (Panicum virgatum L.) and big bluestem (Andropogon gerardii V.) are promising warm-season grasses for biomass production. Understanding the morphological and quality-related traits of these grasses can guide breeders in developing strategies to improve yield and quality for bioindustrial applications. Elite selections were made in Southern Quebec from four promising varieties of switchgrass and one of big bluestem. Biomass yield, morphological characteristics, and selected quality traits were evaluated at two sites in 2011 and 2012. Significant variation was detected for all measured characteristics, with differences varying by site and year. In some cases the selection process modified characteristics including increasing height and reducing tiller mortality. Switchgrasses reached a similar tiller equilibrium density in both years of 690 m−2 and 379 m−2 at a productive and marginal site, respectively. Differences in yield were pronounced at the marginal site, with some advanced selections having a higher yield than their parent varieties. Switchgrass yields were generally greater than those of big bluestem. A delayed spring harvest date greatly reduced yield but reduced moisture content and slightly increased cellulose concentration. Big bluestem had a higher cellulose content than switchgrass, likely due to greater stem content.


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## Body

## 1. Introduction

Switchgrass (Panicum virgatumL.) is a perennial C4 grass native to North America which has historically been used as a forage crop and for conservation plantings [1–3]. Recently interest has shifted towards the use of the crop in biomass energy and biofibre applications [4], with research indicating significant production potential in Eastern Canada [5]. Growing interest in this multipurpose crop has led to an increasing number of breeding and selection programmes and the release of new commercial switchgrass selections in the 1980s (“Trailblazer,” “Forestburg,” “Dacotah,” and “KY1625”), 1990s (“Sunburst” and “Shawnee”), and 2000s (“High Tide,” “Carthage,” “BoMaster,” “Performer,” “Cimarron,” and “Colony”) [6–8]. Despite an increasing acreage dedicated to the production of this crop in Eastern Canada, these selections all represent the efforts of plant material improvement programs located in the Atlantic Coastal, Midwest, and Northern Great Plains regions of the United States. There has been little selection effortin situ in Eastern Canada or in the Northeastern United States.Big bluestem (Andropogon gerardii Vitman) is the most dominant grass of the tallgrass prairie ecosystem and has been demonstrated to be another high yielding warm-season grass in the Eastern North American context [9, 10]. Fully established stands of big bluestem can approximate the yields of switchgrass stands of a similar maturity [10, 11]. Big bluestem is generally taller than upland switchgrass and native big bluestem ecovars have been found to contain 62% of the biomass in the stem component [12], compared with native switchgrass with 47% [13]. Big bluestem appears to have some biomass quality advantages over switchgrass for certain fibre applications as it generally has improved fibre strength properties [11] and higher cellulose contents due to its higher stem-to-leaf ratio [14]. In an assessment of 5 switchgrasses and 4 big bluestems at heading, it was found that there were no differences in cellulose contents between big bluestem and switchgrass stems and leaves; however, stems of both species had on average 11% higher cellulose contents than leaves [14]. Early-harvested big bluestem has also been identified to have improved digestibility for livestock due to its leafy composition prior to heading [15]. Big bluestem has been used for forming polycultures with switchgrass and other native grasses and forbs in mixed prairie systems. Mixtures have many demonstrated benefits including increased indigenous avian and arthropod diversity and species richness [16, 17] and once fully established can produce similar yields to switchgrass monocultures [18, 19].Switchgrass production in Quebec currently covers about 1500 ha, with the acreage increasing up to 30% per year (Huguette Martel, unpublished data). The vast majority of this acreage is the variety “Cave-in-Rock,” a collection made from a field in Cave-in-Rock, Illinois, in 1958 [20]. Previous experiences indicate that appropriate regional selections can significantly increase yield potential in a given environment [21], but despite this there are currently no commercial varieties available that have been developed specifically for agronomic applications for Eastern Canada or the Northeastern United States. There has also been no plant breeding effort conducted in these regions for big bluestem.Previous studies with switchgrass and tall fescue confirmed the effectiveness of seedling-stage selection for developing selections with modified tiller number [22–24] and increased yield per tiller [22, 25]. It has also been demonstrated that selection and breeding programmes have the capacity to alter fiber composition in switchgrass [26], an important characteristic for energy and fibre crops. Fiber content, including lignin and cellulose concentrations, has been demonstrated to be important parameters for multiple conversion technologies and thus important breeding targets for biomass crops [15].The development of a spring harvest system for switchgrass is another potential avenue for improving biomass quality for energy and fibre applications. In biomass crops, the leaching of minerals from plant tissues throughout the winter has been shown to result in lower mineral concentrations [27, 28], while the loss of leaves may decrease the concentration of major ash components such as silicates and increase cellulose content [29]. Elevated levels of silica are generally considered undesirable for commercial combustion processes [30]. Spring harvesting also carries the added advantages of reducing labor demands during peak harvest time for commercial cash crops and drastically reducing moisture content at harvest which reduces or eliminates the need for drying [31] and is thus beneficial for baling and storage [27].The goal of the present study was to compare the agronomic characteristics of several commercial varieties of upland switchgrass and big bluestem along with advanced selections made from these varieties to determine the effects on their performance and morphological characteristics in Southern Quebec. Several of these selections were also subjected to both spring and fall harvest to determine the effects of harvest date on yield, fiber, mineral, and energy concentrations of the harvested biomass.


## 2. Material and Methods

### 2.1. Plant Materials

Selection lines and parent material were supplied by REAP-Canada, based in Southern Quebec (Sainte-Anne-de-Bellevue, QC, Canada). The biomass breeding program is utilizing short breeding cycles incorporating selection at the seedling stage followed by recurrent restricted phenotypic selection (RRPS) in mature spaced-plant nurseries [32]. A total of 11 upland switchgrass selections and three big bluestem selections were evaluated. These included three switchgrass parent varieties and seven selections derived from these (Table 1). “Sandlover,” a selection made by REAP-Canada from “NU-94-2” [15], was also evaluated bringing the total switchgrass selections evaluated to eleven. In addition, two selections of big bluestem were also evaluated alongside their parent material “Prairie View Indiana germplasm”.Table 1
Origins of the commercial switchgrass and big bluestem varieties evaluated in the present study and the selections derived from them through a local selection programme in Southern Quebec.
Variety/selection
Year of release
Site of origin
Latitude of origin (°N)
References
Switchgrass
Cave-in-Rock
1958
Cave-in-Rock, Illinois
37
Jefferson and McCaughey, 2012 [6]
Cave-in-Rock II
N/A
Valleyfield, Quebec
Present study
Cave-in-Rock Early
N/A
Valleyfield, Quebec
Present study
Summer
1953
Nebraska City, Nebraska
41
Jefferson and McCaughey, 2012 [6]
Tecumseh
N/A
Valleyfield, Quebec
Present study
Tecumseh II
N/A
Valleyfield, Quebec
Present study
Sunburst
1998
Union County, South Dakota
43
Jefferson and McCaughey, 2012 [6]
Blue Jacket
N/A
Valleyfield, Quebec
Present study
Blue Jacket II
N/A
Valleyfield, Quebec
Present study
Blue Jacket Early
N/A
Valleyfield, Quebec
Present study
Sandlover
2009
Northern Nebraska
36–40
Vermerris, 2008 [15]
Big bluestem
Prairie view
1994
20 sites across Indiana
38–41
Samson et al., 2014 [32]
Prairie view II
N/A
Valleyfield, Quebec
Present study
Prairie view Early
N/A
Valleyfield, Quebec
Present studyThe “Blue Jacket” and “Blue Jacket II” switchgrass selections were made from “Sunburst” switchgrass using RRPS [33]. The population of “Blue Jacket II” was selected for reduced tillering at the seedling stage, with 200 superior plants selected from a population of 1000 plants [22] followed by a RRPS selection made on mature plants. The “Blue Jacket Early” selection was derived from 50 plants which exhibited early spring growth in the year after establishment in a one ha seed field of “Blue Jacket” switchgrass in Valleyfield, Quebec. The plants were dug up in the spring of 2008 and replanted and seed was collected from the population in the fall of 2009.“Cave-in-Rock II” was derived from a seed collection in the fall of 2006 from 30 superior plants in an eight-year-old switchgrass field in Valleyfield, Quebec. The population was subsequently selected for reduced tillering at the seedling stage were transplanted in the field [22]. At the mature plant stage, the population was selected using RRPS and seed derived from superior plants from a 200-spaced-plant nursery was collected in fall 2009. The “Cave-in-Rock Early” population was derived from seed collected in fall of 2009 from 30 early maturing switchgrass plants in a 10-year-old field of “Cave-in-Rock” switchgrass in Valleyfield, Quebec.The “Tecumseh” and “Tecumseh II” selections were made from “Summer” switchgrass using RRPS [33]. A greenhouse population of 1000 plants of “Tecumseh II” was selected for reduced tillering at the seedling stage [22]. At the mature plant stage, the population was selected using RRPS and seed derived from superior plants from the 200-spaced-plant nursery was collected in fall of 2009.“Sandlover” was derived from 200 plants selected from a 1,000-spaced-plant nursery in Valleyfield, Quebec, using RRPS [33]. The original source population was Northern Upland “NU-942” obtained from Charles Taliaferro at the University of Oklahoma in 2006.Finally, the selections “Prairie View Early” and “Prairie View II” were selected from an 800-spaced-plant nursery of Prairie View Indiana germplasm big bluestem originally transplanted in 2008 in Valleyfield, Quebec.


