Cool-Season Perennial Grasses for the Southern Great Plains[1],2

 

Will C. Cradduck – Texas Tech University

Dr. Andy Hopkins – Noble Foundation, Inc.

 

Grasses that are productive, well adapted, and tested on the southern Great Plains will be in greater demand in the near future.  Decreasing availability of water from the Ogallala Aquifer, and increasing costs of pumping water from greater depths necessitate alternatives that require less water than currently used in irrigated agriculture.  Forage-based livestock production could be an important option.  Annual grains such as wheat (Triticum aestivum) that are planted for forage production are common in this area, but perennial cool season grasses could expand forage availability in autumn and spring and reduce operating costs associated with annual forages.  Identifying such grasses would allow producers to incorporate them into their own systems for greater forage flexibility throughout the year, and reduce dependence on supplemental feed.  Improved forages may also produce higher yields than native species in a high rainfall year, possibly allowing the producer to capitalize on periods of increased rainfall.

 

Rationale.

 

Grasses included in this study are for the most part not native grasses to the southern Great Plains.  These cool season grasses are generally regarded as needing more water than the annual average precipitation in this area can provide.  However, adaptation of these cool season grasses to an area that was historically almost entirely warm season grasses may be possible.  These genotypes were selected from the breeding program of Dr. Andy Hopkins (Noble Foundation, Ardmore, OK), as well as two cultivars from AgResearch (Ashville, NC).  With supplemental irrigation and correct management, these grasses could become important for grazing systems in the southern Great Plains, providing high quality grazing during times in the spring and autumn that have historically been lacking in reliable forage.

Thus, objectives of study are to will determine effects of spring and autumn grazing vs. a non-grazed, hay harvested treatment of different cool-season perennial grass species and cultivars on persistence, quality, mineral concentration, and biomass production.  Please see the end of this summary for a plot map and list of grass species and cultivars.

 

Methods.

 

            Eighteen cultivars and advanced breeding lines were planted near Lubbock, TX in September, 2001.  Plots are fertilized in early spring and late summer with 60 lbs N/acre at each application.  Irrigation is limited to 6 inches in spring and 6 inches in autumn, applied through subsurface drip.  Steers graze plots for 60 days in spring and a shorter period in autumn, sufficient to graze plots down to about 8-10 cm.  Steers are moved on and off plots during the grazing period based on forage mass in the plots.  Non-grazed areas in each plot are cut as for hay at about the panicle emergence growth stage in spring, and about the end of grazing in autumn.

 

Results.

 

Persistence.

For stand counts, 100% stand represents at least 1 live plant for every 8 inch x 8 inch area of the plot (Hopkins, 1993).  Stand counts began in July 2002.  Separate grazed and ungrazed stand counts did not begin until April 2003.  Stand counts have changed very little to date, even with relatively heavy spring grazing and the unusually dry summer of 2003.

Although it is unlikely for the stand counts to increase once the stands are established, these graphs occasionally show an increase.  This is probably due to increases in size of the individual plants as they mature, and some error in sampling.  Increases in stand counts in the western wheatgrass plots are due to prolific rhizomes filling in any empty spaces.

The extensive rhizome production of all four western wheatgrasses included in this study have eliminated any recognition of the original seeded rows.  These grasses are spreading to adjacent plots,  and are beginning to be a problem.  This rhizome production may lend itself to tolerance of high grazing pressures, as it may allow the plant many points of regrowth protected beneath the soil surface.  They also show little drip tape effect as is evident in the other plots, possibly also due to extensive rhizomes and transport of water and nutrients. The western wheatgrasses also maintained a green color through the dry summer of 2003 when the other grasses were basically dormant.

Some of the tall fescue stand counts and all of the smooth brome stand counts appear to be slightly less in the grazed than non-grazed areas.  However, all stand counts are still above 95%, and the difference in grazed and ungrazed is probably not biologically significant. It may only be an artifact of reduced crown and/or overall plant size due to grazing, and not a difference in persistence.  Thus far, all grasses have demonstrated excellent persistence under both grazing and hay cutting management.


Forage Quality.

            Determination of forage quality indicators are in progress.

 

Forage Minerals.

            Determination of forage mineral concentrations are in progress.

 

Canopy Height.

Canopy height was measured by the disk meter method.  Canopy heights are a good indicator of animal grazing patterns, as well as seasonal growth patterns. 

In spring 2003, steers grazed plots fairly uniformly with the exception of the tall and western wheatgrasses.  The steers appeared to find them relatively unpalatable, and we could not force them to graze these plots without overgrazing the other plots.  During the autumn grazing period from November 4 to 11 (last canopy height graph), the steers greatly preferred the fescues to anything else, possibly due to a buildup of sugars in the plant.  This could occur with cooler temperatures causing reduced plant growth, while photosynthesis continues to produce nonstructural carbohydrates in the plant.  The hardinggrasses and bromegrasses were eaten relatively quickly and the intermediate and pubescent wheatgrasses were preferred less.  In Spring 2004, canopy height measurements showed that the steers preferred smooth brome and fescues initially, and left the western wheatgrass and tall wheatgrass for last.  They did eventually graze all the plots down to a fairly uniform height. 