### 2.2. Field Management and Data Collection

Plots were arranged in a randomized complete block design with four replications at two sites in Southern Quebec, Sainte-Anne-de-Bellevue (45°25′32.45′′N, 73°55′48.63′′W, 37 m elevation) and Cookshire-Eaton (45°20′57.49′′N, 71°47′08.40′′W, 243 m elevation). Plot size was 4 × 5 m in Sainte-Anne-de-Bellevue and 2.4 × 5 m in Cookshire-Eaton. The soil at the Sainte-Anne-de-Bellevue site was a free-draining St. Bernard sandy clay loam, while the Cookshire-Eaton site was an imperfectly drained Magog stony loam. All selections of both species were seeded in spring 2010 using a Fabro precision planter (Fabro Enterprises, Swift Current, SK, Canada) with an 18 cm row spacing. The seeding rate used for all selections was 300 pure live seeds (PLS) m−2. Nitrogen was applied at both sites as urea at a rate of 50 kg N ha−1 in May of 2011 and 2012; no other fertilization was done.Plant height was determined in each plot biweekly from May to September in 2011 and 2012. The height of 10 plants was measured in each of three subplots selected at random within each plot, with the height recorded as the tallest overall part of the plant. Tiller numbers were also determined biweekly in 2011 and 2012 in three 50 × 50 cm quadrats placed randomly in each plot. Tiller counts were continued until tiller dies down at the beginning of the transition to dormancy at the end of each growing season. Phenology stages were determined based on sampling 10 plants at random from each plot and was scored based on the mean stage count (MSC) as described by Moore et al. [34]. Big bluestem selections were not included in tiller counts and were measured for height once at the end of the growing season.All plots were harvested in the fall after a first frost using a flail-type forage harvester with a cutting surface of 0.6 × 5 m and a cutting height of 7 cm. The harvest dates for 2011 and 2012 were November 1 and October 23 in Sainte-Anne-de-Bellevue and October 24 and October 17 in Cookshire-Eaton, respectively. In addition, the selections from “Cave-in-Rock” switchgrass and “Prairie View Indiana” big bluestem were also harvested in the spring to determine yield differences related to harvest time. The 2012 spring harvest dates were April 19 and April 30 in Sainte-Anne-de-Bellevue and Cookshire-Eaton, respectively. All harvested biomass was weighed and subsamples of approximately 500 g were collected from each plot to determine biomass yield on a dry matter basis. These subsamples were also used to determine the moisture, ash, fiber, and energy concentration of the harvested biomass for selections that were harvested both in the fall and in the spring.


### 2.3. Laboratory Analyses

Subsamples taken from each plot were dried for 48 hours at 60°C and then reweighed to determine moisture concentration [35] (method number 934.01). Dry samples were then ground with a Model 4 Thomas-Wiley Laboratory Mill forage grinder (Thomas Scientific, Swedesboro, NJ, USA) to pass through a 1 mm screen. The ash fraction was determined using a Thermolyne (Dubuque, IA, USA) muffle furnace [35] (method number 924.05). Ground samples were analyzed for neutral (NDF) and acid (ADF) detergent fiber using an Ankom Fiber Analyzer (Ankom Technology Corporation, Macedon, NY, USA) by incubating the samples in neutral [35] and acid detergent solutions [35] (method number 9738.18), respectively. Acid digestible lignin (ADL) was determined by washing ADF residues with 20 N H2SO4 [35] (method number 9738.18). From the results of these analyses cellulose, hemicellulose, and lignin concentrations were calculated (hemicellulose = NDF − ADF, cellulose = ADF − ADL, and lignin = ADL − mineral ash) [36]. Energy concentration was determined using a Parr adiabatic bomb calorimeter (Parr Oxygen Bomb Model 1341EB, Calorimeter Thermometer Model 6772, Parr Instrument Company, Moline, IL, USA) to calculate higher heating value (HHV).


### 2.4. Statistical Analyses

The experiment design used at both sites was a randomized complete block design with four replications. All data were analyzed using the GLM procedure of the SAS statistical software program [37]. Data were analyzed separately for each environment due to differences in sampling time and sampling numbers. Replicates were considered random effects and treatments (i.e., selections or harvest time (fall versus spring)) were considered fixed. Unless otherwise noted, tests were considered significant at the 5% probability level. Comparisons between means were made using LSD when ANOVAs indicated significant model and treatment effects. Only significant results are discussed in the text unless otherwise noted.


## 2.1. Plant Materials

Selection lines and parent material were supplied by REAP-Canada, based in Southern Quebec (Sainte-Anne-de-Bellevue, QC, Canada). The biomass breeding program is utilizing short breeding cycles incorporating selection at the seedling stage followed by recurrent restricted phenotypic selection (RRPS) in mature spaced-plant nurseries [32]. A total of 11 upland switchgrass selections and three big bluestem selections were evaluated. These included three switchgrass parent varieties and seven selections derived from these (Table 1). “Sandlover,” a selection made by REAP-Canada from “NU-94-2” [15], was also evaluated bringing the total switchgrass selections evaluated to eleven. In addition, two selections of big bluestem were also evaluated alongside their parent material “Prairie View Indiana germplasm”.Table 1
Origins of the commercial switchgrass and big bluestem varieties evaluated in the present study and the selections derived from them through a local selection programme in Southern Quebec.
Variety/selection
Year of release
Site of origin
Latitude of origin (°N)
References
Switchgrass
Cave-in-Rock
1958
Cave-in-Rock, Illinois
37
Jefferson and McCaughey, 2012 [6]
Cave-in-Rock II
N/A
Valleyfield, Quebec
Present study
Cave-in-Rock Early
N/A
Valleyfield, Quebec
Present study
Summer
1953
Nebraska City, Nebraska
41
Jefferson and McCaughey, 2012 [6]
Tecumseh
N/A
Valleyfield, Quebec
Present study
Tecumseh II
N/A
Valleyfield, Quebec
Present study
Sunburst
1998
Union County, South Dakota
43
Jefferson and McCaughey, 2012 [6]
Blue Jacket
N/A
Valleyfield, Quebec
Present study
Blue Jacket II
N/A
Valleyfield, Quebec
Present study
Blue Jacket Early
N/A
Valleyfield, Quebec
Present study
Sandlover
2009
Northern Nebraska
36–40
Vermerris, 2008 [15]
Big bluestem
Prairie view
1994
20 sites across Indiana
38–41
Samson et al., 2014 [32]
Prairie view II
N/A
Valleyfield, Quebec
Present study
Prairie view Early
N/A
Valleyfield, Quebec
Present studyThe “Blue Jacket” and “Blue Jacket II” switchgrass selections were made from “Sunburst” switchgrass using RRPS [33]. The population of “Blue Jacket II” was selected for reduced tillering at the seedling stage, with 200 superior plants selected from a population of 1000 plants [22] followed by a RRPS selection made on mature plants. The “Blue Jacket Early” selection was derived from 50 plants which exhibited early spring growth in the year after establishment in a one ha seed field of “Blue Jacket” switchgrass in Valleyfield, Quebec. The plants were dug up in the spring of 2008 and replanted and seed was collected from the population in the fall of 2009.“Cave-in-Rock II” was derived from a seed collection in the fall of 2006 from 30 superior plants in an eight-year-old switchgrass field in Valleyfield, Quebec. The population was subsequently selected for reduced tillering at the seedling stage were transplanted in the field [22]. At the mature plant stage, the population was selected using RRPS and seed derived from superior plants from a 200-spaced-plant nursery was collected in fall 2009. The “Cave-in-Rock Early” population was derived from seed collected in fall of 2009 from 30 early maturing switchgrass plants in a 10-year-old field of “Cave-in-Rock” switchgrass in Valleyfield, Quebec.The “Tecumseh” and “Tecumseh II” selections were made from “Summer” switchgrass using RRPS [33]. A greenhouse population of 1000 plants of “Tecumseh II” was selected for reduced tillering at the seedling stage [22]. At the mature plant stage, the population was selected using RRPS and seed derived from superior plants from the 200-spaced-plant nursery was collected in fall of 2009.“Sandlover” was derived from 200 plants selected from a 1,000-spaced-plant nursery in Valleyfield, Quebec, using RRPS [33]. The original source population was Northern Upland “NU-942” obtained from Charles Taliaferro at the University of Oklahoma in 2006.Finally, the selections “Prairie View Early” and “Prairie View II” were selected from an 800-spaced-plant nursery of Prairie View Indiana germplasm big bluestem originally transplanted in 2008 in Valleyfield, Quebec.


## 2.2. Field Management and Data Collection

Plots were arranged in a randomized complete block design with four replications at two sites in Southern Quebec, Sainte-Anne-de-Bellevue (45°25′32.45′′N, 73°55′48.63′′W, 37 m elevation) and Cookshire-Eaton (45°20′57.49′′N, 71°47′08.40′′W, 243 m elevation). Plot size was 4 × 5 m in Sainte-Anne-de-Bellevue and 2.4 × 5 m in Cookshire-Eaton. The soil at the Sainte-Anne-de-Bellevue site was a free-draining St. Bernard sandy clay loam, while the Cookshire-Eaton site was an imperfectly drained Magog stony loam. All selections of both species were seeded in spring 2010 using a Fabro precision planter (Fabro Enterprises, Swift Current, SK, Canada) with an 18 cm row spacing. The seeding rate used for all selections was 300 pure live seeds (PLS) m−2. Nitrogen was applied at both sites as urea at a rate of 50 kg N ha−1 in May of 2011 and 2012; no other fertilization was done.Plant height was determined in each plot biweekly from May to September in 2011 and 2012. The height of 10 plants was measured in each of three subplots selected at random within each plot, with the height recorded as the tallest overall part of the plant. Tiller numbers were also determined biweekly in 2011 and 2012 in three 50 × 50 cm quadrats placed randomly in each plot. Tiller counts were continued until tiller dies down at the beginning of the transition to dormancy at the end of each growing season. Phenology stages were determined based on sampling 10 plants at random from each plot and was scored based on the mean stage count (MSC) as described by Moore et al. [34]. Big bluestem selections were not included in tiller counts and were measured for height once at the end of the growing season.All plots were harvested in the fall after a first frost using a flail-type forage harvester with a cutting surface of 0.6 × 5 m and a cutting height of 7 cm. The harvest dates for 2011 and 2012 were November 1 and October 23 in Sainte-Anne-de-Bellevue and October 24 and October 17 in Cookshire-Eaton, respectively. In addition, the selections from “Cave-in-Rock” switchgrass and “Prairie View Indiana” big bluestem were also harvested in the spring to determine yield differences related to harvest time. The 2012 spring harvest dates were April 19 and April 30 in Sainte-Anne-de-Bellevue and Cookshire-Eaton, respectively. All harvested biomass was weighed and subsamples of approximately 500 g were collected from each plot to determine biomass yield on a dry matter basis. These subsamples were also used to determine the moisture, ash, fiber, and energy concentration of the harvested biomass for selections that were harvested both in the fall and in the spring.


## 2.3. Laboratory Analyses

Subsamples taken from each plot were dried for 48 hours at 60°C and then reweighed to determine moisture concentration [35] (method number 934.01). Dry samples were then ground with a Model 4 Thomas-Wiley Laboratory Mill forage grinder (Thomas Scientific, Swedesboro, NJ, USA) to pass through a 1 mm screen. The ash fraction was determined using a Thermolyne (Dubuque, IA, USA) muffle furnace [35] (method number 924.05). Ground samples were analyzed for neutral (NDF) and acid (ADF) detergent fiber using an Ankom Fiber Analyzer (Ankom Technology Corporation, Macedon, NY, USA) by incubating the samples in neutral [35] and acid detergent solutions [35] (method number 9738.18), respectively. Acid digestible lignin (ADL) was determined by washing ADF residues with 20 N H2SO4 [35] (method number 9738.18). From the results of these analyses cellulose, hemicellulose, and lignin concentrations were calculated (hemicellulose = NDF − ADF, cellulose = ADF − ADL, and lignin = ADL − mineral ash) [36]. Energy concentration was determined using a Parr adiabatic bomb calorimeter (Parr Oxygen Bomb Model 1341EB, Calorimeter Thermometer Model 6772, Parr Instrument Company, Moline, IL, USA) to calculate higher heating value (HHV).


## 2.4. Statistical Analyses

The experiment design used at both sites was a randomized complete block design with four replications. All data were analyzed using the GLM procedure of the SAS statistical software program [37]. Data were analyzed separately for each environment due to differences in sampling time and sampling numbers. Replicates were considered random effects and treatments (i.e., selections or harvest time (fall versus spring)) were considered fixed. Unless otherwise noted, tests were considered significant at the 5% probability level. Comparisons between means were made using LSD when ANOVAs indicated significant model and treatment effects. Only significant results are discussed in the text unless otherwise noted.


## 3. Results and Discussion

### 3.1. Biomass Yield

Switchgrass biomass yield across selections, years, and sites averaged 7.2 Mg ha−1 with individual site-year averages ranging between 3.8 and 9.9 Mg ha−1 (Table 2). Large differences were observed between sites, with yields averaging 4.9 and 9.5 Mg ha−1 across years in Cookshire-Eaton and Sainte-Anne-de-Bellevue, respectively. Yields of all selections were greater in Sainte-Anne-de-Bellevue than in Cookshire-Eaton, although differences in the ranking of selections varied at the two sites. Overall much lower yields were observed in Cookshire-Eaton which may have been due to several environmental factors. The Cookshire-Eaton site is less productive as it is at a higher elevation and has a heavier, imperfectly drained soil. It also suffered more intense perennial weed pressure as compared to the Sainte-Anne-de-Bellevue site. The switchgrass and especially the big bluestem appeared to take longer to become established at the Cookshire-Eaton site. The mean switchgrass yield at Sainte-Anne-de-Bellevue increased by 10% in year 2 while the mean switchgrass yield at Cookshire Eaton increased by 58% in year 2. Mean big bluestem yields increased by 34% and 294% in year 2 at the Sainte-Anne-de-Bellevue and Cookshire-Eaton sites, respectively. Overall it appeared that yields are not optimized for switchgrass until the second production year with most selections on productive sites. In the case of switchgrass and especially big bluestem on more marginal sites it may take until year three for the stands to become fully productive as very large increases were experienced in year 2. Amongst the switchgrass accessions tested “Blue Jacket II” appeared to establish very well and had similar yields in both the first and the second year at both sites. This may have been a result of Blue Jacket II’s larger seed size [32, 38] and relatively early maturity. These characteristics may allow it to more fully complete its growth cycle in the establishment year. Switchgrass usually reaches 33–66% of its yield potential in the first production year, while the second production year is generally indicative of long-term biomass yield potential [21]. Overall it appeared that, in the case of a productive site in southern Quebec, a large seeded upland cultivar selected for improved establishment could achieve near full productivity in the first production year. In the case of big bluestem on a marginal site, as little as 1/4 of the productive potential may be achieved in the first production year.Table 2
Yield on dry matter basis of 11 selections of switchgrass and 3 selections of big bluestem seeded in 2010 and harvested in fall of 2011 and 2012 at two sites in Southern Quebec (in Mg ha−1).
Entry
Sainte-Anne-de-Bellevue
Cookshire-Eaton
2011
2012
2011
2012
Switchgrass
Sunburst
7.7
9.1
3.6
5.6
Blue Jacket
9.0
9.1
4.2
4.8
Blue Jacket II
9.7
9.1
5.0
5.3
Blue Jacket Early
8.1
9.1
3.6
4.7
Summer
9.2
11.2
4.9
6.8
Tecumseh
8.2
10.4
2.1
4.2
Tecumseh II
9.3
10.3
4.6
6.7
Cave-in-Rock
10.0
10.3
3.5
7.3
Cave-in-Rock II
10.2
11.1
5.9
9.0
Cave-in-Rock Early
8.8
9.9
2.5
6.4
Sandlover
9.3
9.7
1.6
5.3
Switchgrass mean
9.0
9.9
3.8
6.0
Big Bluestem
Prairie view
6.0
7.5
2.1
5.1
Prairie view II
5.6
8.8
1.9
5.6
Prairie view Early
6.6
8.4
1.6
6.1
Big bluestem mean
6.1
8.2
1.9
5.6
Overall mean
8.4
9.6
3.4
5.9
P value
<0.0001
0.0046
<0.0001
0.0004
LSD (5%)
1.1
1.7
1.4
1.6Variation in switchgrass biomass yield across sites, varieties, and fertilizer regimes has previously been reported [39–42], with a recent meta-analysis reporting a mean yield of 8.7±4.2 Mg ha−1 over 39 trials conducted across the United States [43]. Jannasch et al. [44] reported an average plot yield of 9.2 Mg ha−1 for switchgrass in Southern Quebec, while average yields of 7.0 and 9.0 Mg ha−1 were reported in Minnesota [45] and Iowa [39], respectively.Big bluestem biomass yields averaged 5.5 Mg ha−1 across all selections, sites, and years and were more variable than switchgrass, with values ranging between 1.9 and 8.2 Mg ha−1 in individual site-years. Previous experiences have suggested that big bluestem may not reach its maximum yield potential until 3-4 years after seeding [15], a result supported by the large increases in yield and plant height observed between years in the present study.Differences in switchgrass biomass yield were also observed between selections. Overall yields followed similar patterns as previous studies with early maturing cultivars generally being lower yielding selections than later maturing selections [46] (Table 2). However, higher yields for some of the most recent selections were observed when compared to the original parent materials. For example “Cave-in-Rock II” outyielded Cave-in-Rock in both years at Cookshire-Eaton, while “Blue Jacket II” outyielded “Sunburst” at both sites in 2011. In the case of Tecumseh II there were no significant differences in yield with “Summer” switchgrass observed. “Summer” is known to be a relatively high producing cultivar for its maturity class and breeding progress may be more difficult to achieve. The “Cave-in-Rock II” selection overall appeared to be amongst the most productive selections across sites and years. “Cave-in-Rock” selections generally performed at least as well as or better than the other selections tested, confirming the results of other studies which have found “Cave-in-Rock” to be well adapted and high yielding in Southern Quebec [47].Some selections from the “Sunburst” variety performed poorly in Cookshire-Eaton and in both 2011 and 2012 significantly higher stem rust (Puccinia spp.) incidence was noted on those selections relative to all other selections in the study (data not shown). Stem rust infections are the most common disease reported in switchgrass and may cause significant damage including stunting, early flowering, and reduced yield [39]. The prevalence of rust infections on all “Cave-in-Rock” selections was extremely low, as seen in previous research [48]. Gustafson et al. [49] evaluated the genetic variation in resistance to rust disease in switchgrass populations including “Summer,” “Sunburst,” and “Cave-in-Rock.” “Sunburst” had the highest susceptibility to rust, while “Cave-in-Rock,” having evolved under heavy rust pressure in humid Southern Illinois, was the least susceptible.