Growth patterns over the year were similar for these grasses, although actual amounts differed.  Following is a graph of forage productivity of these cool season grasses over one year, based on growth documented by canopy height measurement.  This graph is based on the haycut portion of the plots.

 


  Biomass Production.

Haycut yields were calculated by clipping a sample of the forage at a 2-inch cutting height.  Each species and variety is harvested in spring based on growth stage rather than a common harvest date.  Forages are harvested when 50% of the tillers reach the panicle emergence stage.  In autumn, all grasses are harvested at a common date.  Grazed areas are only harvested by spring and fall grazing with the exception of an occasional sample to document biomass.  Ungrazed areas are harvested as for hay.

The spring 2003 haycut shows noticeably higher yields for the tall wheatgrasses, and noticeably smaller yields for the fescues.  This is probably primarily due to the different harvest dates, as noted in the graph. Currently, it appears that these grasses are producing a larger percentage of their biomass in the autumn growth period, despite higher rainfall in the spring and less summer precipitation for the last few years.  This year, that may have been affected by the fact that a lot of biomass was left on the plots over the summer and then harvested with the new growth in the autumn, possibly artificially increasing the fall hay harvest.

 

Early establishment

            Visual ratings were used to document the early establishment phase.  Smooth bromes and wheatgrasses were slower to establish, especially the western wheatgrasses, but all of the plots were initially well established, by the following autumn.  Establishment time may be an important factor to many producers, so the quicker establishing grasses such as hardinggrass and fescue may be a better option assuming they measure up in other respects. 

Based on these plots, if these grasses were planted in early autumn, producers might expect very limited forage production from the fescues and hardinggrasses the following spring.  The wheatgrasses and bromes would only supply limited forage the following autumn.  By spring of the second year, plants are mature enough to produce near their full capacity.

 

Conclusion.

Although this research is still in progress, results to date suggest that many of these grasses show promise as viable forage species on the southern Great Plains.  There is one possible exception.  My only variety of pubescent wheatgrass, PI 401166, has shown low biomass for autumn 2003. Although it still has a normal number of live plants, its canopy cover of the ground is greatly reduced to the point that weeds have invaded those plots to a great extent.  I expect its stand count to start dropping significantly, as well as biomass production to continue to be low.  Most of the other grasses are still showing promise for this area, although there may be significant differences in their biomass production, palatability, and growth habits and production patterns over the year.  Hardinggrass appears to be a top biomass producer as well as being palatable.  The tall and western wheatgrasses appear to have good drought tolerance as well as biomass production.  The fescues are doing quite well in persistence and biomass production, especially AGRFA 102.  The smooth bromes are more average in biomass production, but cannot be discounted until quality has been assessed. 

These grasses could fill gaps in available forage in both spring and autumn, where producers have generally relied on hand feeding and annual cereal crops.  These grasses may allow livestock producers valuable options and flexibility when designing their grazing systems.

 

 

 


 

 

 

                Block 1

 
Cool Season Perennial Grasses Plot Map                                                       N

 

 

 

                      Block 2

 
                                                                                                                        W ­ E

      

       Block 3

 
                                                                                                                             S

 

 

      Block 4

 
                                                                                                                            

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1.  Hardinggrass; Phalaris aquatica; Maru

2.  Hardinggrass; Phalaris aquatica; Maru IP

Surv. C2

3.  Tall fescue; Festuca arundinacea; AGRFA 102

4.  Tall fescue; Festuca arundinacea; AGRFA 103

5.  Tall fescue; Festuca arundinacea; Jesup E+

6.  Tall fescue; Festuca arundinacea; PDF E-

7.  Tall fescue; Festuca arundinacea; 97TF1 E-

8.  Smooth bromegrass; Bromus inermis; Achenbach

9.  Smooth bromegrass; Bromus inermis; Lincoln

10.Smooth bromegrass; Bromus inermis; Lincoln IP Surv. C2

 

 

11. Intermediate wheatgrass; Thinopyrum intermedium; PI 401166

12. Pubescent wheatgrass; Thinopyrum intermedium spp. barbulatum; Luna

13. Tall wheatgrass; Thinopyrum ponticum; Jose

14. Tall wheatgrass; Thinopyrum ponticum; PI401007

15. Western wheatgrass; Pascopyrium smithii; Barton

16. Western wheatgrass; Pascopyrium smithii; Barton H.S. Vig. C1 Syn 1

17. Western wheatgrass; Pascopyrium smithii; 01WW1

18. Western wheatgrass; Pascopyrium smithii; 97WW5


 



[1] Sponsored in part by a grant from the Samuel Roberts Noble Foundation, Inc., Ardmore, OK.

2In conjunction with Ag Research, Ashville, NC.