### 3.2. Tiller Density

Significant differences in tiller number were observed among selections at all measurement points in both years at Sainte-Anne-de-Bellevue (Figure1). At the first measurement period (early June in 2011 and late May in 2012), the mean tiller density per square meter across all entries was 906 in 2011 and increased to 1033 in 2012, with “Sunburst” producing the most tillers m−2 in both years (1307 in 2011 and 1375 in 2012). Low tiller counts were observed on “Tecumseh” and “Sandlover” switchgrass in 2011 as the plots had relatively thin plant stands. Due to the large variability between plots, the significant differences observed were often between selection lineages and not between selections within a lineage. By the end of August, tiller density in Sainte-Anne-de-Bellevue had decreased to 674 and 706 tillers per square meter in 2011 and 2012, respectively, representing average decreases of 22% and 30%, respectively. The magnitude of the decrease varied considerably depending on the selection lineage. The average decrease in tiller density throughout the season across both years was 38% for “Sunburst” selections, 26% for “Cave-in-Rock” selections, and 19% for “Summer” selections, while no decrease was observed for “Sandlover” which had a thin stand. All selections from the “Sunburst” lineage displayed reduced tillering early in the season. The variable degree of tiller loss across selections ultimately had an equalizing effect on tiller density between all selections.Number of tillers m−2 of 11 selections of switchgrass at Sainte-Anne-de-Bellevue, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD, P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)In Cookshire-Eaton stands were considerably thinner and more variable, but significant differences were still observed between selections at all measurement periods (Figure2). At both sites differences between selections were much larger at the beginning of the season, with only stands with the highest initial density self-thinning throughout the season. However, due to the thinner stands at Cookshire-Eaton tiller mortality during the season was greatly reduced. In 2011, the low initial tiller density in Cookshire-Eaton resulted in no significant decrease over the course of the season with mean tiller number across all selections decreasing from 360 to 324 tillers m−2. In 2012 all stands had higher initial tiller density and a correspondingly greater decrease from 522 to 434 tillers m−2, an average decrease of 14% over the season. Once stands had more fully established at the Cookshire-Eaton site in 2012, trends in average tiller decrease also began to align more closely with those seen at Sainte-Anne-de-Bellevue with an average decrease of 25% for “Sunburst” selections, 21% for “Cave-in-Rock” selections, and 11% for “Summer” selections, while “Sandlover” did not decrease at all due to a thin stand.Number of tillers m−2 of 11 selections of switchgrass at Cookshire-Eaton, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD, P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II, CIR; Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)High tiller mortality as the growing season progresses is common in grasses, with crops such as ryegrass losing 60% of their tillers [50]. The large majority of these are small vegetative tillers which senesce in the sward after being shaded out by the larger reproductive tillers. In perennial grasses such as switchgrass high vegetative tiller production occurs in the spring with subsequent mortality throughout the season [51].The results of the present study support previous findings that indicate that there is likely an optimal tiller density for efficient capture of solar radiation which swards target through increased vegetative tiller production or self-thinning. This optimum is known as tiller equilibrium density [23]. Madakadze et al. [52] found that populations of switchgrass had differing leaf area indices associated with various heights of their canopy. The authors also found that leaf angle and leaf area index varied by variety, indicating that different populations have different canopy structures. The variability in tiller mortality among selections in the present study may indicate that tiller plasticity also plays a large role in this variability. Boe and Casler [13] reported a large degree of plasticity in tiller morphology within populations. In the present study this plasticity seemed to allow tiller density across many selections to converge towards equilibrium density. “Sunburst” had the highest initial density and displayed >40% tiller mortality over the season (Figures 1 and 2), while conversely “Sandlover,” the selection with the lowest initial tiller density, did not display any tiller mortality on average.A trend was also noted for differences in decrease between selections when compared to their parent variety, appearing to often be due to lower initial tiller density in the selections at the beginning of the season. Redfearn et al. [48] examined tiller density in switchgrass plots in Iowa and Nebraska managed for forage and found G × E interactions to be present for both yield and tiller density, with “Cave-in-Rock” producing the lowest tiller number but highest forage yield. The authors noted that tiller density differed with location, even between selections from the same base population. In the present study at Sainte-Anne-de-Bellevue average tiller mortality over both years was 10% lower in “Blue Jacket II” than in “Sunburst” and 13% lower in “Cave-in-Rock II” than in the “Cave-in-Rock” base population. However, there was an average increase in tiller loss in the “Summer” lineage, with mortality on average 16% higher in “Tecumseh II” than in “Summer.” This was likely due to “Tecumseh II” establishing more quickly and having a higher initial density than “Summer” in 2011. In 2012 the “Summer” population was more fully established and there was no significant difference between the two. These trends suggest progress in modification of tillering among the selection lineages where populations were well established.


### 3.3. Height

Significant differences were observed between the heights of selections at all periods observed throughout all site-years (Figures3 and 4); however, trends varied by site. The trends observed were generally supported by previous studies which have indicated that later maturing varieties produce taller tillers due to their slower rates of leaf appearance [53]. “Cave-in-Rock II” was significantly taller than the other selections in its lineage at both sites in 2012, reaching an average of 201 cm in Sainte-Anne-de-Bellevue. Over all site-years this represented an average increase of 12 cm or 7% over the parent variety. The “Cave-in-Rock” selections were the tallest three recorded in 2012 at Cookshire-Eaton. In 2012 the relatively early maturing “Tecumseh” and “Tecumseh II” selections performed very well in Sainte-Anne-de-Bellevue, attaining the second and third highest average heights; however, there was no significant increase in height over the parent variety “Summer.”Height of 11 selections of switchgrass at Sainte-Anne-de-Bellevue, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD,P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)Height of 11 selections of switchgrass at Cookshire-Eaton, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD,P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)No meaningful height differences were observed among big bluestem selections (data not shown); however, there was a significant increase in height in the second year at both sites. This result is consistent with the slower establishment in big bluestem. Average height increased from 144 to 192 cm (33%) at the Cookshire-Eaton site and from 194 to 216 cm (11%) at Sainte-Anne-de-Bellevue in 2011 and 2012, respectively.


### 3.4. Maturity

There were significant differences observed in phenological development at both sites for all measurement periods (Figures5 and 6). The differences observed were almost exclusively between selections in different selection lineages and not within a lineage. The “Sunburst” selections displayed the earliest maturity, followed by the “Summer” selections, with the “Cave-in-Rock” and “Sandlover” selections displaying the latest maturity. These findings are supported by recent literature linking latitude of origin with maturity [46, 54]. The latitudes of origin of the selections in this study rank in the same order as the maturity observed (Table 1). The moisture concentration of the selections at harvest also mirrored this pattern, with significant differences observed between selections related to maturity at harvest (Table 3). No significant moisture differences were observed between selections from a same parent variety.Table 3
Moisture concentration (%) at fall harvest of 11 selections of switchgrass and 3 selections of big bluestem at two sites in Southern Quebec.
Entry
Sainte-Anne-de-Bellevue
Cookshire-Eaton
2011
2012
2011
2012
Switchgrass
Sunburst
36.8
34.1
33.8
27.6
Blue Jacket
36.1
33.8
31.6
31.8
Blue Jacket II
35.5
35.4
32.7
30.1
Blue Jacket Early
38.1
35.2
30.1
28.0
Summer
39.7
31.9
26.1
24.4
Tecumseh
37.7
35.8
37.5
29.3
Tecumseh II
40.3
34.3
31.4
20.2
Cave-in-Rock
46.1
41.0
43.6
29.8
Cave-in-Rock II
45.8
44.5
44.9
39.6
Cave-in-Rock Early
44.1
41.8
35.5
31.6
Sandlover
49.1
44.5
38.7
34.8
Switchgrass mean
40.8
37.5
35.1
29.7
Big Bluestem
Prairie view
43.7
39.6
44.3
38.9
Prairie view II
46.8
41.0
35.6
30.9
Prairie view Early
43.8
39.0
44.0
33.7
Big bluestem mean
44.8
39.9
41.3
34.5
Overall mean
41.7
38.0
36.4
30.8
P value
<0.0001
<0.0001
0.0002
0.0023
LSD (5%)
3.3
3.2
7.9
7.6Mean stage count of 11 selections of switchgrass at Sainte-Anne-de-Bellevue, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD,P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)Mean stage count of 11 selections of switchgrass at Cookshire-Eaton, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD,P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)


### 3.5. Effects of Harvest Date on Biomass Yield and Quality Variables

Differences were observed at both sites for some selections between fall and spring harvest dates for yield, moisture concentration, and cellulose concentration (Tables4 and 5). The Sainte-Anne-de-Bellevue spring harvest resulted in an overall 41% yield reduction compared to a fall harvest. In Cookshire-Eaton a spring harvest only reduced yield in the highest-yielding selection, “Cave-in-Rock II”, which had an average loss of 56%. Reductions of up to 40% in biomass yield have also been reported in Pennsylvania, where this yield loss was attributed to the loss of panicles and leaves, the leaching of stem components such as minerals and cell solubles [27], and the translocation of mobile nutrients and N-rich compounds into underground perennial structures, a process which may continue into December [3]. These processes have also been shown to decrease the ash fraction in the spring [27, 28]. In the present study no differences were observed between ash concentrations of spring versus fall harvested material (Tables 4 and 5). This lack of change in ash concentration may have been due to soil contamination from the grasses overwintering on the site in a lodged state. Current best management practice by farmers in Eastern Canada is to mow the grasses in late fall and to bale the biomass in spring. This system helps to reduce biomass losses by minimizing the breakage of the leaves and seed heads resulting from wind and snow exposure in material standing over winter [55]. Small plot studies may, therefore, overestimate yield losses compared to an on-farm spring harvest regime. In this study the yield and quality comparisons of the fall and spring material were only made on first production year (2nd year after seeding) material, which had not yet reached full establishment at the marginal site.Table 4
Fall 2011 and spring 2012 values on dry matter basis for yield, moisture concentration, cell wall components, ash, and higher heating value (HHV) of three selections of switchgrass and three selections of big bluestem in Sainte-Anne-de-Bellevue, Quebec.
Entry
CIR
CIR2
CIRE
PV
PV2
PVE
P value
LSD
Moisture (%)
Fall
46.1
45.8
44.1
43.7
46.8
43.8
0.1843
3.076
Spring
11.2
14
10.6
10.7
11.5
10.9
0.326
3.411
% change†
−75.7
−69.4
−76
−75.4
−75.4
−75.1
P value
0.0001
<0.0001
0.0002
<0.0001
0.0002
0.0002
LSD
4.209
2.812
4.925
3.737
4.706
4.2826
Yield (Mg ha−1)
Fall
10
10.2
8.8
6
5.6
6.6
<0.0001
1.202
Spring
6.2
6.1
6.6
3.8
2.8
3
<0.0001
1.518
% change†
−38.3
−40.4
−25.2
−37.9
−49.5
−55.1
P value
0.0052
0.0102
0.0493
0.053
0.0018
0.0034
LSD
1.67
2.253
2.205
2.341
0.8374
1.3616
Cellulose (g kg−1)
Fall
419
414
389
439
431
438
0.0056
25.05
Spring
456
438
429
476
449
447
0.001
17.59
% change†
8.8
5.6
10.4
8.3
4.2
2.1
P value
0.0654
0.0004
0.0042
0.029
0.1361
0.0143
LSD
41.2
4.227
16.29
29.42
28.491
5.676
Hemicellulose (g kg−1)
Fall
315
321
324
316
303
300
0.0593
17.42
Spring
324
336
340
291
313
307
0.0005
18.97
% change†
2.9
4.7
4.9
−7.9
3.3
2.3
P value
0.457
0.2528
0.0061
0.056
0.209
0.1208
LSD
34.56
35.1
7.173
26.219
20.403
10.329
Lignin (g kg−1)
Fall
77
69
65.5
60.1
62.9
63.1
0.2727
14.94
Spring
90.3
73.5
64.5
79.3
63.7
67.9
<0.0001
8.647
% change†
17.3
6.5
−1.5
31.9
1.3
7.6
P value
0.2283
0.3488
0.8434
0.0094
0.8919
0.2655
LSD
28.093
12.857
14.786
9.9
16.149
11.246
Ash (g kg−1)
Fall
45.2
48.9
47.4
48.2
49.1
46.3
0.9689
11.14
Spring
50.4
53.2
50.8
48.3
50.3
55.5
0.9601
17.25
% change†
11.5
8.8
7.2
0.2
2.4
19.9
P value
0.5503
0.4563
0.2225
0.9562
0.7607
0.1186
LSD
24.9
16.041
6.897
9.329
11.929
13.538
HHV (MJ kg−1)
Fall
18.71
18.96
18.78
18.73
19
18.94
0.5896
0.4463
Spring
18.96
18.99
18.73
18.85
18.88
18.92
0.761
0.399
% change†
1.3
0.2
−0.3
0.6
−0.6
−0.1
P value
0.4213
0.8845
0.7915
0.4774
0.4568
0.9009
LSD
0.887
0.5706
0.5966
0.4781
0.46
0.4408
†Percent change relative to fall value.
CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early; PV, Prairie view; PV2, Prairie view II; PVE, Prairie view Early.Table 5
Fall of 2011 and spring of 2012 values on dry matter basis for yield, moisture concentration, cell wall components, ash, and higher heating value (HHV) of three selections of switchgrass and three selections of big bluestem in Cookshire-Eaton, Quebec.
Entry
CIR
CIR2
CIRE
PV
PV2
PVE
P value
LSD
Moisture (%)
Fall
43.6
44.9
35.5
44.3
35.6
43.9
0.0962
8.8360
Spring
8.5
8.8
7.3
% change†
−80.4
−80.3
−79.5
P value
0.0007
0.001
0.0106
LSD
3.8578
4.8707
12.587
Yield (Mg ha−1)
Fall
3.5
5.9
2.5
2.1
1.9
1.6
0.0002
1.2830
Spring
2.6
2.6
2.3
0.0
0.0
0.0
% change†
−26.2
−56.3
−8.5
−100.0
−100.0
−100.0
P value
0.2539
0.0188
0.6558
LSD
2.5201
1.9826
1.7471
Cellulose (g kg−1)
Fall
415
396
376
385
381
371
0.2719
40.852
Spring
445
454
415
0.001
10.307
% change†
7.2
14.7
10.3
P value
0.3218
0.1236
0.0132
LSD
98.893
97.169
19.321
Hemicellulose (g kg−1)
Fall
352
317
339
316
301
290
0.0088
29.914
Spring
345
304
333
0.0001
6.325
% change†
−1.7
−4.0
−1.7
P value
0.3591
0.2353
0.2808
LSD
22.334
32.475
17.053
Lignin (g kg−1)
Fall
73
77
61
55
70
66
0.1155
16.628
Spring
72
89
63
0.0009
6.488
% change†
−0.5
16.2
3.4
P value
0.9687
0.3272
0.5228
LSD
34.118
41.443
11.684
Ash (g kg−1)
Fall
39
48
45
45
46
45
0.6675
11.274
Spring
33
30
32
0.0179
1.539
% change†
−17.5
−38.0
−30.2
P value
0.1626
0.0725
0.0625
LSD
13.665
22.343
15.498
HHV (MJ kg−1)
Fall
19.15
19.09
19.31
19.22
19.20
19.27
0.7519
3.452
Spring
19.35
19.36
19.25
0.6191
3.264
% change†
1.0
1.4
−0.3
P value
0.158
0.4399
0.2681
LSD
0.387
1.2138
0.1836
†Percent change relative to fall value.
CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early; PV, Prairie view; PV2, Prairie view II; PVE, Prairie view Early.The decrease in moisture concentration in the spring biomass compared to the fall averaged 74% across selections and sites, falling from 45% to 11% moisture concentration (Table4). The high fall moisture values for “Cave-in-Rock” selections are a result of its late maturity and high biomass production. Plant materials are difficult to dry in the short, cool, and high humidity days in Eastern Canada in the late fall [31]. The calorific value for combustion of herbaceous biomass declines linearly with rising moisture concentration, making this an important measure for certain applications [56]. Drying can also take place in covered storage, with fall-baled material at 16-17% moisture declining to 12–14% by the following spring [31].The cell walls of grasses contain cellulose, hemicellulose, lignin, and other compounds including p-coumaric, phenolic, and ferulic acids [26, 57]. The increase in cellulose concentration for some selections at both sites (Tables 4 and 5) is likely related to increased stem fraction combined with an overall reduction of mineral and cell soluble concentrations in overwintered materials. Whole plant big bluestem tended to have slightly higher cellulose and lower hemicellulose concentrations than switchgrass, again likely due to increased stem fraction in the big bluestem. Overwintering generally had a tendency to increase concentration of cellulose in both switchgrass and big bluestem. If big bluestem genetics can be improved to produce similar yields to switchgrass it could be a promising species where high cellulose content biomass feedstocks are required for markets such as bioethanol production and biofibre applications. For lignin there were no trends evident between species or selections. Overall big bluestem appeared to have a higher cellulose to hemicellulose ratio than upland switchgrass. This could be of interest for specialty applications requiring high cellulose content feedstocks.There were no differences in HHV observed between selections or between harvest dates, with Sainte-Anne-de-Bellevue and Cookshire-Eaton averaging 18.9 and 19.3 kJ g−1, respectively, over both harvest times. A previous analysis of four varieties of fall-harvested switchgrass determined an average energy concentration of 18.8±0.2 kJ g−1 with no significant differences between varieties [58], while Madakadze et al. [52] reported a lower energy yield of 17.4 kJ g−1 for “Cave-in-Rock” harvested in the fall in Southern Quebec.Turn et al. [59] have indicated that the leaching process that often occurs in the winter increases HHV in herbaceous biomass through removal of inorganic constituents. However, in the present study harvest time had no effect on HHV. Experiences with spring harvested reed canary grass (Phalaris arundinacea L.) in Sweden demonstrated significant reductions in Cl, K, S, alkali, ash, and several other important quality factors but curiously also a decrease in HHV [28]. The authors also noted large variation in HHV and ash concentration related to soil type, with clay soils having much lower values than humus rich or sandy soils.


## 3.1. Biomass Yield

Switchgrass biomass yield across selections, years, and sites averaged 7.2 Mg ha−1 with individual site-year averages ranging between 3.8 and 9.9 Mg ha−1 (Table 2). Large differences were observed between sites, with yields averaging 4.9 and 9.5 Mg ha−1 across years in Cookshire-Eaton and Sainte-Anne-de-Bellevue, respectively. Yields of all selections were greater in Sainte-Anne-de-Bellevue than in Cookshire-Eaton, although differences in the ranking of selections varied at the two sites. Overall much lower yields were observed in Cookshire-Eaton which may have been due to several environmental factors. The Cookshire-Eaton site is less productive as it is at a higher elevation and has a heavier, imperfectly drained soil. It also suffered more intense perennial weed pressure as compared to the Sainte-Anne-de-Bellevue site. The switchgrass and especially the big bluestem appeared to take longer to become established at the Cookshire-Eaton site. The mean switchgrass yield at Sainte-Anne-de-Bellevue increased by 10% in year 2 while the mean switchgrass yield at Cookshire Eaton increased by 58% in year 2. Mean big bluestem yields increased by 34% and 294% in year 2 at the Sainte-Anne-de-Bellevue and Cookshire-Eaton sites, respectively. Overall it appeared that yields are not optimized for switchgrass until the second production year with most selections on productive sites. In the case of switchgrass and especially big bluestem on more marginal sites it may take until year three for the stands to become fully productive as very large increases were experienced in year 2. Amongst the switchgrass accessions tested “Blue Jacket II” appeared to establish very well and had similar yields in both the first and the second year at both sites. This may have been a result of Blue Jacket II’s larger seed size [32, 38] and relatively early maturity. These characteristics may allow it to more fully complete its growth cycle in the establishment year. Switchgrass usually reaches 33–66% of its yield potential in the first production year, while the second production year is generally indicative of long-term biomass yield potential [21]. Overall it appeared that, in the case of a productive site in southern Quebec, a large seeded upland cultivar selected for improved establishment could achieve near full productivity in the first production year. In the case of big bluestem on a marginal site, as little as 1/4 of the productive potential may be achieved in the first production year.Table 2
Yield on dry matter basis of 11 selections of switchgrass and 3 selections of big bluestem seeded in 2010 and harvested in fall of 2011 and 2012 at two sites in Southern Quebec (in Mg ha−1).
Entry
Sainte-Anne-de-Bellevue
Cookshire-Eaton
2011
2012
2011
2012
Switchgrass
Sunburst
7.7
9.1
3.6
5.6
Blue Jacket
9.0
9.1
4.2
4.8
Blue Jacket II
9.7
9.1
5.0
5.3
Blue Jacket Early
8.1
9.1
3.6
4.7
Summer
9.2
11.2
4.9
6.8
Tecumseh
8.2
10.4
2.1
4.2
Tecumseh II
9.3
10.3
4.6
6.7
Cave-in-Rock
10.0
10.3
3.5
7.3
Cave-in-Rock II
10.2
11.1
5.9
9.0
Cave-in-Rock Early
8.8
9.9
2.5
6.4
Sandlover
9.3
9.7
1.6
5.3
Switchgrass mean
9.0
9.9
3.8
6.0
Big Bluestem
Prairie view
6.0
7.5
2.1
5.1
Prairie view II
5.6
8.8
1.9
5.6
Prairie view Early
6.6
8.4
1.6
6.1
Big bluestem mean
6.1
8.2
1.9
5.6
Overall mean
8.4
9.6
3.4
5.9
P value
<0.0001
0.0046
<0.0001
0.0004
LSD (5%)
1.1
1.7
1.4
1.6Variation in switchgrass biomass yield across sites, varieties, and fertilizer regimes has previously been reported [39–42], with a recent meta-analysis reporting a mean yield of 8.7±4.2 Mg ha−1 over 39 trials conducted across the United States [43]. Jannasch et al. [44] reported an average plot yield of 9.2 Mg ha−1 for switchgrass in Southern Quebec, while average yields of 7.0 and 9.0 Mg ha−1 were reported in Minnesota [45] and Iowa [39], respectively.Big bluestem biomass yields averaged 5.5 Mg ha−1 across all selections, sites, and years and were more variable than switchgrass, with values ranging between 1.9 and 8.2 Mg ha−1 in individual site-years. Previous experiences have suggested that big bluestem may not reach its maximum yield potential until 3-4 years after seeding [15], a result supported by the large increases in yield and plant height observed between years in the present study.Differences in switchgrass biomass yield were also observed between selections. Overall yields followed similar patterns as previous studies with early maturing cultivars generally being lower yielding selections than later maturing selections [46] (Table 2). However, higher yields for some of the most recent selections were observed when compared to the original parent materials. For example “Cave-in-Rock II” outyielded Cave-in-Rock in both years at Cookshire-Eaton, while “Blue Jacket II” outyielded “Sunburst” at both sites in 2011. In the case of Tecumseh II there were no significant differences in yield with “Summer” switchgrass observed. “Summer” is known to be a relatively high producing cultivar for its maturity class and breeding progress may be more difficult to achieve. The “Cave-in-Rock II” selection overall appeared to be amongst the most productive selections across sites and years. “Cave-in-Rock” selections generally performed at least as well as or better than the other selections tested, confirming the results of other studies which have found “Cave-in-Rock” to be well adapted and high yielding in Southern Quebec [47].Some selections from the “Sunburst” variety performed poorly in Cookshire-Eaton and in both 2011 and 2012 significantly higher stem rust (Puccinia spp.) incidence was noted on those selections relative to all other selections in the study (data not shown). Stem rust infections are the most common disease reported in switchgrass and may cause significant damage including stunting, early flowering, and reduced yield [39]. The prevalence of rust infections on all “Cave-in-Rock” selections was extremely low, as seen in previous research [48]. Gustafson et al. [49] evaluated the genetic variation in resistance to rust disease in switchgrass populations including “Summer,” “Sunburst,” and “Cave-in-Rock.” “Sunburst” had the highest susceptibility to rust, while “Cave-in-Rock,” having evolved under heavy rust pressure in humid Southern Illinois, was the least susceptible.


## 3.2. Tiller Density

Significant differences in tiller number were observed among selections at all measurement points in both years at Sainte-Anne-de-Bellevue (Figure1). At the first measurement period (early June in 2011 and late May in 2012), the mean tiller density per square meter across all entries was 906 in 2011 and increased to 1033 in 2012, with “Sunburst” producing the most tillers m−2 in both years (1307 in 2011 and 1375 in 2012). Low tiller counts were observed on “Tecumseh” and “Sandlover” switchgrass in 2011 as the plots had relatively thin plant stands. Due to the large variability between plots, the significant differences observed were often between selection lineages and not between selections within a lineage. By the end of August, tiller density in Sainte-Anne-de-Bellevue had decreased to 674 and 706 tillers per square meter in 2011 and 2012, respectively, representing average decreases of 22% and 30%, respectively. The magnitude of the decrease varied considerably depending on the selection lineage. The average decrease in tiller density throughout the season across both years was 38% for “Sunburst” selections, 26% for “Cave-in-Rock” selections, and 19% for “Summer” selections, while no decrease was observed for “Sandlover” which had a thin stand. All selections from the “Sunburst” lineage displayed reduced tillering early in the season. The variable degree of tiller loss across selections ultimately had an equalizing effect on tiller density between all selections.Number of tillers m−2 of 11 selections of switchgrass at Sainte-Anne-de-Bellevue, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD, P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)In Cookshire-Eaton stands were considerably thinner and more variable, but significant differences were still observed between selections at all measurement periods (Figure2). At both sites differences between selections were much larger at the beginning of the season, with only stands with the highest initial density self-thinning throughout the season. However, due to the thinner stands at Cookshire-Eaton tiller mortality during the season was greatly reduced. In 2011, the low initial tiller density in Cookshire-Eaton resulted in no significant decrease over the course of the season with mean tiller number across all selections decreasing from 360 to 324 tillers m−2. In 2012 all stands had higher initial tiller density and a correspondingly greater decrease from 522 to 434 tillers m−2, an average decrease of 14% over the season. Once stands had more fully established at the Cookshire-Eaton site in 2012, trends in average tiller decrease also began to align more closely with those seen at Sainte-Anne-de-Bellevue with an average decrease of 25% for “Sunburst” selections, 21% for “Cave-in-Rock” selections, and 11% for “Summer” selections, while “Sandlover” did not decrease at all due to a thin stand.Number of tillers m−2 of 11 selections of switchgrass at Cookshire-Eaton, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD, P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II, CIR; Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)High tiller mortality as the growing season progresses is common in grasses, with crops such as ryegrass losing 60% of their tillers [50]. The large majority of these are small vegetative tillers which senesce in the sward after being shaded out by the larger reproductive tillers. In perennial grasses such as switchgrass high vegetative tiller production occurs in the spring with subsequent mortality throughout the season [51].The results of the present study support previous findings that indicate that there is likely an optimal tiller density for efficient capture of solar radiation which swards target through increased vegetative tiller production or self-thinning. This optimum is known as tiller equilibrium density [23]. Madakadze et al. [52] found that populations of switchgrass had differing leaf area indices associated with various heights of their canopy. The authors also found that leaf angle and leaf area index varied by variety, indicating that different populations have different canopy structures. The variability in tiller mortality among selections in the present study may indicate that tiller plasticity also plays a large role in this variability. Boe and Casler [13] reported a large degree of plasticity in tiller morphology within populations. In the present study this plasticity seemed to allow tiller density across many selections to converge towards equilibrium density. “Sunburst” had the highest initial density and displayed >40% tiller mortality over the season (Figures 1 and 2), while conversely “Sandlover,” the selection with the lowest initial tiller density, did not display any tiller mortality on average.A trend was also noted for differences in decrease between selections when compared to their parent variety, appearing to often be due to lower initial tiller density in the selections at the beginning of the season. Redfearn et al. [48] examined tiller density in switchgrass plots in Iowa and Nebraska managed for forage and found G × E interactions to be present for both yield and tiller density, with “Cave-in-Rock” producing the lowest tiller number but highest forage yield. The authors noted that tiller density differed with location, even between selections from the same base population. In the present study at Sainte-Anne-de-Bellevue average tiller mortality over both years was 10% lower in “Blue Jacket II” than in “Sunburst” and 13% lower in “Cave-in-Rock II” than in the “Cave-in-Rock” base population. However, there was an average increase in tiller loss in the “Summer” lineage, with mortality on average 16% higher in “Tecumseh II” than in “Summer.” This was likely due to “Tecumseh II” establishing more quickly and having a higher initial density than “Summer” in 2011. In 2012 the “Summer” population was more fully established and there was no significant difference between the two. These trends suggest progress in modification of tillering among the selection lineages where populations were well established.


## 3.3. Height

Significant differences were observed between the heights of selections at all periods observed throughout all site-years (Figures3 and 4); however, trends varied by site. The trends observed were generally supported by previous studies which have indicated that later maturing varieties produce taller tillers due to their slower rates of leaf appearance [53]. “Cave-in-Rock II” was significantly taller than the other selections in its lineage at both sites in 2012, reaching an average of 201 cm in Sainte-Anne-de-Bellevue. Over all site-years this represented an average increase of 12 cm or 7% over the parent variety. The “Cave-in-Rock” selections were the tallest three recorded in 2012 at Cookshire-Eaton. In 2012 the relatively early maturing “Tecumseh” and “Tecumseh II” selections performed very well in Sainte-Anne-de-Bellevue, attaining the second and third highest average heights; however, there was no significant increase in height over the parent variety “Summer.”Height of 11 selections of switchgrass at Sainte-Anne-de-Bellevue, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD,P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)Height of 11 selections of switchgrass at Cookshire-Eaton, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD,P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)No meaningful height differences were observed among big bluestem selections (data not shown); however, there was a significant increase in height in the second year at both sites. This result is consistent with the slower establishment in big bluestem. Average height increased from 144 to 192 cm (33%) at the Cookshire-Eaton site and from 194 to 216 cm (11%) at Sainte-Anne-de-Bellevue in 2011 and 2012, respectively.


## 3.4. Maturity

There were significant differences observed in phenological development at both sites for all measurement periods (Figures5 and 6). The differences observed were almost exclusively between selections in different selection lineages and not within a lineage. The “Sunburst” selections displayed the earliest maturity, followed by the “Summer” selections, with the “Cave-in-Rock” and “Sandlover” selections displaying the latest maturity. These findings are supported by recent literature linking latitude of origin with maturity [46, 54]. The latitudes of origin of the selections in this study rank in the same order as the maturity observed (Table 1). The moisture concentration of the selections at harvest also mirrored this pattern, with significant differences observed between selections related to maturity at harvest (Table 3). No significant moisture differences were observed between selections from a same parent variety.Table 3
Moisture concentration (%) at fall harvest of 11 selections of switchgrass and 3 selections of big bluestem at two sites in Southern Quebec.
Entry
Sainte-Anne-de-Bellevue
Cookshire-Eaton
2011
2012
2011
2012
Switchgrass
Sunburst
36.8
34.1
33.8
27.6
Blue Jacket
36.1
33.8
31.6
31.8
Blue Jacket II
35.5
35.4
32.7
30.1
Blue Jacket Early
38.1
35.2
30.1
28.0
Summer
39.7
31.9
26.1
24.4
Tecumseh
37.7
35.8
37.5
29.3
Tecumseh II
40.3
34.3
31.4
20.2
Cave-in-Rock
46.1
41.0
43.6
29.8
Cave-in-Rock II
45.8
44.5
44.9
39.6
Cave-in-Rock Early
44.1
41.8
35.5
31.6
Sandlover
49.1
44.5
38.7
34.8
Switchgrass mean
40.8
37.5
35.1
29.7
Big Bluestem
Prairie view
43.7
39.6
44.3
38.9
Prairie view II
46.8
41.0
35.6
30.9
Prairie view Early
43.8
39.0
44.0
33.7
Big bluestem mean
44.8
39.9
41.3
34.5
Overall mean
41.7
38.0
36.4
30.8
P value
<0.0001
<0.0001
0.0002
0.0023
LSD (5%)
3.3
3.2
7.9
7.6Mean stage count of 11 selections of switchgrass at Sainte-Anne-de-Bellevue, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD,P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)Mean stage count of 11 selections of switchgrass at Cookshire-Eaton, Quebec, in 2011 and 2012. Vertical bars represent the least significant difference (LSD,P=0.05) at each sampling point throughout the season. BJ1, Blue Jacket; BJ2, Blue Jacket II; BJE, Blue Jacket Early; TEC1, Tecumseh; TEC2, Tecumseh II; CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early.
(a)
(b)


## 3.5. Effects of Harvest Date on Biomass Yield and Quality Variables

Differences were observed at both sites for some selections between fall and spring harvest dates for yield, moisture concentration, and cellulose concentration (Tables4 and 5). The Sainte-Anne-de-Bellevue spring harvest resulted in an overall 41% yield reduction compared to a fall harvest. In Cookshire-Eaton a spring harvest only reduced yield in the highest-yielding selection, “Cave-in-Rock II”, which had an average loss of 56%. Reductions of up to 40% in biomass yield have also been reported in Pennsylvania, where this yield loss was attributed to the loss of panicles and leaves, the leaching of stem components such as minerals and cell solubles [27], and the translocation of mobile nutrients and N-rich compounds into underground perennial structures, a process which may continue into December [3]. These processes have also been shown to decrease the ash fraction in the spring [27, 28]. In the present study no differences were observed between ash concentrations of spring versus fall harvested material (Tables 4 and 5). This lack of change in ash concentration may have been due to soil contamination from the grasses overwintering on the site in a lodged state. Current best management practice by farmers in Eastern Canada is to mow the grasses in late fall and to bale the biomass in spring. This system helps to reduce biomass losses by minimizing the breakage of the leaves and seed heads resulting from wind and snow exposure in material standing over winter [55]. Small plot studies may, therefore, overestimate yield losses compared to an on-farm spring harvest regime. In this study the yield and quality comparisons of the fall and spring material were only made on first production year (2nd year after seeding) material, which had not yet reached full establishment at the marginal site.Table 4
Fall 2011 and spring 2012 values on dry matter basis for yield, moisture concentration, cell wall components, ash, and higher heating value (HHV) of three selections of switchgrass and three selections of big bluestem in Sainte-Anne-de-Bellevue, Quebec.
Entry
CIR
CIR2
CIRE
PV
PV2
PVE
P value
LSD
Moisture (%)
Fall
46.1
45.8
44.1
43.7
46.8
43.8
0.1843
3.076
Spring
11.2
14
10.6
10.7
11.5
10.9
0.326
3.411
% change†
−75.7
−69.4
−76
−75.4
−75.4
−75.1
P value
0.0001
<0.0001
0.0002
<0.0001
0.0002
0.0002
LSD
4.209
2.812
4.925
3.737
4.706
4.2826
Yield (Mg ha−1)
Fall
10
10.2
8.8
6
5.6
6.6
<0.0001
1.202
Spring
6.2
6.1
6.6
3.8
2.8
3
<0.0001
1.518
% change†
−38.3
−40.4
−25.2
−37.9
−49.5
−55.1
P value
0.0052
0.0102
0.0493
0.053
0.0018
0.0034
LSD
1.67
2.253
2.205
2.341
0.8374
1.3616
Cellulose (g kg−1)
Fall
419
414
389
439
431
438
0.0056
25.05
Spring
456
438
429
476
449
447
0.001
17.59
% change†
8.8
5.6
10.4
8.3
4.2
2.1
P value
0.0654
0.0004
0.0042
0.029
0.1361
0.0143
LSD
41.2
4.227
16.29
29.42
28.491
5.676
Hemicellulose (g kg−1)
Fall
315
321
324
316
303
300
0.0593
17.42
Spring
324
336
340
291
313
307
0.0005
18.97
% change†
2.9
4.7
4.9
−7.9
3.3
2.3
P value
0.457
0.2528
0.0061
0.056
0.209
0.1208
LSD
34.56
35.1
7.173
26.219
20.403
10.329
Lignin (g kg−1)
Fall
77
69
65.5
60.1
62.9
63.1
0.2727
14.94
Spring
90.3
73.5
64.5
79.3
63.7
67.9
<0.0001
8.647
% change†
17.3
6.5
−1.5
31.9
1.3
7.6
P value
0.2283
0.3488
0.8434
0.0094
0.8919
0.2655
LSD
28.093
12.857
14.786
9.9
16.149
11.246
Ash (g kg−1)
Fall
45.2
48.9
47.4
48.2
49.1
46.3
0.9689
11.14
Spring
50.4
53.2
50.8
48.3
50.3
55.5
0.9601
17.25
% change†
11.5
8.8
7.2
0.2
2.4
19.9
P value
0.5503
0.4563
0.2225
0.9562
0.7607
0.1186
LSD
24.9
16.041
6.897
9.329
11.929
13.538
HHV (MJ kg−1)
Fall
18.71
18.96
18.78
18.73
19
18.94
0.5896
0.4463
Spring
18.96
18.99
18.73
18.85
18.88
18.92
0.761
0.399
% change†
1.3
0.2
−0.3
0.6
−0.6
−0.1
P value
0.4213
0.8845
0.7915
0.4774
0.4568
0.9009
LSD
0.887
0.5706
0.5966
0.4781
0.46
0.4408
†Percent change relative to fall value.
CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early; PV, Prairie view; PV2, Prairie view II; PVE, Prairie view Early.Table 5
Fall of 2011 and spring of 2012 values on dry matter basis for yield, moisture concentration, cell wall components, ash, and higher heating value (HHV) of three selections of switchgrass and three selections of big bluestem in Cookshire-Eaton, Quebec.
Entry
CIR
CIR2
CIRE
PV
PV2
PVE
P value
LSD
Moisture (%)
Fall
43.6
44.9
35.5
44.3
35.6
43.9
0.0962
8.8360
Spring
8.5
8.8
7.3
% change†
−80.4
−80.3
−79.5
P value
0.0007
0.001
0.0106
LSD
3.8578
4.8707
12.587
Yield (Mg ha−1)
Fall
3.5
5.9
2.5
2.1
1.9
1.6
0.0002
1.2830
Spring
2.6
2.6
2.3
0.0
0.0
0.0
% change†
−26.2
−56.3
−8.5
−100.0
−100.0
−100.0
P value
0.2539
0.0188
0.6558
LSD
2.5201
1.9826
1.7471
Cellulose (g kg−1)
Fall
415
396
376
385
381
371
0.2719
40.852
Spring
445
454
415
0.001
10.307
% change†
7.2
14.7
10.3
P value
0.3218
0.1236
0.0132
LSD
98.893
97.169
19.321
Hemicellulose (g kg−1)
Fall
352
317
339
316
301
290
0.0088
29.914
Spring
345
304
333
0.0001
6.325
% change†
−1.7
−4.0
−1.7
P value
0.3591
0.2353
0.2808
LSD
22.334
32.475
17.053
Lignin (g kg−1)
Fall
73
77
61
55
70
66
0.1155
16.628
Spring
72
89
63
0.0009
6.488
% change†
−0.5
16.2
3.4
P value
0.9687
0.3272
0.5228
LSD
34.118
41.443
11.684
Ash (g kg−1)
Fall
39
48
45
45
46
45
0.6675
11.274
Spring
33
30
32
0.0179
1.539
% change†
−17.5
−38.0
−30.2
P value
0.1626
0.0725
0.0625
LSD
13.665
22.343
15.498
HHV (MJ kg−1)
Fall
19.15
19.09
19.31
19.22
19.20
19.27
0.7519
3.452
Spring
19.35
19.36
19.25
0.6191
3.264
% change†
1.0
1.4
−0.3
P value
0.158
0.4399
0.2681
LSD
0.387
1.2138
0.1836
†Percent change relative to fall value.
CIR, Cave-in-Rock; CIR2, Cave-in-Rock II; CIRE, Cave-in-Rock Early; PV, Prairie view; PV2, Prairie view II; PVE, Prairie view Early.The decrease in moisture concentration in the spring biomass compared to the fall averaged 74% across selections and sites, falling from 45% to 11% moisture concentration (Table4). The high fall moisture values for “Cave-in-Rock” selections are a result of its late maturity and high biomass production. Plant materials are difficult to dry in the short, cool, and high humidity days in Eastern Canada in the late fall [31]. The calorific value for combustion of herbaceous biomass declines linearly with rising moisture concentration, making this an important measure for certain applications [56]. Drying can also take place in covered storage, with fall-baled material at 16-17% moisture declining to 12–14% by the following spring [31].The cell walls of grasses contain cellulose, hemicellulose, lignin, and other compounds including p-coumaric, phenolic, and ferulic acids [26, 57]. The increase in cellulose concentration for some selections at both sites (Tables 4 and 5) is likely related to increased stem fraction combined with an overall reduction of mineral and cell soluble concentrations in overwintered materials. Whole plant big bluestem tended to have slightly higher cellulose and lower hemicellulose concentrations than switchgrass, again likely due to increased stem fraction in the big bluestem. Overwintering generally had a tendency to increase concentration of cellulose in both switchgrass and big bluestem. If big bluestem genetics can be improved to produce similar yields to switchgrass it could be a promising species where high cellulose content biomass feedstocks are required for markets such as bioethanol production and biofibre applications. For lignin there were no trends evident between species or selections. Overall big bluestem appeared to have a higher cellulose to hemicellulose ratio than upland switchgrass. This could be of interest for specialty applications requiring high cellulose content feedstocks.There were no differences in HHV observed between selections or between harvest dates, with Sainte-Anne-de-Bellevue and Cookshire-Eaton averaging 18.9 and 19.3 kJ g−1, respectively, over both harvest times. A previous analysis of four varieties of fall-harvested switchgrass determined an average energy concentration of 18.8±0.2 kJ g−1 with no significant differences between varieties [58], while Madakadze et al. [52] reported a lower energy yield of 17.4 kJ g−1 for “Cave-in-Rock” harvested in the fall in Southern Quebec.Turn et al. [59] have indicated that the leaching process that often occurs in the winter increases HHV in herbaceous biomass through removal of inorganic constituents. However, in the present study harvest time had no effect on HHV. Experiences with spring harvested reed canary grass (Phalaris arundinacea L.) in Sweden demonstrated significant reductions in Cl, K, S, alkali, ash, and several other important quality factors but curiously also a decrease in HHV [28]. The authors also noted large variation in HHV and ash concentration related to soil type, with clay soils having much lower values than humus rich or sandy soils.


## 4. Conclusions

A two-year field study of elite selections of switchgrass and big bluestem found significant differences among selections for yield, tiller density, height, and maturity. Switchgrass was quicker to reach its optimum yield than big bluestem on both productive and marginal sites. Big bluestem was slower to establish and exhibited a higher cellulose content, which was attributed to its high stem content. On both productive and marginal sites switchgrass reached a similar optimum tiller density at the end of the growing season of 690 and 379 tillers m−2, respectively. Tiller mortality throughout the season ranged from 25 to 38%, from 21 to 26%, and from 11 to 19% on the “Sunburst,” “Cave-in-Rock,” and “Summer” lineages, respectively, on the two sites. Two of the elite selections of switchgrass (“Blue Jacket II” and “Cave-in-Rock II”) derived from lineages with high tiller mortality showed upwards trends in height, yield, and reduction of tiller mortality when compared to their parent materials. The present study is one of the most detailed to date on tiller mortality in upland switchgrass. Selection for reduced tillering appears to be a promising strategy for improving yield and quality of upland switchgrass biomass. The differences in maturity and moisture concentration observed at harvest in the fall appear to correspond to the germplasm latitude of origin, and earlier maturity typically was related to lower moisture concentration at harvest. Delayed spring harvest resulted in a large decrease in moisture concentration and a slight increase in cellulose concentration; however, yield losses approached 40%. Unlike in previous studies the ash concentration was not affected by harvest date, nor was the HHV.The results of this study indicate that regional selection programmes have the potential to produce improved selections of upland switchgrass for bioenergy and biofibre markets. From a biomass quality standpoint, big bluestem also appears to be a species of significant potential; however, there is a need for plant breeders to focus on improving establishment to enhance its agronomic potential.



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*Source: 192824-2014-12-17.xml*